Volcanic eruption inside the Member State
Volcanic eruption or volcanism inside the Member State. Applicable to PM & SO2.
Volcanic eruption or volcanism outside the Member State. Applicable to PM & SO2.
Seismic activity inside the Member State
Seismic activity inside the Member State. Applicable to PM only.
Seismic activity outside the Member State
Seismic activity outside the Member State. Applicable to PM only.
Geothermal activity inside the Member State
Geothermal activity inside the Member State. Applicable to PM only.
Geothermal activity outside the Member State
Geothermal activity outside the Member State. Applicable to PM only.
Wild-land/natural fire inside the Member State. Applicable to PM & SO2.
Wild-land/natural fire outside the Member State. Applicable to PM & SO2.
High wind event inside the Member State. Applicable to PM & SO2.
High wind event outside the Member State
High wind event outside the Member State. Applicable to PM & SO2.
Atmospheric resuspension inside the Member State
Atmospheric resuspension inside the Member State. Applicable to PM only.
Atmospheric resuspension outside the Member State
Atmospheric resuspension outside the Member State. Applicable to PM only.
Transport of natural particles from dry regions inside the Member State
Transport of natural particles from dry regions inside the Member State. Applicable to PM only.
Transport of natural particles from dry regions outside the Member State
Transport of natural particles from dry regions outside the Member State. Applicable to PM only.
All corrections for natural source & winter sanding or salting applied
No adjustment is due to NS or WSS have been applied or are applicable to the observed levels for this pollutant.
No corrections have been applied to adjust for contributions from natural sources or winter sanding & salting.
An adjustment to corrected observed concentrations for contributions from natural sources has been applied.
An adjustment to corrected observed concentrations for contributions from winter sanding or salting has been applied.
Accumulated Ozone Exposure 40 (expressed in (ug/m3) XXX hours) means the sum of the difference between hourly concentrations greater than 80 ug/m3 and 80 ug/m3 between 1 May to 31 July using only the one-hour values measured between 8.00 and 20.00 Central European Time (CET) each day.
Described in section 5.2.4 of the Aggregation Document
AOT40 vegetation protection averaged over 5 years
AOT40 vegetation protection (AOT40) averaged over 5 years. Following Directive 2008/50/EC: If the three or five year averages cannot be determined on the basis of a full and consecutive set of annual data- the minimum annual data required for checking compliance with the target values will be as follows for the target value for the protection of vegetation: valid data for three years.
Number of valid hourly value for AOTc calculations
Number of valid hourly values (flag 1, 2, 3) between StartTime => 07:00 UTC and EndTime =< 19:00 AND YYYY-05-01T01:00:00+00:00 and YYYY-07-31T24:00:00+00:00
Number of valid hourly value for AOTf calculations
Number of valid hourly values (flag 1, 2, 3) between StartTime => 07:00 UTC and EndTime =< 19:00 AND YYYY-04-01T01:00:00+00:00 and YYYY-09-31T24:00:00+00:00)
Preliminary hourly calculation for AOT40 for AOT40c & AOT40f
max (0, hourly concentration - 80) for hours with StartTime => 07:00 UTC and EndTime =< 19:00 and period YYYY-04-01T01:00:00+00:00 and YYYY-09-31T24:00:00
The daily average or daily mean is the average of all valid hourly values for a day. A daily or 24-hourly average is calculated if at least 18 valid hourly values are available.
Base aggregation - described in section 3.1 of Aggregation document
Data capture for one day. This is an aggregation type added by EEA
Internal calculation - described in section 4.1.1 of Aggregation document
Number of hours with values higher than 180 (unit) in given day
Number of hours with values higher than 240 (unit) in given day
Data fractions missing due to calibration or station repaire. This is an aggregation type added by EEA
Internal calculation - described in section 4 of Aggregation document
Average between 1 hour/day of month X to last hour/day of month X (example for 31 days month: 1/X/YearY - 31/X/YearY)
Number of days with daymax (P8H-dmax) values higher than 100 (unit) in given month
Number of days with daymax (P8H-dmax) values higher than 120 (unit) in given month
Number of hours with values higher than 180 (unit) in given month
Described in section 5.3.2 of the Aggregation Document
Number of hours with values higher than 200 (unit) in given month
Number of hours with values higher than 240 (unit) in given month
Number of hours with values higher than 350 (unit) in given month
Number of hours with values higher than 400 (unit) in given month
Average between 1st January to 31st December Year X (1/1/YearX - 31/12/YearX)
Described in section 5.1 of Aggregation document (Averages and means)
Number of periods when 3 consecutive days are higher than 50 in a given year
Number of periods when 3 consecutive days are higher than 90 in a given year
3 consecutive hours in exceedance of 200
Number of periods when 3 consecutive hours are higher than 200 in a given year
3 consecutive hours in exceedance of 350
Number of periods when 3 consecutive hours are higher than 350 in a given year
3 consecutive hours in exceedance of 400
Number of periods when 3 consecutive hours are higher than 400 in a given year
Described in section 5.3.3 of the Aggregation Document
3 consecutive hours in exceedance of 500
Number of periods when 3 consecutive hours are higher than 500 in a given year
Number of days with daymax values (P8H_dmax) higher than 10 (unit) in given year
The 90.4th percentile of daily averages (P1D) in a given year Aggregation for Compliance.
Described in section 5.2.1 of the Aggregation Document
The 90.41th percentile of daily averages (P1D) in a given year
1 year 95.07 percentile of daily means (P1D) or .../aq/primaryObservation/day
The 95.07th percentile of daily averages in a given year associated to New Directive for pollutants (corresponding with the 19th highest daily value)
1 year 99 percentile of daily means (P1D) or .../aq/primaryObservation/day
The 99th percentile of daily averages in a given year associated to WHO guidelines for pollutants PM10 (5), PM2.5 (6001), NO2 (8), SO2 (1) and CO (10)
New aggregates for new AQ 2021 WHO guidelines
1 year 99.18 percentile of daily value/mean (see P1Y-day-max-per99.18)
The 99.18th percentile of daily averages (P1Y-P1D) in a given year (corresponding with the 4th highest daily value) - Aggregation uses P1Y-day-max-per99.18
The mean for a multi-__day sampler based data types shall be evaluated in a similar way to the data capture (see section 4.2)- although in this instance is calculated as the time weighted mean of valid measurements over the sample period. mean = _i DCi * Nvalid-i Cvalid-i / _i DCi * Nvalid-i i=1.... n where DCi = the data capture of sample i Nvalid-i = the number of hours of the valid sampling period i Cvalid-i = concentration for valid sampling period i
The data capture for multi day sampler based data types integrated over an averaging period is calculated as the proportion of valid measurement time (at a minimum seconds- alternatively decimal hours or days) relative total measured time in the averaging period- expressed as an percentage. The data capture for a given averagingperiod shall be calculated as follows: Data capture = _i DCi * Nvalid-i / _i Ni * 100 % where DCi = the data capture (in %) of the valid sample I- that is- the effective sampling time in a measuring period Nvalid-i = the number of hours in the valid sample i (validity flag sample > 0) Ni = number of hours in sample i
The time coverage is the percentage of measurement time in a given averaging period. Also the time coverage is calculated on base of the number of hours in the sample periods. The time coverage for a given averaging period is calculated as follows (weighted average): Time coverage = _i TCi * Ni / Naveraging_period * 100 % where TCi = the time coverage of sample i Ni = number of hours in sample i Naveraging_period = the total number of hours in the given averaging period (e.g. a year)
Extra aggregation - described in section 5.2.2 of the Aggregation Document
1 year 99.18 percentile of daily MEAN (P1Y-P1D-per99.18)
The 99.18th percentile of daily MEAN (P1Y-P1D) in a given year (corresponding with the 4th highest daily value) - DESCRIPTION UPDATE - notation SHOULD REALLY BE P1Y-P1D-per99.18
The 36th highest daily average value in a given year
The 4th highest daily value in a given year
1 year 50 %ile of daily values in a year
The 50th percentile of DAILY values in a given year
Number of days with values higher than 100 (unit) in given year
Number of days with daily average values higher than 125 (unit) in given year
Number of days with daily average values higher than 25 (unit) in given year
Number of days with daily average values higher than 4 (unit) in given year
Number of days with daily average values higher than 45 (unit) in given year
Number of days with daily average values higher than 50 (unit) in given year
Number of days with daily average values higher than 90 (unit) in given year
Data capture of reported units in 1 year
Data capture of primary reported units (like hour/day XXX) for the given year
Described in section 4.1.1 of Aggregation document
1 year 93.15 percentile daily 8h maximum
The 93.15th percentile of daily 8h maximum (P8H-dmax) in a given year
1 year 95.07 percentile daily 8h maximum
The 95.07th percentile of daily 8h maximum (P8H-dmax) in a given year
The 99th percentile of daily 8h maximum (P8H-dmax) in a given year
Number of days with daymax (P8H-dmax) values higher than 100 (unit) in given year
Number of days with daymax (P8H-dmax) values higher than 120 (unit) in given year
Average day max value between 1st January to 31st December Year X (1/1/YearX - 31/12/YearX)
Described in section 3.1 of Aggregation document
Data capture of daily maximum values in 1 year
The highest P8H-dmax value in given year
It is the highest P8H-dmax (https://dd.eionet.europa.eu/vocabularyconcept/aq/aggregationprocess/P8H-dmax/view) value in a year, and because of that, only calculated for O3 and CO.
The 26th highest daymax value in a given year
Number of valid daymax values in given year
1 year 99.73 %ile of hourly values in a given year
The 99.73th percentile of hourly values (/hour) in a given year (equivalent to 25th highest hourly value)
1 year 99.79 %ile of hourly values in a given year
The 99.79 percentile of hourly values in a given year (corresponding to 19th highest hourly value)
1 year 99.97 %ile of hourly values in a given year
The 99.97th percentile of hourly values (/hour) in a given year (equivalent to 4th highest hourly value)
The 19th highest hourly value in a given year
The 25th highest hourly value in a given year
The 50th percentile of HOURLY values in a given year
Number of hours with values higher than 150 (unit) in given year
Number of hours with values higher than 180 (unit) in given year
Number of hours with values higher than 200 (unit) in given year
Number of hours with values higher than 240 (unit) in given year
Number of hours with values higher than 275 (unit) in given year
Number of hours with values higher than 350 (unit) in given year
Number of hours with values higher than 400 (unit) in given year
Yearly highest six monthly average of daily maximum 8-hour mean concentration
Average of daily maxiumum 8-hour mean concentration in the six consecutive months (P6M-P8H-dmax) with the highest P6M-P8H-dmax in the year
Author's note: this differs to P1Y-peakP6M-P8H-dmax where the yearly 6 month average is selected according to the highest six-month running-average concentration (highest P6M in the year).
Total number of primary reported units (like hours/days XXX) in current year
Total number of valid primary reported units (like hours/days...) in current year
Average of daily maxiumum 8-hour mean concentration in the six consecutive months (P6M-P8H-dmax) with the highest six-month running-average concentration (highest P6M in the year).
ETC has done some work on the proposed methodology for P1Y-peakP6M-P8H-dmax and agreed with EEA, we have decided to simplify the process and calculate, for now, P1Y-maxP6M-P8H-dmax P1Y-maxP6M-P8H-dmax is the maximum P6M-P8H-dmax of the year (using date-end. NOTE: remember that you are storing end date as 01/XX/YYYY instead of end of the period). DC should be calculated base on the number of P6M-P8h-dmax valid in the year and following similar approach for DataCapture, MissingData and TimeCoverage. Example: if for 2020 we have 12 P6M-P8h-dmax with end time within 2020 of which 11 are valid (above 75% DC) then, the DC for P1Y-maxP6M-P8h-dmax will be 11/12 -> 91.67%
Three-year running mean concentration. Average between 1st January Year X-2 to 31st December Year X (1/1/Year X-2 - 31/12/Year X)
Daymax exceed 120 averaged over 3 consecutive years
Number of days with daymax values higher than 120 (unit) averaged over 3 years
Average between 1 hour/day of month X-5 to last hour/day of month X (example for first 6 month's in the year: 1/1/2021 to 31/6/2021) (example for months between years: 1/8/2021 to 31/1/2022)
Average of the daily maximum eight-hour mean (P8H-dmax) in 6 consecutive months
The daily maximum 8-hour running mean for a day is the maximum of the valid hourly 8-hour running means for that day. A daily maximum 8-hour mean is calculated if at least 18 valid hourly 8-hour running means are available for that particular day.
Base aggregation - described in section 3.2 of Aggregation document
The 8-hour running mean value for each hour is calculated as the average of the valid values for that hour and the 7 foregoing hours (averaging period). So- the averaging period of hour1 of dayn is hour17 of dayn-1 until hour1 of dayn. The averaging period of hour24 of dayn is hour16 of dayn until hour24 of dayn. A 8-hourly running averaged concentration is calculated if at least 6 valid hourly values are available.
For quantification of the health impacts the World Health Organisation recommends the use of the SOMO35 indicator. SOMO10 stands for means the sum of the differences between maximum daily 8-hour running mean concentrations greater than 20 µg/m3 (= 10 parts per billion) and 20 µg/m3
For quantification of the health impacts the World Health Organisation recommends the use of the SOMO35 indicator. SOMO35 stands for means the sum of the differences between maximum daily 8-hour running mean concentrations greater than 70 µg/m3 (= 35 parts per billion) and 70 µg/m3
Average between 1st May to 31th July Year X.
Average between 1st April to 30th September Year X.
Average between 1st October Year X-1 to 31st March Year X.
Accumulated Ozone Exposure 40 (expressed in (ug/m3) XXX hours) means the sum of the difference between hourly concentrations greater than 80 ug/m3 and 80 ug/m3 between 1 April to 30 September using only the one-hour values measured between 8.00 and 20.00 Central European Time (CET) each day.
Atomic absorption spectroscopy (AAS) is a spectroanalytical procedure for the quantitative determination of chemical elements employing the absorption of optical radiation (light) by free atoms in the gaseous state. In analytical chemistry the technique is used for determining the concentration of a particular element (the analyte) in a sample to be analyzed. AAS can be used to determine over 70 different elements in solution or directly in solid samples (source: http://en.wikipedia.org/wiki/Atomic_absorption_spectroscopy)
Luminescence is the phenomenon whereby matter emits light of a specific wavelength without emitting heat and returns to a ground state from an excited state after having absorbed external energy from an electromagnetic wave, heat, friction, electric field, or chemical reaction (Fig. 1). When the source of the energy absorbed is a chemical reaction, this phenomenon is called chemiluminescence
The COTAG system determines the exchange of ammonia by means of the aerodynamic flux-gradient method
Cold vapour atomic absorption spectrometry (CV-AAS)
Cold vapour atomic fluorescence spectrometry
Cold vapour atomic fluorescence spectroscopy is a subset of the analytical technique known as atomic fluorescence spectroscopy (AFS). Used in the measurement of trace amounts of volatile heavy metals such as mercury, cold vapour AFS makes use of the unique characteristic of mercury that allows vapour measurement at room temperature. Free mercury atoms in a carrier gas are excited by a collimated ultraviolet light source at a wavelength of 253.7 nanometres. The excited atoms re-radiate their absorbed energy (fluoresce) at this same wavelength.
Source: http://en.wikipedia.org/wiki/Cold_vapour_atomic_fluorescence_spectroscopy
Energy dispersive X-Ray fluorescense (ED-XRF)
Energy Dispersive X-ray Fluorescence (EDXRF) is one of two general types of X-ray Fluorescence techniques used for elemental analysis applications. In EDXRF spectrometers, all of the elements in the sample are excited simultaneously, and an energy dispersive detector in combination with a multi-channel analyzer is used to simultaneously collect the fluorescence radiation emitted from the sample and then separate the different energies of the characteristic radiation from each of the different sample elements.
Flame atomic absorption spectrometry (F-AAS)
A flame ionization detector (FID) is a type of gas detector used in gas chromatography. The detection of organic compounds is most effectively done with flame ionization.
Gas chromatograph with Electron Capture Detector
Gas chromatography (GC) + flame ionisation (GC-FID)
Gas chromatography (GC) + flame ionisation (FID) + ECD (GC-FID-ECD)
Gas chromatography + flame ionisation detection GC-FID after solvent or thermal desorption
Gas chromatography (separation from methane), flame ionization detection (GC (sep methane)-FID)
Gas chromatograph with high-resolution mass spectrometry
Gas chromatography + mass spectrometry (GC-MS)
Gas chromatography–mass spectrometry (GC-MS) is a method that combines the features of gas-liquid chromatography and mass spectrometry to identify different substances within a test sample. Applications of GC-MS include drug detection, fire investigation, environmental analysis, explosives investigation, and identification of unknown samples. GC-MS can also be used in airport security to detect substances in luggage or on human beings. Additionally, it can identify trace elements in materials that were previously thought to have disintegrated beyond identification.
Gas chromatography + mass spectrometry GC-MS after solvent or thermal desorption
Gas Chromatography with Nitrogen Phosphorous Detector GC-NPD
Gas chromatography followed by photo ionization detection (GC-PID)
Graphite furnace atomic absorption spectrometry (GF-AAS)
Graphite furnace atomic absorption spectrometry (GF-AAS) (also known as Electrothermal Atomic Absorption Spectrometry (ET-AAS)) is a type of spectrometry that uses a graphite-coated furnace to vaporize the sample. Briefly, the technique is based on the fact that free atoms will absorb light at frequencies or wavelengths characteristic of the element of interest (hence the name atomic absorption spectrometry). Within certain limits, the amount of light absorbed can be linearly correlated to the concentration of analyte present. Free atoms of most elements can be produced from samples by the application of high temperatures. Source: http://en.wikipedia.org/wiki/Graphite_furnace_atomic_absorption
Analysis of Pb, As, Cd, Ni (Reference) & Hg
Analysis of NO2 based on the Griess-Saltzman reaction
Hydride generation electrothermal - atomic absorption spectrometry (HG-ET-AAS)
High performance liquid chromatography - fluorescence detection (HPLC-FLD)
High-performance liquid chromatography (sometimes referred to as high-pressure liquid chromatography), HPLC, is a chromatographic technique used to separate a mixture of compounds in analytical chemistry and biochemistry with the purpose of identifying, quantifying and purifying the individual components of the mixture. HPLC-FLD is done with fluorescence detection.
High performance liquid chromatography HPLC with UV detection (HPLC-UV)
High-performance liquid chromatography (sometimes referred to as high-pressure liquid chromatography), HPLC, is a chromatographic technique used to separate a mixture of compounds in analytical chemistry and biochemistry with the purpose of identifying, quantifying and purifying the individual components of the mixture. HPLC-FLD is done with UV detection.
High-resolution gas chromatograph with mass spectrometry
High performance liquid chromatography - mass spectrometry (HPLC-MS)
High performance liquid chromatography–mass spectrometry (HPLC-MS, or alternatively LC-MS) is an analytical chemistry technique that combines the physical separation capabilities of liquid chromatography (or HPLC) with the mass analysis capabilities of mass spectrometry. LC-MS is a powerful technique used for many applications which has very high sensitivity and selectivity. Generally its application is oriented towards the general detection and potential identification of chemicals in the presence of other chemicals (in a complex mixture). The limitations of LC-MS in urine analysis drug screening is that it often fails to distinguish between specific metabolites, in particular with hydrocodone and its metabolites.
High resolution continuum source atomic absorption spectrometry (HR-CS-AAS)
When a continuum radiation source is used for AAS measurement it is indispensable to work with a high-resolution monochromator. The resolution has to be equal to or better than the half width of an atomic absorption line (about 2 pm) in order to avoid losses of sensitivity and linearity of the calibration graph. These spectrometers use a compact double monochromator with a prism pre-monochromator and an echelle grating monochromator for high resolution. A linear charge coupled device (CCD) array with 200 pixels is used as the detector. The second monochromator does not have an exit slit; hence the spectral environment at both sides of the analytical line becomes visible at high resolution. As typically only 3–5 pixels are used to measure the atomic absorption, the other pixels are available for correction purposes. One of these corrections is that for lamp flicker noise, which is independent of wavelength, resulting in measurements with very low noise level; other corrections are those for background absorption, as will be discussed later.
Ion chromatography (or ion-exchange chromatography) is a process that allows the separation of ions and polar molecules based on their charge. It can be used for almost any kind of charged molecule including large proteins, small nucleotides and amino acids. The solution to be injected is usually called a sample, and the individually separated components are called analytes. It is often used in protein purification, water analysis, and quality control.
Inductive coupled plasma atomic emission spectrometry (ICP-AES)
Inductively coupled plasma atomic emission spectroscopy (ICP-AES), also referred to as inductively coupled plasma optical emission spectrometry (ICP-OES), is an analytical technique used for the detection of trace metals. It is a type of emission spectroscopy that uses the inductively coupled plasma to produce excited atoms and ions that emit electromagnetic radiation at wavelengths characteristic of a particular element.[1][2] The intensity of this emission is indicative of the concentration of the element within the sample.
Inductive coupled plasma mass spectrometryscopy (ICP-MS)
Inductively coupled plasma mass spectrometry (ICP-MS) is a type of mass spectrometry which is capable of detecting metals and several non-metals at concentrations as low as one part in 1012 (part per trillion). This is achieved by ionizing the sample with inductively coupled plasma and then using a mass spectrometer to separate and quantify those ions.
Isotope dilution analysis is a technique to increase the precision and accuracy of chemical analysis. The isotopic composition of the sample will be slightly changed. Then, by measuring each isotope, the amount of a single element/pollutant in the original sample can be calculated. In a typical gas chromatography analysis, isotopic dilution can decrease the error of injection from 5% to 1%. It can also be used in mass spectrometry (commonly referred to as isotopic dilution mass spectrometry or IDMS), in which the isotopic ratio can be determined with precision typically better than 0.25%.
Isotope-ratio mass spectrometry (IRMS) is a spectroscopic analysis method used to determine the ratio of different isotopes within a sample. IRMS can help establish the sample's isotope fingerprint, which gives it applications in evaluating the authenticity and geographical origin of products and materials.
The extracted samples are analyzed for ammonium on the high sensitivity AMFIA (AMmonia Flow Injection Analysis) system, which is an automated system developed at ECN, Petten, NL (Wyers et al. 1993). AMFIA is based on the selective dialysis of ammonia across a membrane at high pH with subsequent analysis of conductivity.
AMFIA technique: The ammonium moves through a membrane with concentration measured by coductivity
Spectrophotometry is the quantitative measurement of the reflection or transmission properties of a material as a function of wavelength. It is more specific than the general term electromagnetic spectroscopy in that spectrophotometry deals with visible light, near-ultraviolet, and near-infrared, but does not cover time-resolved spectroscopic techniques. Spectrophotometry involves the use of a spectrophotometer. A spectrophotometer is a photometer that can measure intensity as a function of the light source wavelength. Important features of spectrophotometers are spectral bandwidth and linear range of absorption or reflectance measurement.
Thermal-optical analysis is currently under consideration by the European standardization body (CEN) as the reference method to quantitatively determine organic carbon (OC) and elemental carbon (EC) in ambient air.
Ultra Performance Liquid Chromatography (UPLC)
Wavelength Dispersive X-ray fluorescense (WD-XRF)
Wavelength Dispersive X-ray Fluorescence (WDXRF) is one of two general types of X-ray Fluorescence instrumentation used for elemental analysis applications. In WDXRF spectrometers, all of the elements in the sample are excited simultaneously. The different energies of the characteristic radiation emitted from the sample are diffracted into different directions by an analyzing crystal or monochrometer (similar to the action of a prism dispersing different colors of visible light into different directions). By placing the detector at a certain angle, the intensity of X-rays with a certain wavelength can be measured.
X-ray fluorescence (XRF) is the emission of characteristic "secondary" (or fluorescent) X-rays from a material that has been excited by bombarding with high-energy X-rays or gamma rays. The phenomenon is widely used for elemental analysis and chemical analysis, particularly in the investigation of metals, glass, ceramics and building materials, and for research in geochemistry, forensic science and archaeology.
Zeeman atomic absorption spectrometry (ZeemanAAS)
Analysis of Pb, As, Cd & Ni - reference method EN14902
Colorimetric or colourimetric determination of concentration. Example: Colorimetric with p-rosaniline for SO2
Gravimetric analysis describes a set of methods in analytical chemistry for the quantitative determination of an analyte based on the mass of a solid. A simple example is the measurement of solids suspended in air sample: A known volume of air is filtered, and the collected solids are weighed
Analysis of PM10, PM2,5, PM1 (Reference)
Nephelometry is a light scattering method to detect particles in liquid samples. The principle is to measure forwarded scattered light when a laser beam passes through a sample and the light is deflected by the particles.
Photometry is the science of the measurement of light, in terms of its perceived brightness to the human eye.[1] It is distinct from radiometry, which is the science of measurement of radiant energy (including light) in terms of absolute power; rather, in photometry, the radiant power at each wavelength is weighted by a luminosity function (a.k.a. visual sensitivity function) that models human brightness sensitivity.
Titration, also known as titrimetry, is a common laboratory method of quantitative chemical analysis that is used to determine the unknown concentration of an identified analyte. Because volume measurements play a key role in titration, it is also known as volumetric analysis.
Criteria for determining the minimum number of sampling points for fixed measurement
Minimum requirement for pollutant 1 for pop between 0 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 1000000 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 2000000 and 4749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 4750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 250000 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 750000 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 1000000 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 1500000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 2000000 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 2750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 1 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 0 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 1000000 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 2000000 and 4749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 4750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 250000 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 750000 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 1000000 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 1500000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 2000000 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 2750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 10 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 0 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 1000000 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 2000000 and 4749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 4750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 250000 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 750000 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 1000000 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 1500000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 2000000 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 2750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 20 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 0 and 249999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 250000 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 1000000 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 2000000 and 3749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 3750000 and 5999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 6000000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 250000 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 750000 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 1000000 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 1500000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 2000000 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 2750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 0 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 999999 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 1999999 and 4749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 4749999 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 249999 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 749999 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 999999 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 1499999 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 1999999 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 2749999 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 3749999 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 4749999 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5012 for pop between 5999999 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5014 for pop between 0 and 3749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5014 for pop between 3750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5014 for pop between 0 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5014 for pop between 750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5014 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5014 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5014 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5015 for pop between 0 and 3749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5015 for pop between 3750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5015 for pop between 0 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5015 for pop between 750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5015 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5015 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5015 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5018 for pop between 0 and 3749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5018 for pop between 3750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5018 for pop between 0 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5018 for pop between 750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5018 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5018 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5018 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5029 for pop between 0 and 3749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5029 for pop between 3750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 5029 for pop between 0 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5029 for pop between 750000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5029 for pop between 2000000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5029 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 5029 for pop between 4750000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 0 and 249999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 250000 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 1000000 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 2000000 and 3749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 3750000 and 5999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 6000000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 250000 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 750000 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 1000000 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 1500000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 2000000 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 2750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 6001 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 7 for pop between 0 and 249999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between 0 and 249999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between 249999 and 499999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between 249999 and 999999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between 499999 and 999999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between 999999 and 1499999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between 999999 and 1999999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between 1499999 and 1999999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between 1999999 and 2749999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between 1999999 and 2749999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between (3+2)749999 and 2749999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between (3+2)749999 and 2749999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between (3+4)749999 and 5749999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between (3+4)749999 and 5749999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between (3+6)749999 and 7749999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between (3+6)749999 and 7749999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between (3+8)749999 and 9749999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between (3+8)749999 and 9749999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between (3+10)749999 and 11749999 when assessment is - zone type is agg
Minimum requirement for pollutant 7 for pop between 9749999 and 11749999 when assessment is - zone type is noagg
Minimum requirement for pollutant 8 for pop between 0 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 1000000 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 2000000 and 4749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 4750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 250000 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 750000 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 1000000 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 1500000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 2000000 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 2750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 4750000 and 5999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 8 for pop between 6000000 and 1000000000 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 0 and 999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 1000000 and 1999999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 2000000 and 4749999 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 4750000 and 1000000000 when assessment is LAT-UAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 0 and 249999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 250000 and 749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 750000 and 999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 1000000 and 1499999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 1500000 and 1999999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 2000000 and 2749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 2750000 and 3749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 9 for pop between 3750000 and 4749999 when assessment is aboveUAT - zone type is not considered
Minimum requirement for pollutant 7 for pop between (3+12)749999 and 11749999 when assessment is - zone type is noagg
Minimum requirement for pollutant 7 for pop between (3+12)749999 and 11749999 when assessment is - zone type is agg
All areas, that do not fulfil the criteria for urban or suburban areas, are defined as "rural" areas. There are three subdivisions in this category to indicate the distance to the nearest built-up urban area:
area within 10 km from the border of an urban or suburban area.
10-50 km from major sources/source areas.
> 50 km from major sources/source areas.
Largely built-up urban area. ‘Largely built-up’ means contiguous settlement of detached buildings of any size with a building density less than for ‘continuously built-up’ area. The built-up area is mixed with non-urbanised areas (e.g. agricultural, lakes, woods). It must also be noted that ‘suburban’ as defined here has a different meaning than in every day English i.e. ‘an outlying part of a city or town’ suggesting that a suburban area is always associated to an urban area. In our context, a suburban area can be suburban on its own without any urban part.
Continuously built-up urban area meaning complete (or at least highly predominant) building-up of the street front side by buildings with at least two floors or large detached buildings with at least two floors. With the exception of city parks, the built-up area is not mixed with non-urbanised areas.
Criteria for determining the minimum number of sampling points for fixed measurement for ozone when supplementary methods like modelling is used (according to Article 10)
Min requirement O3 with sup. area 0 to 50k and Pop 0 to 2 million
Min requirement O3 with sup. area 0 to 50000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 450001 to 500000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 500001 to 550000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 550001 to 600000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 600001 to 650000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 650001 to 700000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 700001 to 750000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 750001 to 800000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 800001 to 850000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 850001 to 900000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 900001 to 950000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 950001 to 1000000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1000001 to 1050000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1050001 to 1100000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1100001 to 1150000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1150001 to 1200000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1200001 to 1250000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1250001 to 1300000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1300001 to 1350000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1350001 to 1400000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1400001 to 1450000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 1450001 to 1500000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1500001 to 1550000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1550001 to 1600000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1600001 to 1650000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1650001 to 1700000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1700001 to 1750000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1750001 to 1800000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1800001 to 1850000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1850001 to 1900000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 1900001 to 1950000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 1950001 to 2000000 and Pop 0 to 22000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 50001 to 100000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 100001 to 150000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 150001 to 200000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 200001 to 250000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 250001 to 300000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 300001 to 350000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 350001 to 400000 and Pop 20000001 to 22000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 0 to 2000000.
Min requirement O3 with sup. area 0 to 50000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 2000001 to 4000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 4000001 to 6000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 6000001 to 8000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 8000001 to 10000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 10000001 to 12000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 12000001 to 14000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 14000001 to 16000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 16000001 to 18000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 18000001 to 20000000.
Min requirement O3 with sup. area 400001 to 450000 and Pop 20000001 to 22000000.
Between Lower and Upper Assessment Threshold (LAT-UAT)
Between the upper and lower threshold (LAT-UAT), on 3 or more occasions during the 5 previous years.
Above the long-term objective for ozone (>LTO) on 1 or more occasions during the 5 previous years.
Above the Upper Assessment Threshold (>UAT), on 3 or more occasions during the 5 previous years.
Below the Lower Assessment Threshold (<LAT), on 3 or more occasions during the 5 previous years.
Below the long-term objective for ozone (<LTO) during any of the 5 previous years.
‘fixed measurements’ shall mean measurements taken at fixed sites, either continuously or by random sampling, to determine the levels in accordance with the relevant data quality objectives; Legal reference: Decision 2011/850/EU - ANNEX II - (D) Information on the assessment methods , (ii) "Fixed measurement Information" describes the information to be made available by the Member States (mandatory or voluntary).
‘indicative measurements’ shall mean measurements which meet data quality objectives that are less strict than those required for fixed measurements; Legal reference: Decision 2011/850/EU, Article 9, paragraph 4 and Annex II D (iii)
Legal reference : Decision 2011/850/EU, Article 9, paragraph 5 and Annex II D (iv)
Legal reference: Decision 2011/850/EU, Article 9, paragraph 6 and Annex II D (v) “Objective estimation techniques” will be interpreted as mathematical methods to calculate concentrations from values measured at other locations and/or times, based on scientific knowledge of the concentration distribution. One example is linear interpolation based on a justified assumption that the concentration pattern is sufficiently smooth. Another example is a dispersion model that has been adjusted to reproduce concentrations measured within its domain. More information is available at: http://ec.europa.eu/environment/air/pdf/guidanceunderairquality.pdf
“other measurement” shall mean measurements that do not meet the Air Quality Directives’ requirements for fixed or indicative measurements, but can be provided on the basis of exchange of information. For example, measurements from short measurement campaigns or measurements with lower quality.
Member States may apply random measurements instead of continuous measurements for benzene, lead and particulate matter if they can demonstrate to the Commission that the uncertainty, including the uncertainty due to random sampling, meets the quality objective of 25 % and the time coverage is still larger than the minimum time coverage for indicative measurements. Random sampling must be evenly distributed over the year in order to avoid skewing of results. The uncertainty due to random sampling may be determined by the procedure laid down in ISO 11222 (2002) ‘Air Quality — Determination of the Uncertainty of the Time Average of Air Quality Measurements’. If random measurements are used to assess the requirements of the PM10 limit value, the 90,4 percentile (to be lower than or equal to 50 μg/m3) should be evaluated instead of the number of exceedances, which is highly influenced by data coverage.
Code list that corresponds to the context of the authority’s role
Reporting AQ data and assessments to EEA
AQ e-Reporting authority's role: reporting data and assessments to EEA
Establishment of air quality plans and air quality roadmaps
AQ e-Reporting authority's role: establishment of air quality plans. According to article 5, (h) establishment of air quality plans and air quality roadmaps;
AQ e-Reporting authority's role: establishment of action plans. According to Article 5, (i) establishment of short-term action plans;
Air quality index and public information
AQ e-Reporting authority's role: air quality index and public information. According to Article 5, (j) provision and maintenance of an air quality index and other relevant public information as specified in Annex X.
Reporting AQ plans, roadmaps and short-term action plans to EEA
AQ e-Reporting authority's role: reporting AQ plans, roadmaps and short-term action plans to EEA
AQ e-Reporting authority's role: assessment of air quality. According to Article 5, (a) assessment of ambient air quality, including ensuring an adequate functioning and maintenance of the monitoring network;
AQ e-Reporting authority's role: approval of measurement system. According to Article 5, (b) approval of measurement systems (methods, equipment, networks and laboratories);
AQ e-Reporting authority's role: accuracy of measurements. According to Article 5, (c) ensuring the accuracy of measurements and the transfer and sharing of measurement data;
AQ e-Reporting authority's role: accuracy of modelling applications. According to Article 5, (d) promoting the accuracy of modelling applications;
AQ e-Reporting authority's role: analysis of assessment methods. According to Article 5, (e) analysis of assessment methods;
Coordinator for EU quality assurance programmes
AQ e-Reporting authority's role: coordinator for EU quality assurance programmes. According to article 5, (f) coordination on their territory if Union-wide quality assurance programmes are being organised by the Commission;
Cooperation with other MS/Commission (icl. transboundary)
AQ e-Reporting authority's role: cooperation with other MS/Commission (icl. transboundary). According to article 5, (g) cooperation with the other Member States and the Commission, including on transboundary air pollution;
Indication whether the authority is "active" or "inactive”
AQD - Quality control and assurance on CDR
aqd:AQD_ReportingHeader element must be present.
XML must include Reporting Header
[Crucial]: Yes - System requirement - Integrated into one qa check
Reporting period must be reported and the envelop starting year must match the specific year within Reporing Header in the XML
aqd:AQD_ReportingHeader/aqd:reportingPeriod must be reported in all XMLs. The (start) year value must be equal to the year specified in (aqd:AQD_ReportingHeader) in the XML file and it must be between 2014 - 2015.
The following elements must be included within Reporting Header (inspire Id, reporting authority and change element)
aqd:AQD_ReportingHeader must include aqd:inspireId, aqd:reportingAuthority, aqd:change elements
For aqd:AQD_ReportingHeader, if aqd:change='true', the following information must also be provided: aqd:AQD_ReportingHeader/aqd:changeDescription and aqd:AQD_ReportingHeader/aqd:content
For aqd:AQD_ReportingHeader, if aqd:change='false', element aqd:content IS NOT expected.
At least one file in the folder must be an XML with correct extension (*.xml)
Checks if this delivery is new or an update (on same reporting year)
Check if delivery if this is a new delivery or updated delivery (via reporting year)
Compile & feedback upon the total number of AQ zone feature types included in the delivery
Number of zones reported
Number of new zones compared to previous report. Blocker will be returned if XML is a new delivery and localId are all new compared to previous deliveries
Compile & feedback upon the total number of new records for AQ zones included in the delivery against previous delivery
[Crucial]: Yes - Information - Update to check if all localId are new
Number of existing zones compared to previous report. Blocker will be returned if XML is an update delivery and localId are all new compared to previous deliveries
Compile & feedback upon the total number of existing records for AQ zones included in the delivery against previous delivery
[Crucial]: Yes - System requirement - Update to check if all localId are new
Compile & feedback upon all reported zones. Feedback report shall include the gml:id attribute, am:inspireId, am:name/gn:GeographicalName/gn:spelling/gn:text & aqd:zoneCode elements as available.
List reported zones
Compile & feedback upon the total number of modification to existing for AQ zone feature types included in the delivery, including ./aqd:predecessor information Report if the object xlinked via aqd:predecessor is not found within the current or previous deliveries (aqd:AQD_Zone)
reserved
Not implemented -IPR requirement (Annex II-B-8)
New zones/agglomerations for the protection of Health must link to predecessor.
New zones/agglomerations compared to previous deliveries for the protection of Health must link to predecessor (aqd:predecessor). .
New zones/agglomerations for the protection of vegetation should link to predecessor.
New zones/agglomerations compared to previous deliveries for the protection of Vegetation should link to predecessor (aqd:predecessor).
Number of zones that provides coordinates inside the xml via geometry element
The number of zones designated with coordinates via the ./am:geometry element
Number of zones that provides coordinates via Local Administrative Units (LAU) element and external shapefile link
The number of zones designated with coordinates via the ./aqd:LAU element and the ./aqd:shapefileLink element
Number of unique combinations of zone types, pollutants and protection target
List of unique combinations of aqd:aqdZoneType, aqd:pollutantCode and aqd:protectionTarget
Check and count expected combinations of Pollutant and ProtectionTarget
Check and count expected combinations of Pollutant and ProtectionTarget: Sulphur dioxide (1) + health - Sulphur dioxide (1) + vegetation - Ozone (7) + health - Ozone (7) + vegetation - Nitrogen dioxide (8) + health - Nitrogen oxides (9) + vegetation - Particulate matter < 10 µm (5) + health - Particulate matter < 2.5 µm (6001) + health - Carbon monoxide (10) + health - Benzene (20) + health - Lead in PM10 (5012) + health - Arsenic in PM10 (5018) + health - Cadmium in PM10 (5014) + health -Nickel in PM10 (5015) + health - Benzo(a)pyrene in PM10 (5029) + health
[Crucial]: Yes - SYSTEM & INSPIRE requirement
Internal XML and INSPIRE identifiers must be unique (gml:id, base:localId)
All gml:id attributes, am:inspireId and aqd:inspireId elements shall have unique content
List unique namespaces used and count number of elements
./am:inspireId/base:Identifier/base:namespace List base:namespace and count the number of base:localId assigned to each base:namespace.
Check that namespace is registered in vocabulary (http://dd.eionet.europa.eu/vocabulary/aq/namespace/view)
Unregistered country namespaace has been used
The sum of the population of different zones for expected combinations of Pollutant and ProtectionTarget must be within +/-5%
The sum of the population reported via aqd:residentPopulation of different zones for expected combinations of Pollutant and ProtectionTarget must be within +/-5% (according to http://dd.eionet.europa.eu/vocabulary/aq/namespace/view)
The sum of the population of different zones for expected combinations of Pollutant and ProtectionTarget must not differ substantially between themselves
The sum of the population reported via aqd:population of different zones for expected combinations of Pollutant and ProtectionTarget can not be greater than 1% of the total Population or 50,000 inhabitants (whichever is lower)
The sum of the area (km2) of different zones for expected combinations of Pollutant and ProtectionTarget must be within +/-0.5%
The sum of the area (km2) reported via aqd:area of different zones for expected combinations of Pollutant and ProtectionTarget must be within +/-0.5% (according to http://dd.eionet.europa.eu/vocabulary/aq/namespace/view)
The sum of the areas of different zones for expected combinations of Pollutant and ProtectionTarget must not differ substantially between themselves
The sum of the area (km2) reported via aqd:area of different zones for expected combinations of Pollutant and ProtectionTarget can not be greater than must be within 1% of SurfaceArea or 50 km2 (whichever is lower)
Compare area declared for each zone compared to previous (based on localId)
The geographical language code must correspond to either the ISO 639-3 or ISO 639-5.
/aqd:AQD_Zone/am:name/gn:GeographicalName/gn:language value shall be the language of the name, given as a three letters code, in accordance with either ISO 639-3 or ISO 639-5.
Check the sum of area and population for Health protection combinations against vocabulary.
Check and make the sum of area (aqd:area) and population (aqd:residentPopulation) expected combinations of Pollutant and ProtectionTarget: Sulphur dioxide (1) + health - Ozone (7) + health - Nitrogen dioxide (8) + health - Particulate matter < 10 µm (5) + health - Particulate matter < 2.5 µm (6001) + health - Carbon monoxide (10) + health - Benzene (20) + health - Lead in PM10 (5012) + health - Arsenic in PM10 (5018) + health - Cadmium in PM10 (5014) + health -Nickel in PM10 (5015) + health - Benzo(a)pyrene in PM10 (5029) + health
Check the sum of area and population for all Health protection combinations are within 5% of the mode of the sums.
The sum of area and population for all Health protection combinations should be within 5% of the mode of the sums for the same combination
Check results on B14 and B15. Any combination with a warning in both B14 and B15 will result in Error.
Compare the list of zone-pollutant-protectionTarget combination with previous delivery
QC rule B17 checks if the combinations of aqd:AQD_Zone - aqd:pollutantCode - aqd:protectionTarget from the current XML are present in the latest delivery of the previous year; it lists all aqd:AQD_Zone - aqd:pollutantCode - aqd:protectionTarget combinations which are different from the previous year submission of data flow B.
The geographical language text must be a string
./am:name/gn:GeographicalName/gn:spelling/gn:SpellingOfName/gn:text shall return a string
[Crucial]: Yes - IPR requirement (Annex II-B-4)
./am:name/gn:GeographicalName/gn:spelling/gn:SpellingOfName/gn:script attribute xsi:nil="true" nilReason="unknown"
The coordinate reference system for the zones must be defined with a correct uniform resource name
/am:geometry/gml:Polygon, ./am:geometry/gml:Point, ./am:geometry/gml:MultiPoint, ./am:geometry/gml:MultiSurface, ./am:geometry/gml:Grid, ./am:geometry/gml:RectifiedGrid the srsName attribute shall be a recognisable URN. The following 3 srsNames are expected urn:ogc:def:crs:EPSG::3035 or urn:ogc:def:crs:EPSG::4258 or urn:ogc:def:crs:EPSG::4326
Coordinate system for Zones needs revision
[Crucial]: Yes - IPR requimrent (Annex II-B-6)
The dimension attribute must be given the value "2"
/am:geometry/gml:Polygon, ./am:geometry/gml:Point, ./am:geometry/gml:MultiPoint, ./am:geometry/gml:MultiSurface, ./am:geometry/gml:Grid, ./am:geometry/gml:RectifiedGrid, ./am:geometry/gml:Polygon/gml:exterior/gml:LinearRing/gml:posList the srsDimension attribute shall resolve to "2" to allow the x & y-coordinate of the feature of interest
Geometry information needs revising as errors were detected which will prevent processing it.
The count attribute must be equal to the Y and X coordinate doublets
./am:geometry /gml:Polygon/gml:exterior/gml:LinearRing/gml:posList the count attribute shall resolve to the sum of y & x-coordinate doublets.
Coordinate provided for Zones needs revision as not provided a Y and X coordinate doublets
[Crucial]: Yes - IPR requirement (Annex II-B-6) & system requirement (can not process if not correct)
The coordinates must be ordered as latitude (y-axis), longtitude (x-axis). Please note that if warning, GEOMETRY checks might fail.
Check that the coordinates lists in ./am:geometry /gml:Polygon/gml:exterior/gml:LinearRing/gml:posList ar presented in lat / long (y-axis / x-axis) notation.
The coordinates must be ordered as latitude (y-axis), longtitude (x-axis)
[Crucial]: Yes - IPR requimrent (Annex II-B-6) - Exception with France
Zone type must conform to http://inspire.ec.europa.eu/codelist/ZoneTypeCode/airQualityManagementZone
./am:zoneType value shall resolve to http://inspire.ec.europa.eu/codelist/ZoneTypeCode/airQualityManagementZone (working URL)
Codelist for am:zoneType requires revision: INSPIRE codelist is required
Start time must be less than end time and must be provided
./am:designationPeriod/gml:TimePeriod/gml:beginPosition shall be less than ./am:designationPeri/gml:TimePeriod/gml:endPosition. (start time must be provided)
Zone's Start time must be less than end time
[Crucial]: Yes - IPR requimrent (Annex II-B-7)
The begin date of a zone should be the same as previous delivery (inc. updates for the same year)
./am:designationPeriod/gml:TimePeriod/gml:beginPosition shall NOT be different from previous delivery
The zone's end date should not differ from previous delivery (if already closed)
./am:designationPeri/gml:TimePeriod/gml:endPosition shall not be different from previous delivery (exception from NULL to a value) - If in previous delivery the zone was already closed, it can not be re-opened - If previous delivery has an end date, in new delivery, it can not change
End date must be greater than start date, if end date exists
./am:beginLifespanVersion shall be a valid historical date for the start of the version of the zone in extended ISO format. If an am:endLifespanVersion exists its value shall be greater than the am:beginLifespanVersion
Zone's End date must be greater than start date, if end date exists
./am:beginLifespanVersion shall be LESS THAN OR EQUAL TO ./am:designationPeriod/gml:TimePeriod/gml:endPosition ./am:beginLifespanVersion shall be GREATER THAN OR EQUAL TO ./am:designationPeriod/gml:TimePeriod/gml:beginPosition
Start date shall be less, or equal to
Enviromental Domain must conform to http://inspire.ec.europa.eu/codelist/MediaValue/[code]
./am:environmentalDomain shall be a citation via href xlink attribute of http://inspire.ec.europa.eu/codelist/MediaValue/[code] (currently resolves to 404 error)
Codelist for am:environmentalDomain requires revision: INSPIRE codelist is required
Legislation citation name must be “2011/850/EC”
./am:legalBasis/base2:LegislationCitation/base2:name value shall be “2011/850/EC”
Legislation citation date must be “2011-12-12”
./am:legalBasis/base2:LegislationCitation/base2:date value shall be “2011/12/12”
Legislation citation line must be “http://rod.eionet.europa.eu/instruments/650”
./am:legalBasis/base2:LegislationCitation/base2:link value shall be “http://rod.eionet.europa.eu/instruments/650”
Base level must conform to http://inspire.ec.europa.eu/codelist/LegislationLevelValue/[code]
./am:legalBasis/base2:LegislationCitation/base2:level shall be a citation via href xlink attribute of http://inspire.ec.europa.eu/codelist/LegislationLevelValue/[code]
Codelist for …base2:level requires revision: INSPIRE codelist is required
Zone code must be unique. The value may e equal the LocalId
./aqd:zoneCode shall be a unique code for the zone within the ./am:inspireId/base:Identifier/base:namespace. ./aqd:zoneCode . The value may equal the value at ./am:inspireId/base:Identifier/base:localId
[Crucial]: Yes - IPR requimrent (Annex II-B-3)
Population must be a value higher than zero
./aqd:residentPopulation shall be an integer value GREATER THAN 0 (zero)
[Crucial]: Yes - IPR requimrent (Annex II-B-9)
Year in which the resident population was estimated must have the format yyyy
./aqd:residentPopulationYear/gml:TimeInstant/gml:timePosition shall cite the year in which the resident population was estimated in yyyy format
The year in which resident population was provided is in the wrong format
[Crucial]: Yes - IPR requimrent (Annex II-B-10)
The Area value must be a decimal number, greater than zero.
./aqd:area the value will be a decimal number GREATER THAN 0 (zero)
Check for correct Pollutant/ProtectionTarget combination
The allowed content combination within ./aqd:pollutants/aqd:Pollutant/aqd:pollutantCode AND ./aqd:pollutants/aqd:Pollutant/aqd:protectionTarget shall be constrained to Sulphur dioxide (air) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/1 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Sulphur dioxide (air) + vegetation (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/1 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/V) - Ozone (air) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/7 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Ozone (air) + vegetation (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/7 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/V) - Nitrogen dioxide (air) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/8 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Nitrogen oxides (air) + eco (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/9 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/V) - Particulate matter < 10 µm (aerosol) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Particulate matter < 2.5 µm (aerosol) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/6001 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Carbon monoxide (air) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/10 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Benzene (air) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/20 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Lead in PM10 (aerosol) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5012 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Arsenic in PM10 (aerosol) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5018 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Cadmium in PM10 (aerosol) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5014 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H) - Nickel in PM10 (aerosol) + health (http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5015 + http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H)
[Crucial]: Yes - Air quality requirement
Check if at least one of the expected Pollutant/ProtectionTarget combination(s) is provided in the delivery
Count number of occurrences across XML and list it as below (it can not be 0): Sulphur dioxide (1) + health & Sulphur dioxide (1) + vegetation & Ozone (7) + health & Ozone (7) + vegetation & Nitrogen dioxide (8) + health & Nitrogen oxides (9) + vegetation & Particulate matter < 10 µm (5) + health & Particulate matter < 2.5 µm (6001) + health & Carbon monoxide (10) + health & Benzene (20) + health Lead in PM10 (5012) + health & Arsenic in PM10 (5018) + health & Cadmium in PM10 (5014) + health & Nickel in PM10 (5015) + health & Benzo(a)pyrene in PM10 (5029) + health & One exception: Nitrogen oxides (9) + vegetation can be 0 for Gibraltar
Missing expected combinations of Pollutant and ProtectionTarget
Check and list if any individual zone with any duplicated Pollutant/ProtectionTarget combination
Check if any combination in B39a is repeated within individual AQD:Zone . An error is returned if repeated.
Pollutant/ProtectionTarget combination is repeated withing same zone. Please amend
ExtensionExemption accepted prior to 2015 deliveries
IF aqd:reportingPeriod included in the ReportingHeader is equal or greater than year 2015, ./aqd:timeExtensionExemption must resolve to http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/none Only 1 entry is allowed. Else ./aqd:timeExtensionExemption attribute must resolve to one of concept within http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/… Multiple entries are allowed.
Time extensions are NOT expected in zones after 2015.
[Crucial]: Yes - IPR requimrent (Annex II-B-13)
Where AQTimeExemption is either NO2-1h, or NO2-annual, then NO2 and Protection Target Health must be present
Where ./aqd:timeExtensionExemption resolves to http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/NO2 1h OR http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/NO2 annual at least one combination within ./aqd:pollutants which includes ./aqd:pollutants/aqd:Pollutant/aqd:pollutantCode AND ./aqd:pollutants/aqd:Pollutant/aqd:protectionTarget shall be constrained to Nitro gen dioxide Nitrogen dioxide (air) + health http://dd.eionet.europa.eu/vocabulary/aq/pollutant/8 http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H
[Crucial]: Yes - Content check according to Article 22 of Directive 2008/50/EC
Where AQTimeExemption is either PM10-24h, or PM10-annual, then PM10 and Protection Target Health must be present.
Where ./aqd:timeExtensionExemption resolves to http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/PM10-24h OR http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/PM10-annual at least one combination within ./aqd:pollutants which includes ./aqd:pollutants/aqd:Pollutant/aqd:pollutantCode AND ./aqd:pollutants/aqd:Pollutant/aqd:protectionTarget shall be constrained to Particulate matter < 10 μm (aerosol) + health http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5 http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H
Where AQTimeExemption is C6H6-annual, then C6H6 and Protection Target Health must be present.
Where ./aqd:timeExtensionExemption resolves to http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/C6H6-annual at least one combination within ./aqd:pollutants which includes ./aqd:pollutants/aqd:Pollutant/aqd:pollutantCode AND ./aqd:pollutants/aqd:Pollutant/aqd:protectionTarget shall be constrained to Benzene (air) + healt http://dd.eionet.europa.eu/vocabulary/aq/pollutant/20 http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/H
Geometry should not be a hyperlink. If provided via shapefile, element aqd:shapefileLink need to be used
./am:geometry shall not be a href xlink. If geometry is provided via shapefile, please use element aqd:shapefileLink
Link to shapefiles use incorrect element. Please use aqd:shapefileLink
[Crucial]: - SYSTEM & INSPIRE requirement
Where a link is provided, it should refer to an existing and valid shape file in the same folder in the CDR as the XML is uploaded
Where ./aqd:shapefileLink has been used this should return a link to a valid and existing link in cdr (e.g. http://cdr.eionet.europa.eu/es/eu/aqd/b/envurng9g/ES_Zones_2014.shp)
Shapefile have not been reported correctly in the expected CDR envelope. Please revise
[Crucial]: Skipped - Not implemented - This is required for correctly processing geometries
Zone type must be either Agglomeration or Non-agglomeration
./aqd:aqdZoneType attribute must resolve to one of concept within http://dd.eionet.europa.eu/vocabulary/aq/zonetype/[concept] Currently, these are: http://dd.eionet.europa.eu/vocabulary/aq/zonetype/noagg or http://dd.eionet.europa.eu/vocabulary/aq/zonetype/agg
Designation Period DATE must be provided in extended ISO format
When am:designationPeriod/am:designationPeriod/gml:beginPosition & am:designationPeriod/am:designationPeriod/gml:endPosition ARE populated, the DATE must be in extended ISO format
Where ./aqd:LAU has been used the list of the administrative these shall be checked to ensure they relate to the MS. This must be provided if /aqd:shapefileLink is not provided or am:geometry does not contain geometry. The value shall be a valid code from the following codelist: http://dd.eionet.europa.eu/vocabulary/common/nuts/ http://dd.eionet.europa.eu/vocabulary/lau1/ http://dd.eionet.europa.eu/vocabulary/lau2/ NUTS, LAU1 or LAU2 codes must belong to the country reporting data. Country ISO code at cdr.eionet.europa.eu/ZZ/eu/aqd/b/…. shall be the same as the codelist: http://dd.eionet.europa.eu/vocabulary/common/nuts/ZZ[concept] http://dd.eionet.europa.eu/vocabulary/lau1/zz/[concept] http://dd.eionet.europa.eu/vocabulary/lau2/zz/[concept] (exception of gb which has lau and nut codeas as uk)
Compile & feedback upon the total number of AQ Assessment Regime feature types included in the delivery
Number of Assessment Regimes reported
Number of new Assessment Regimes compared to previous report. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries
Compile & feedback upon the total number of new records for AQ Assessment Regime feature types included in the delivery. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries.
[Crucial]: Error, new delivery but re-using localId from previous -
Number of existing Assessment Regimes compared to previous report. ERROR will be returned if XML is an update and ALL localId (100%) are NEW to previous delivery (for the same YEAR).
Compile & feedback upon the total number of modifications to previously reported AQ Assessment Regime feature types included in the delivery ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
Error, updated delivery but all localId are new
Number of Assessment Regimes in C should match Assessment Regimes in Preliminary C (for the same YEAR).
The assessment regimes previously declared in the preliminary Assessment Regime (forward looking) should match those declared under the current Assessment Regime (retrospective look)
Number of Assessment Methods used under Assessment Regimes should be the same as Preliminary Assessment Regime (for the same YEAR).
The assessment methods previously declared in the preliminary Assessment Regime (forward looking) should match those declared under the current Assessment Regime (retrospective look)
Check if, for matching methods, the AssessmentType has changed the assessmentTypes
List new assessment methods in C compared to C preliminary
gml:id must be unique within the XML document
All gml:id attributes shall have unique content within the document or namespace
Local Id shall be unique for the assessment regime.
./aqd:inspireId/base:Identifier/base:localId shall be an unique code for the assessment regime.
[Crucial]: Yes - INSPIRE/system requirement
./aqd:inspireId/base:Identifier/base:namespace List base:namespace and count the number of base:localId assigned to each base:namespace.
Check namespace is registered
Each Assessment Regime shall have one Environmental Objective element
Each of the number of /aqd:AQD_AssessmentRegime records shall contain 1 ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmental Objective records per /aqd:AQD_AssessmentRegime element
[Crucial]: Yes - IPR/system requirement - aqd:AQD_AssessmentRegime/aqd:assessmentThreshold [Cardinality 0..* to 0..1]
Assessment regimes must be reported all expected pollutants
./aqd:pollutant xlink:href attribute may resolve to one of http://dd.eionet.europa.eu/vocabulary/aq/pollutant/1 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/7 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/8 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/9 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/6001 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/10 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/20 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5012 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5014 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5015 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5018 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5029
[Crucial]: Yes - IPR requirement (Annex II-C-4)
Check valid combination of pollutant/EnvironmentalObjective (Objective/ProtectionTarget/ReportingMetric). Error if unexpected combination
Check that EnvironmentalObjetive (ObjectiveType+ReportingMetric+ProtectionTarget) correspond to a valid combination in http://dd.eionet.europa.eu/vocabulary/aq/environmentalobjective/view
Unexpected combinations found
[Crucial]: Yes - IPR requirement (Annex II-C-4 + Annex II-C-5) -Updated in v5.0 to use EnvObjective vocabulary
Check discrepancies between the expected Assessment Regime combinations based on dataflow B - Zones (latest released same reporting years)
The new check C11 will double check that data-flow C is complete according to all zones declared in data-flow B. The validation throws error when: a) The combination of elements Pollutant + Protection Target + ZoneId + Environmental objective from B is missing in C. b) The combination of elements Pollutant + Protection Target + ZoneId + Environmental objective from C is missing in B. c) The combination of elements Pollutant + Protection Target + ZoneId + Environmental objective is duplicated. Exception when objective type is "MO", "ECO", "ERT", "LVMOT", "LVmaxMOT", "INT" and "ALT"
Check the minimum number of fixed SPO required per each Zone+EnvironmentalObjective according to AQ Directive
Evaluate the minimum number of fixed sampling points for all zones considering the population number reported in dataflow B and the classification of the zone for the particular Environmental Objective. Minimum according to anexV & IX. Numbers in EEA vocabulary: https://dd.eionet.europa.eu/vocabulary/aq/anexV_IX_minimum_spo/view & https://dd.eionet.europa.eu/vocabulary/aq/art10_O3_Model_minimum_spo/view
Check and list any missing combination of pollutant/EnvironmentalObjective. Error if combination missing
Provide any missing combination of Pollutant/EnvironmentalObjective according to vocabulary http://dd.eionet.europa.eu/vocabulary/aq/environmentalobjective/ (Exceptions: when ObjectiveType = .../MO + .../LVMOT + .../LVmaxMOT &those combinations when "Exceedance threshold" within the vocabulary is populated)
Missing combination of pollutant/EnvironmentalObjective.
[Crucial]: Yes - IPR requirement (Annex II-C-4 + Annex II-C-5) + correct content check vs AQD/IPR
Count number of Assessment Regimes for pollutants with Monitoring Objective according to Annex X (Directive 2008/50/EC)
Count on unique pollutants when Assessment regime(s)'s aqd:objectiveType xlink:href attribute resolve to http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/MO According to ANNEX X - MEASUREMENTS OF OZONE PRECURSOR SUBSTANCES (DIRECTIVE 2008/50/EC) Measurement of ozone precursor substances shall include at least nitrogen oxides (NO and NO2), and appropriate volatile organic compounds (VOC). A list of volatile organic compounds recommended for measurement is given below: 1-Butene Isoprene Ethyl benzene Ethane Trans-2-Butene n-Hexane m + p-Xylene Ethylene cis-2-Butene i-Hexane o-Xylene Acetylene 1,3-Butadiene n-Heptane 1,2,4-Trimethylebenzene Propane n-Pentane n-Octane 1,2,3-Trimethylebenzene Propene i-Pentane i-Octane 1,3,5-Trimethylebenzene n-Butane 1-Pentene Benzene Formaldehyde i-Butane 2-Pentene Toluene Total non-methane hydrocarbons
Count number of Assessment Regimes for pollutants with Monitoring Objetive
[Crucial]: N/A - IPR requirement (Annex II-C-4)
Check if combination of pollutant/EnvironmentalObjective for reporting PM2.5 National Exposure Reduction Target is included
Check Assessment Threshold Classification according to the allowed combination
Assess correctness of /aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:exceedanceAttainment depending on combination aqd:pollutant + aqd:objectiveType + aqd:reportingMetric + aqd:protectionTarget against vocabulary http://dd.eionet.europa.eu/vocabulary/aq/environmentalobjective/
Assessment Threshold classification required ratification.
[Crucial]: Yes - IPR requirement (Annex II-C-6) + correct content check vs AQD/IPR
Check modifications of Assessment Threshold Classification
Modification of Assessment Threshold Classification must be accompanied by change of classification year.
The assessement type shall be either "Fixed Measurement," "modelling," "Indicative Measurement", "Objective Estimation", or "other"
./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:assessmentType xlink:href attribute shall resolve to one of http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/[concept]Current options in the codelist are:http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/fixed http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/model http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/indicative http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/objective http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/other
The assessement type shall be either Fixed Measurement – Modelling – Objective Estimation or Indicative measurement
[Crucial]: Yes - IPR requirement (Annex II-C-9)
A textual description of assessment type is expected
./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:assessmentTypeDescription resolve to a text description of Assessment Type
[Crucial]: - IPR requirement (Annex II-C-9) https://taskman.eionet.europa.eu/issues/72746
When providing a link to model or objective estimation(s), a valid link must be provided
The assessment methods referenced by ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMetadata xlink:href attribute shall resolve to a traversable link to an assessment method /aqd:AQD_Model reported under cdr.eionet.europa.eu/ZZ/eu/aqd/d/… (The href is made using “namespace”/”localId”)
Invalid link to model or objetive estimation(s)
[Crucial]: Yes (crosscheck) - IPR requirement (Annex II-C-11)
When providing a link to fix or indicative measurement(s), a valid link must be provided
The assessment methods referenced by ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute shall resolve to a traversable link to an assessment method /aqd:AQD_SamplingPoint reported under cdr.eionet.europa.eu/ZZ/eu/aqd/d/… (The href is made using “namespace”/”localId”)
Invalid link to samplingPoint(s)
[Crucial]: Yes (crosscheck) - IPR requirement (Annex II-C-12)
Any assessment method used under Assessment must be operational within the Reporting Period
The assessment methods referenced by ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMeta data or ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute shall contain one element /aqd:AQD_Model/ef:observingCapability/ef:ObservingCapability/ef:observingTime/gml:TimePeriod/gml:endPosition or /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:observingTime/gml:TimePeriod/gml:endPosition that is operational within the aqd:reportingPeriod included in the ReportingHead
Some assessment method seem to be closed while being declared in the Assessment Regime. Please revise.
[Crucial]: Yes (crosscheck) - Crosscheck to ensure Method operational within Reporting Year
The number of zones must be the same as cited in the AssessmentRegime (for the same Reporting Year)
The number of unique zones cited by /aqd:AQD_AssessmentRegime shall be EQUAL to the number of unique zones in ./aqd:AQD_Zone for the same ReportingYear
A mismatch between zones linked in C and B has been identified. Please revise both deliveries
Crosscheck to ensure Zone operational within Reporting Year
The zone linked to each Assessment Regime must be operational within the Reporting Period
The lifecycle information of ./aqd:zone xlink:href shall be current,/aqd:AQD_Zone/am:designationPeriod/gml:TimePeriod/gml:endPosition shall be greater than the begin position of the aqd:reportingPeriod included in the ReportingHeader If endPosition is indeterminate (i.e.<gml:endPosition indeterminatePosition="unknown"/>) /aqd:AQD_Zone/am:designationPeriod/gml:TimePeriod/gml:beginPosition shall NOT be greater than the begin position of the aqd:reportingPeriod included in the ReportingHeader
The regime(s) for PM2.5 AEI (both ECO & ERT) MUST not link to any specific zone.
The regime(s) for PM2.5 AEI (both ECO & ERT) MUST not link to any specific zone. Specific syntax in XML is: <aqd:zone nilReason="inapplicable"/>
If the Asseement Metadata lifecycle information is current, then the Operational Activity End Time shall be within ReportingPeriod
The lifecycle information of ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href shall be current, /AQD_SamplingPoint/ef:operationActivityPeriod/gml:endPosition shall be operational within the aqd:reportingPeriod included in the ReportingHeader
[Crucial]: Yes - Crosscheck to ensure Method operational within Reporting Year - Important update, very similar to C26 (missing AQD_Model)
If a sampling point or a model is used in any Assessment Regime, it has to be described as TRUE for AQ Directive use
/aqd:AQD_SamplingPoint/aqd:usedAQD or /aqd:AQD_Model/aqd:used shall EQUAL “true” for all ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:[samplingPoint or model]AssessmentMetadata xlink:href citations
[Crucial]: Yes - Cross-check coherence between C & D
Delivery should contain one and only one Assessment Regime for PM2.5 Exposure Concentration Obligation (ECO)
There shall be only 1 record per MS where ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmental Objective/aqd:EnvironmentalObjective/aqd:objectiveType xlink:href attribute resolves to http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/ECO
Delivery should contain one and only one Assessment Regime for PM2.5 Exposure Reduction Target (ERT)
There shall be only 1 record per MS where ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmental Objective/aqd:EnvironmentalObjective/aqd:objectiveType xlink:href attribute resolves to http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/ERT
Assessment Regime for AEI is missing or multiple records have been provided (only 1 expected per country)
The cited stations under the Assessment Regime for the Average Exposure Indicator should be classified as Background.
Where./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:reportingMetric xlink:href attribute resolves to http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/AEI the /aqd:AQD_SamplingPoint/aqd:relevantEmissions/aqd:RelevantEmissions/aqd:stationClassification xlink:href attribute shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/stationclassification/background for all aqd:AQD_SamplingPoint linked via aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods /aqd:samplingPointAssessmentMetadata citations
SamplingPoint(s) declared for assessing AEI are not background
[Crucial]: Yes - INFORMATION, warnes if any AEI station is not background
Pollutant, Assessment Threshold and Environmental Objective shall equal one combination, except where Particulate Matter 2.5, which is not applicable.
aqd:zone xlink:href attribute shall resolve to a traversable link to an AQ zone in /aqd:AQD_Zone reported under cdr.eionet.europa.eu/ZZ/eu/aqd/b/... The ./aqd:pollutant and ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget within the Assessment Regime shall equal one combination /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode and /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:protectionTarget within the linked zone aqd:AQD_Zone/aqd:pollutantsException : Where ./aqd:pollutant resolves to http://dd.eionet.europa.eu/vocabulary/aq/pollutant/6001 ./aqd:zone xlink:href attribute MAY resolve to <aqd:zone nilReason='inapplicable'/>
A mismatch between the pollutant declared in Assessment Regime and the zone pollutant has been identified. Please revise.
[Crucial]: Yes (crosscheck) - Crosscheck to ensure Method operational within Reporting Year - Improved in cdr (swaped with C27)
COUNT number zone-pollutant-target comibantion to match those in dataset B for the same reporting Year
COUNT number zone-pollutant-target comibantion to match those in dataset B for the same reporting Year ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget + ./aqd:pollutant + /aqd:zone combinations shall reconcile to corresponding information within / aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:protectionTarget , /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode + /aqd:AQD_Zone/am:inspireId/base:Identifier/base:localId : Sulphur dioxide (1) + health (B vs C) & Sulphur dioxide (1) + vegetation (B vs C) & Ozone (7) + health (B vs C) & Ozone (7) + vegetation (B vs C) & Nitrogen dioxide (8) + health (B vs C) & Nitrogen oxides (9) + vegetation (B vs C) & Particulate matter < 10 µm (5) + health (B vs C) & Particulate matter < 2.5 µm (6001) + health (B vs C) & Carbon monoxide (10) + health (B vs C) & Benzene (20) + health (B vs C) & Lead in PM10 (5012) + health (B vs C) & Arsenic in PM10 (5018) + health (B vs C) & Cadmium in PM10 (5014) + health (B vs C) & Nickel in PM10 (5015) + health (B vs C) & Benzo(a)pyrene in PM10 (5029) + health (B vs C)
[Crucial]: Yes (crosscheck) - Updated in 4.0.2 if any C is greater than B = ERROR (RED) IF all B = C then OK if any C is smaller than B = WARNING
COUNT number zone-pollutant-target combination to match those in dataset C preliminary for the same reporting Year
COUNT number zone-pollutant-target comibantion to match those in dataset B for the same reporting Year ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget + ./aqd:pollutant + /aqd:zone combinations shall reconcile to corresponding information within / aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:protectionTarget , /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode + /aqd:AQD_Zone/am:inspireId/base:Identifier/base:localId : Sulphur dioxide (1) + health (C_pre vs C) & Sulphur dioxide (1) + vegetation (C_pre vs C) & Ozone (7) + health (C_pre vs C) & Ozone (7) + vegetation (C_pre vs C) & Nitrogen dioxide (8) + health (C_pre vs C) & Nitrogen oxides (9) + vegetation (C_pre vs C) & Particulate matter < 10 µm (5) + health (C_pre vs C) & Particulate matter < 2.5 µm (6001) + health (C_pre vs C) & Carbon monoxide (10) + health (C_pre vs C) & Benzene (20) + health (C_pre vs C) & Lead in PM10 (5012) + health (C_pre vs C) & Arsenic in PM10 (5018) + health (C_pre vs C) & Cadmium in PM10 (5014) + health (C_pre vs C) & Nickel in PM10 (5015) + health (B vs C) & Benzo(a)pyrene in PM10 (5029) + health (C_pre vs C)
Check Assessment Type of Asssessment Methods compared to assessmentType within Assessment Regime
./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:assessmentType shall be compared with the /aqd:AQD_SamplingPoint/aqd:assessmentType for assessment method cited by ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute and/or /aqd:AQD_Model/aqd:assessmentType for assessment method cited by ./aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute. The following combinations are allowed: Within AssessmentRegime Within SamplingPoint/Model Status: fixed fixed OK & indicative indicative/fixed OK & model model OK & objective objective OK & fixed indicative/model/objective WRONG & indicative fixed/model/objective WRONG & model fixed/indicative/objective WRONG & objective fixed/indicative/model OK
A mismatch has been detected between assessment types in Assessment Regime and assessment type in data flow D
Evaluate the consistency of SamplingPoints used for the assessment of PM2.5 AEI (ECO) and AEI (ERT) in current delivery. They should be the same.
Evaluate the continuity of Stations used for the assessment of PM2.5 AEI ECO compared to latest delivery from previous year
Evaluate the continuity of SamplingPoints used for the assessment of PM2.5 AEI ECO compared to latest delivery from previous year
All Assessment Regimes should be linked to at least one Assessment Method (either SamplingPoint or Model/ObjectiveEstimation)
The total number of /aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata and /aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMetadata citations within a MS (delivery) shall be GREATER THAN OR EQUAL to 1 where ./aqd:pollutant xlink:href attribute resolves to
Assessment Regime(s) must link to at least one assessment method. Please revise
[Crucial]: - IPR requirement (Annex II-C-11)
All Assessment Regimes must not be empty
Blocker will return if all Assessment Regimes are empty (i.e. not linked to an Assessment Method)
The year of the latest Classification report must be within the last 5 years according to AQ Directive
gml:timePosition MUST be provided and must be equal or greater than (aqd:reportingPeriod – 5 yeasr ) included in the ReportingHeader
Classification report needs updating, it is more than 5 years old.
[Crucial]: - IPR requirement (Annex II-C-7)
A valid url should be provided linking to the latest Classification Report
Free text shall be provided including at least 1 valid URL
[Crucial]: - IPR requirement (Annex II-C-8)
Alert & Information - At least one assessment regime for those Environmental Objectives with information and/or alert thresholds must be reported
At least one assessment regime for the following Environmental Objectives must be reported: NO2-Health-Alert, SO2-Health-Alert, O3-Health-Information & O3-Health-Alert.
INF and ALT thresholds - COUNT number zone-pollutant-target combination to match those in dataset B for the same reporting Year
COUNT number zone-pollutant-target comibantion to match those in dataset B for the same reporting Year ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget + ./aqd:pollutant + /aqd:zone combinations shall reconcile to corresponding information within / aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:protectionTarget , /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode + /aqd:AQD_Zone/am:inspireId/base:Identifier/base:localId : Sulphur dioxide (1) + health (B vs C) & Ozone (7) + health (B vs C) & Nitrogen dioxide (8) + health (B vs C)
INF and ALT thresholds - COUNT number zone-pollutant-target combination to match those in dataset C preliminary for the same reporting Year
COUNT number zone-pollutant-target comibantion to match those in dataset B for the same reporting Year ./aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget + ./aqd:pollutant + /aqd:zone combinations shall reconcile to corresponding information within / aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:protectionTarget , /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode + /aqd:AQD_Zone/am:inspireId/base:Identifier/base:localId : Sulphur dioxide (1) + health (Cprel vs C) & Ozone (7) + health (Cprel vs C) & Nitrogen dioxide (8) + health (Cprel vs C)
If classification is (LAT-UAT o aboveUAT or aboveLTO), there must be at least 1 assessmentMethod fixed
At least 1 assessmentMethod must be set to fixed when aqd:exceedanceAttainment is LAT-UAT, aboveUAT, or aboveLTO.
Assessment regime with exceedance in previous years should be classified as above UAT / LTO
If an assessment regime has reported exceedances in the previous year, the latest classification must be aboveUAT or aboveLTO.
Total number of individual element reported within this XML Document for assessment methods. Error wil be returned if any of the expected elements are missing.
Compile & feedback upon the total number of each environmental monitoring feature types included in the delivery
Total number of new records for each feature type included in the delivery. Error will be returned if all LocalIds are new.
Compile and feedback upon the total number of new records for each environmental monitoring feature types included in the delivery
Total number of updated records for each feature type included in the delivery. Error will be returned if all LocalIds are new.
Compile and feedback upon the total number of updated environmental monitoring feature types included in the delivery
Total number of updated records for each feature type included in the delivery. Blocker will be returned if D is not complete in relation to previous Delivery.
Compile and feedback upon the total number of updated environmental monitoring feature types included in the delivery. All feature types in the previous delivered must be included in this delivery to maintain historical information. If the update is genuine, please contact AQ IPR helpdesk.
Total number of updated records for each feature type included in the delivery. Blocker will be returned if D is not complete in relation to latest Delivery from previous year.
Compile and feedback upon the total number of updated environmental monitoring feature types included in the delivery. All feature types in the previous delivered (latest envelope from previous year) should be included in this delivery to maintain historical information. This is for information purposes.
Full list of reported Environmental Monitoring Features within this XML Document
Compile & feedback a list of the unique identifier information for each new record or modification to an environmental monitoring feature type. Feedback report shall include the gml:id attribute, ef:inspireId, aqd:inspireId, ef:name and/or ompr:name elements as available.
All gml:id attributes, ef:inspireId and aqd:inspireId elements shall have unique content
Id elements must have unique content
LocalId must be a unique code for the AQD_network (wtihin the unique namespace).
aqd:AQD_Network/ef:inspireId/base:Identifier/base:localId shall be an unique code for AQD_network and unique within the namespace.
LocalId must be a unique code for the AQD_network.
[Crucial]: Yes - IPR requirement (Annex II-D-ii-3)
List unique namespaces used and count number of Networks used. Error will be returned if namespace is not unique.
Count the number of unique AQD_Network (via localId) submitted within base:namespace. Blocker will be returned if base:namespace is not unique.
List unique namespaces used and count number of Networks used.
Must conform to a recognised media value. These are: Air, Biota, Landscape, Sediment, Soil/Ground, Waste and Water.
The content of aqd:AQD_Network/ef:mediaMonitored shall resolve to any concept inhttp://inspire.ec.europa.eu/codelist/MediaValue/
Must conform to a recognised Organisation Level. These are: International, Local, LocalAuthority, Municipality, National and Regional.
The content of aqd:AQD_Network/ef:organisationLevel shall resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/organisationallevel/
If provide, must conform to a recognised network type in the vocabulary.
The content of aqd:AQD_Network/aqd:networkType shall resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/networktype/
Check closed SPOs do not have data for closed periods
When a Sampling Point is closed, monitoring data for closed periods should not be in the system.
aqd:AQD_Network/aqd:operationActivityPeriod/gml:TimePeriod/gml:beginPosition shall be less than gml:endPosition
Network's Start time must be before End time.
[Crucial]: Yes - IPR requirement (Annex II-D-ii-36)
Network name is required. Please revise.
[Crucial]: Yes - IPR requirement (Annex II-D-ii-35)
Information on responsible authority for the network management must be provided
Not implemented - IPR requirement (Annex II-D-ii-36)
Must conform to a recognised Time Zone as vocabulary . These are UTC (+01 to +06) and (-01 to -06)
The content of /aqd:AQD_Network/aqd:aggregationTimeZone attribute shall resolve to a valid code in http://dd.eionet.europa.eu/vocabulary/aq/timezone/
Network's aggregation time zone is not correct
aqd:AQD_Station/ef:inspireId/base:Identifier/base:localId shall be an unique code within namespace
LocalId(s) for stations are not unique
[Crucial]: Yes - IPR requirement (Annex II-D-ii-1)
List unique namespaces used and count number of Stations used. Blocker will be returned if namespace is not unique.
Count the number of unique AQD_Station (via localId) submitted within base:namespace. Blocker will be returned if base:namespace is not unique.
Namespace are not unique
Station missing name
[Crucial]: Yes - IPR requirement (Annex II-D-ii-6) - Error, the provision of Station name is MANDATORY.
./ef:belongsTo shall resolve to a traversable local of global URI to ../AQD_Network
Station(s) are not linked to network
The content of /aqd:AQD_Station/ef:mediaMonitored shall resolve to any concept in http://inspire.ec.europa.eu/codelist/MediaValue/
The coordinate reference system for the stations must be defined with a correct uniform resource name
The srsName attribute within ./ef:geometry/gml:Point shall be a recognisable URN. The following 3 srsNames are expected urn:ogc:def:crs:EPSG::3035 or urn:ogc:def:crs:EPSG::4258 or urn:ogc:def:crs:EPSG::4326
Coordinate system for Station(s) needs revision
The location of the station must be correctly reported and within the countries' bounding box
./ef:geometry/gml:Point/gml:pos srsDimension attribute shall resolve to “2” to allow the coordinate of the station. ORDER of 2 coordinates MUST BE Latitude & Longitud when providing the accepted srsNames and found within the bounding box of the reporting country.
Coordinate provided for Stations needs revision as not latitude/Longitude
[Crucial]: Yes - IPR requirement (Annex II-D-ii-26) - Exception for FR
./ef:geometry/gml:Point shall resolve to within the geographic boundary or bounding box of the MS.
Check if the operational period for the station is within the network it belongs to.
List the total number aqd:AQD_Station invalid operational activity periods compared to aqd:AQD_Network
Station has incorrect operation period
[Crucial]: Yes - IPR requirement (Annex II-D-ii-7)
List the total number of aqd:AQD_Station which are operational ./ef:operationActivityPeriod/ef:OperationActivityPeriod/ef:activityTime/gml:TimePeriod/gml:endPosition which are unclosed (null) or have an indeterminatePosition="unknown" attribute
Total number of operational Stations
Station altitude must be provided in meters according to vocabulary and between -10 to 5700 meters
Altitude <aqd:altitude uom="http://dd.eionet.europa.eu/vocabulary/uom/length/m"> must be provided as valid number between -10 to 5.700 and unit of measurement must match http://dd.eionet.europa.eu/vocabulary/uom/length/m. Example: <aqd:altitude uom="http://dd.eionet.europa.eu/vocabulary/uom/length/m">570</aqd:altitude>
Station code must be unique, starting with ISO2-country code
AQD_Station/aqd:EUStationCode shall be an unique code for the station starting with ISO2-country code
EUStationCode(s) are not unique
[Crucial]: Yes, key - IPR requirement (Annex II-D-ii-2)
Station Meterological Parameters must conform to the standard "Climate and Forecast Standard" Subset of GRIB or the Meteo parameter list eionet data dictionary
The content of aqd:AQD_Station/aqd:meteoParams shall resolve to any concept in http://vocab.nerc.ac.uk/collection/P07/current/, http://vocab.nerc.ac.uk/collection/I01/current/, http://dd.eionet.europa.eu/vocabulary/aq/meteoparameter/
Not required - odd element if we really need to collect met data
Must conform to a recognised Station Classification from the eionet data dictionary. These are: Rural, Rural-Nearcity, Rural-Regional, Rural-Remote, Suburban, Urban
The content of aqd:AQD_Station/aqd:areaClassification shall resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/
Codelist for station classification requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-D-ii-28)
Must use a recognised Local description from the eionet data dictionary. These are: Canyon, Detached, Elevated and Open.
The content of aqd:AQD_Station/aqd:dispersionLocal shall resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/dispersionlocal/
Codelist for local dispersion requires revision: EEA codelist is required
Must use a recognised Regional descriptor: Alpine, Base, Basin-Hilly, Coast-Mount, Coast-Plane, Hilly, Mount, Mount-Slope, Plane, Valley-Hilly and Valley-Mount.
The content of aqd:AQD_Station/aqd:dispersionRegional shall resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/dispersionregional/
Codelist for regional dispersion requires revision: EEA codelist is required
AQD_SamplingPoint/ef:inspireId/base:Identifier/base:localId not unique codes:
LocalId(s) for samplingPoint(s) are not unique
List unique namespaces used and count number of SamplingPoint used.
Count the number of unique AQD_SamplingPoint (via localId) submitted within base:namespace.
[Crucial]: Yes - INSPIRE & system requirement
Must conform to the code 'air' in the Media codelist in the Inspire registry
The content of aqd:AQD_SamplingPoint/ef:mediaMonitored shall resolve to any concept inhttp://dd.eionet.europa.eu/vocabulary/inspire/MediaValue/
aqd:AQD_SamplingPoint/am:geometry/gml:Point the srsName attribute shall be a recognisable URN . The following 3 srsNames are expected urn:ogc:def:crs:EPSG::3035 or urn:ogc:def:crs:EPSG::4258 or urn:ogc:def:crs:EPSG::4326
Coordinate system for SamplingPoints needs revision
[Crucial]: Yes - Not required under IPR. However this is rather important
The Dimension attribute shall resolve to "2" and the order must be Latitude & Longitude
The srsDimension attribute within ./ef:geometry/gml:Point/gml:pos shall resolve to “2” to allow the x.y-coordinate of the station ORDER of 2 coordinates MUST BE Latitude & Longitude when providing the accepted srsNames (see D34)
Coordinate provided for SamplingPoints needs revision as not latitude/Longitude
The sampling point location shall resolve within the approximate location of the AQD_Station
./ef:geometry/gml:Point/gml:pos shall resolve to within the approximate geographic location of the AQD_Station cited by .aqd:AQD_SamplingPoint ef:broader
SamplingPoint coordinates seem to be too distant to the Station. Please revise
Check if the operational period for the Sampling Points is invalid or overlaps
.ef:observingCapability/ef:ObservingCapability/ef:observingTime/gml:TimePeriod/gml:beginPosition shall be equal to or less than ./ef:operationalActivityPeriod/ef:OperationalActivityPeriod/ef:activityTime/gml:TimePeriod /gml:endPosition gml:TimePeriod within the multiple ef:observingCapability MUST NOT overlap which each other
Operational times for SamplingPoins and Station need revising due to being invalid or overlap
[Crucial]: Yes - Quality check. Moved to d37a and d37b
Check if any sampling point includes more than one Operational Activity Period.
Sampling point can only include one ./ef:operationalActivityPeriod/ef:OperationalActivityPeriod. Multiple entries will be return error/blocker.
Check if the time period of the Observing Capability(ies) operate within overall OperationalActivity of the Sampling Points, are invalid and do not overlap
.ef:observingCapability/ef:ObservingCapability/ef:observingTime/gml:TimePeriod/gml:beginPosition shall be equal to or less than ./ef:operationalActivityPeriod/ef:OperationalActivityPeriod/ef:activityTime/gml:TimePeriod /gml:endPosition gml:TimePeriod within the multiple ef:observingCapability MUST NOT overlap which each other. The check will result in a warning if initial gaps are detected pre-eReporting (before 2013/01/01) The check will be skipped if d37a is a blocker.
Amended wording after improvements on d37a and d37b.
Check that a Sampling Point with only one Observing Capability has an OperationalActivityPeriod older than 12 years
A Sampling Point with only one Observing Capability is expected not to have OperationalActivityPeriod older than 12 years. In the live spam of a sampling points (with changes in equipment), multiple observing capabilities are expected.
Check if superseded SamplingPoint exists in previous deliveries.
Check if there is element <ef:supersedes/> in the delivery. This element must link to an existing SamplingPoint
Preventive check - Check if any SamplingPoint is being superseded or supersedes this delivery.
Preventive check if any SamplingPoint has element <ef:supersedes/> and/or <ef:supersededBy/> in the delivery. This is to ensure that the element is not misused and will prevent errors in the database.
Pollutant must be a registered under vocabulary and each SamplingPoint must be defined for a unique pollutant under all measurement configurations
The content of ../ef:observedProperty shall resolve to a valid code within http://dd.eionet.europa.eu/vocabulary/aq/pollutant/ and within a unique SamplingPoint, multiple ef:observedProperty may be found. These MUST always resolve to the same code
Codelist for all pollutants requires revision: EEA codelist is required
Links between SamplingPoint and Sample shall be traceable and valid
Cross-check with AQD_Sample (./ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest/@xlink shall resolve to a traversable local of global URI to an ../AQD_Sample)
Incorrect link between SamplingPoint and Sample
[Crucial]: YES, key check - System requirement
Links between SamplingPoint and SamplingPointProcess shall be traceable and valid
Cross-check with AQD_SamplingPointProcess (./ef:observingCapability/ef:ObservingCapability/ef:procedure/@xlink shall resolve to a traversable local of global URI to ../AQD_SamplingPointProcess)
Incorrect link between SamplingPoint and SamplingPointProcess
Links between SamplingPoint and Station shall be traceable and valid
Cross-check with AQD_Station (../ef:broader/@xlink shall resolve to a traversable local of global URI to ../AQD_Station)
Incorrect link between SamplingPoint and Station
[Crucial]: YES, key check - System requirement Works if all in one XML
Links between Station and Network shall be traceable and valid
Cross-check with AQD_Network (aqd:AQD_SamplingPoint/ef:belongsTo shall resolve to a traversable local of global URI to ../AQD_Network)
Incorrect link between Station and Network
Links between SamplingPoint and Network shall be traceable and valid
Cross-check with AQD_Network (aqd:AQD_Station/ef:belongsTo shall resolve to a traversable local of global URI to ../AQD_Network)
Incorrect link between SamplingPoint and Network
Invalid or overlapping operational activity periods
Total number aqd:AQD_SamplingPoint/ef:operationActivityPeriod/ef:OperationActivityPeriod/ef:activityTime/gml:TimePeriod/ invalid operational activity periods
Operational times for SamplingPoins need revising due to being invalid
Total number of AQD_SamplingPoints which are operational
Number of operational sampling points:
./ef:operationActivityPeriod/ef:OperationActivityPeriod/ef:activityTime/gml:TimePeriod/gml:endPosition with valid content (historical content) shall indicate that the environmental monitoring feature type is no longer operational.
Check that Assessment Type conforms to: Fixed, Indicative, Model or Objective
./aqd:assessmentType shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/ via xlink:href
Check that all elements under relevantEmissions conforms to registered vocabulary
Check that all elements under./aqd:relevantEmissions shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/ via xlink:href and http://dd.eionet.europa.eu/vocabulary/uom/ via uom. PLEASE NOTE the system expect the usage of FULL URL like: http://dd.eionet.europa.eu/vocabulary/uom/length/m http://dd.eionet.europa.eu/vocabulary/aq/emissionsource/2
Check that main emission source conforms to registered vocabulary
Check that Classifications conforms to: Background, Industrial or Traffic
Total number/aqd:stationClassification which resolve to http://dd.eionet.europa.eu/vocabulary/aq/stationclassification/ via xlink:href
Codelist for samplingPoint classification requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-D-ii-22)
Number of invalid 3 elements in Sampling Point and Environmental Objective combinations:
Number of invalid 3 elements aqd:AQD_SamplingPoint/aqd:environmentalObjective/aqd:EnvironmentalObjective/ combinations:
The Environmental Objective combination declared under SamplingPoint are invalid. Please revise.
Check if there are any invalid link from SamplingPoint to zone(s)
Number of invalid aqd:AQD_SamplingPoint/aqd:zone xlinks:
Incorrect link between SamplingPoint(s) and zone(s)
Local Id for Sampling Point Process must be unique
aqd:AQD_SamplingPointProcess/ompr:inspireId/base:Identifier/base:localId not unique codes:
LocalId(s) for samplingPointProcess(es) are not unique
List unique namespaces used and count number of SamplingPointProcess(es) used.
Count the number of unique AQD_SamplingPointProcess (via localId) submitted within base:namespace
Must conform to a recognised Measurement Type from the eionet data dictionary. These are: Active, Automatic, Passive, Remote and Unknown.
./aqd:measurementType shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/measurementtype/[concept]
Codelist for measurementType requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-D-ii-8)
If Measurement Type is Automatic or Remote, Measurement Method must be provided. However, Sampling Method and Technique shall not be provided.
If ./aqd:measurementType resolves to ./measurementtype/automatic or ./measurementtype/remote, aqd:measurementMethod & aqd:measurementEquipment MUST be included AND /aqd:samplingMethod and ./aqd:analyticalTechnique SHALL NOT BE PROVIDED
Key information is missing for automatic/remote methods
If Measurement Type is Active or Passive then Sampling Method and Analytical Technique must be provided. Measurement method shall not be provided.
If ./aqd:measurementType resolves to http://dd.eionet.europa.eu/vocabulary/aq/measurementtype/active or http://dd.eionet.europa.eu/vocabulary/aq/measurementtype/passive ./aqd:samplingMethod & ./aqd:analyticalTechnique shall be included AND ./aqd:measurementMethod SHALL NOT BE PROVIDED
Key information is missing for active/passive methods
Analytical Technique must use any of the analytical technique recognised methods in the eionet data dictionary.
The content of /aqd:AQD_SamplingPointProcess/aqd:analyticalTechnique shall resolve to any concept inhttp://dd.eionet.europa.eu/vocabulary/aq/analyticaltechnique/
Codelist for analyticalTechnique requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-D-ii-8+10)
When measurementMethod is provided, please use any of the measurement methods in the eionet data dictionary.
The content of aqd:measurementMethod MUST resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/measurementmethod/
When Sampling Equipment is provided, please use any of the sampling equipment in the eionet data dictionary.
The content of aqd:AQD_SamplingPointProcess/aqd:samplingEquipment/aqd:SamplingEquipment/aqd:equipment MUST resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/samplingequipment/
When Measurement Equipment is provided, please use any of the measurement equipment in the eionet data dictionary.
The content of aqd:measurementEquipment/aqd:MeasurementEquipment/aqd:equipment MUST resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/measurementequipment/
When Sampling Method is provided, please use any of the sampling methods in the eionet data dictionary.
The content of aqd:samplingMethod MUST resolve to any concept in http://dd.eionet.europa.eu/vocabulary/aq/samplingmethod/
Please contact IPR helpdesk in order to add new vocabulary for either MeasurementMethods/MeasurementEquipment/SamplingMethod/SamplingEquipment/AnalyticalTecnique
If /aqd:AQD_SamplingPointProcess/aqd:measurementMethod/aqd:MeasurementMethod/aqd:otherMeasurementMethod, /aqd:AQD_SamplingPointProcess/aqd:measurementEquipment/aqd:MeasurementEquipment/aqd:otherEquipment, /aqd:AQD_SamplingPointProcess/aqd:samplingMethod/aqd:SamplingMethod/aqd:otherSamplingMethod, /aqd:AQD_SamplingPointProcess/aqd:SamplingEquipment/aqd:SamplingEquipment/aqd:otherEquipment or /aqd:AQD_SamplingPointProcess/aqd:analyticalTechnique/aqd:AnalyticalTechnique/aqd:otherAnalyticalTechnique populated must give a warning to contact helpdesk to add new vocabulary
Method(s) and equipment(s) have been provided using the element Other
Method(s) and equipment(s) have been provided using the element
SamplingPointProcess parameters shall conform with registered vocabulary
./ompr:processParameter/ompr:ProcessParameter/ompr:name must correspond to a valid code under http://dd.eionet.europa.eu/vocabulary/aq/processparameter/
Codelist for process parameter requires revision: EEA codelist is required
If Detection Limit is specified, then a link to a concentration value from the eionet data dictionary must be provided.
Where ./aqd:detectionLimit is resolved uom link resolving to any concept in http://dd.eionet.europa.eu/vocabulary/uom/concentration/ shall be provided
Codelist for Detection Limit unit requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-D-ii-11)
Check that measurementMethod, aqd:samplingMethod & aqd:analyticalTechnique is persistent of the samplingPointProcess ID
f ./aqd:measurementType resolves to ./measurementtype/automatic or ./measurementtype/remote, aqd:measurementMethod MUST be the same as provided in previous delivery If ./aqd:measurementType resolves to http://dd.eionet.europa.eu/vocabulary/aq/measurementtype/active or http://dd.eionet.europa.eu/vocabulary/aq/measurementtype/passive /aqd:samplingMethod & ./aqd:analyticalTechnique MUST be the same as provided in previous delivery
Check persistence of sampling point process
Check persistence of sampling point process reported for same samplingpoint/observingCapability
Check that measurement equipment is for the right pollutant.
Check that the measurement equipment (https://dd.eionet.europa.eu/vocabulary/aq/measurementequipment) used is correct for the pollutant measured. Please contact the helpdesk if EEA vocabulary needs updating.
Time unit for process duration and cadence shall conform with registered vocabulary
./aqd:unit shall resolve to http://dd.eionet.europa.eu/vocabulary/uom/time/
Codelist for Time unit requires revision: EEA codelist is required
[Crucial]: - IPR requirement (Annex II-D-ii-14+15)
./aqd:numUnits shall contain an integer value
Not implemented - IPR requirement (Annex II-D-ii-14+15)
Sampling Process (used for compliance) was reported without or incorrect information on Equivalence demonstration.
Where ../AQD_SamplingPoint/aqd:usedAQD is “true”, ./aqd:equivalenceDemonstration/aqd:EquivalenceDemonstration/aqd:equivalenceDemonstrated must resolve to http://dd.eionet.europa.eu/vocabulary/aq/equivalencedemonstrated/
Information on reference/equivalence demonstration is required for SamplingPoints used for Assessement
[Crucial]: Yes - IPR requirement (Annex II-D-ii-12)
Sampling Process was reported without or incorrect information on Equivalence demonstration.
./aqd:equivalenceDemonstration/aqd:EquivalenceDemonstration/aqd:equivalenceDemonstrated should resolve to http://dd.eionet.europa.eu/vocabulary/aq/equivalencedemonstrated/ for all SamplingPointProcess
Sampling Process was declared as an equivalent method but the Demonstration Report was not provided.
SamplingPointProcess(es) declared as an equivalent method” i.e. http://dd.eionet.europa.eu/vocabulary/aq/equivalencedemonstrated/yes but /aqd:demonstrationReport not provided.
Equivalent demonstration report is missing
[Crucial]: Yes - IPR requirement (Annex II-D-ii-13)
Sampling Process is missing mandatory document on Traceability and Uncertainty Estimation or QA report
SamplingPointProcess(es) is missing mandatory document on Traceability and Uncertainty Estimation via aqd:AQD_SamplingPointProcess/aqd:dataQuality/aqd:DataQuality/aqd:documentation OR ./aqd:qaReport
Document on traceability and uncertatinity estimation or QA report missing
[Crucial]: Yes - IPR requirement (Annex II-D-ii-43+44)
Check closed SamplingPoints versus the link between Assessment Regimes and measurement methods
aqd:AQD_Sample/ompr:inspireId/base:Identifier/base:localId not unique codes:
LocalId(s) for sample(s) are not unique
List unique namespaces used and count number of Sample(s) used.
Count the number of unique AQD_Sample (via localId) submitted within base:namespace
./sams:shape/gml:Point the srsName attribute shall be a recognisable URN . The following 3 srsNames are expected urn:ogc:def:crs:EPSG::3035 or urn:ogc:def:crs:EPSG::4258 or urn:ogc:def:crs:EPSG::4326
Coordinate system for Sample needs revision
./sams:shape/gml:Point, the srsDimension attribute shall resolve to “2” to allow the coordinate of the feature of interest
The Sample should be located near the SamplingPoint
./sams:shape/gml:Point/gml:pos shall resolve to within the approximate geographic location of the sampling point referencing the ../AQD_Sample record via ../aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest
Same coordinates seem to be too distant to the SamplingPoint. Please revise
Distance to building should be provided if SamplingPoint is classified as Traffic
./aqd:builldingDistance shall contain a numerical value, WHERE ../aqd:AQD_SamplingPoint/aqd:relevantEmissions/aqd:RelevantEmissions/aqd:stationClassification = http://dd.eionet.europa.eu/vocabulary/aq/stationclassification/traffic AND ../aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest is xlinked to this./aqd:AQD_Sample via /aqd:inspireId/base:Identifier/base:localId
Traffic samplingPoint miss distance to building. Please revise Sample (inlet)
[Crucial]: - IPR requirement (Annex II-D-ii-20)
Distance to kerbside should be provided if SamplingPoint is classified as Traffic
./aqd:kerbDistance shall contain a numerical value, WHERE ../aqd:AQD_SamplingPoint/aqd:relevantEmissions/aqd:RelevantEmissions/aqd:stationClassification is EQUAL to http://dd.eionet.europa.eu/vocabulary/aq/stationclassification/traffic AND ../aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest is xlinked to this./aqd:AQD_Sample via /aqd:inspireId/base:Identifier/base:localId
Traffic samplingPoint miss distance to kerbside Please revise Sample (inlet)
[Crucial]: - IPR requirement (Annex II-D-ii-21)
Inlet Height must be in meters and between 0 to 30 meters. URL to uom must be full.
./aqd:inletHeight shall contain a numerical value between 0 to 30.0 and unit of measurement (uom) shall resolve to http://dd.eionet.europa.eu/vocabulary/uom/length/m
Inlet height is expected to use EEA uom vocabulary
[Crucial]: Yes - IPR requirement (Annex II-D-ii-19)
sam:sampledFeature shall resolve to a traversable local of global URI to an ../AQD_RepresentativeArea or a nilReason must be provided like <sam:sampledFeature nilReason="unknown"/>
./aqd:inspireId/base:Identifier/base:localId shall be an unique code for AQD_RepresentativeArea and unique within namespace
List unique namespaces used and count number of Sample used.
./aqd:InspireId/base:Identifier/base:namespace shall be a unique namespace identifier for the data source (within an annual e-Reporting cycle). The namespace value will be owned by the data provider of the spatial object
./sam:sampledFeature shall resolve to http://sweet.jpl.nasa.gov/2.2/realm.owl#Atmosphere
The srsName attribute within ./sams:shape/gml:Point shall be a recognisable URN. The following 3 srsNames are expected urn:ogc:def:crs:EPSG::3035 or urn:ogc:def:crs:EPSG::4258 or urn:ogc:def:crs:EPSG::4326 Alternatives, like http://www.opengis.net/gml/srs/epsg.xml#4258 or EPSG:4258 should be flagged as error
./sams:shape/gml:Polygon/gml:exterior/gml:LinearRing/gml:posList shall resolve to within the approximate geographic location of the sampling point referencing the
./sams:shape/gml:Polygon/gml:exterior/gml:LinearRing/gml:posList srsDimension attribute shall resolve to “2” to allow the x &y-coordinate of the feature of interest. ORDER of 2 coordinates MUST BE Latitude & Longitud when providing the accepted srsNames (see D81)
./sams:shape/gml:Polygon/gml:exterior/gml:LinearRing/gml:posList count attribute shall resolve to the sum of x-y coordinate doublets. ORDER of 2 coordinates doublets MUST BE Latitude & Longitud when providing the accepted srsNames (see D81)
./sams:shape/gml:Polygon/gml:exterior/gml:LinearRing/gml:posList shall resolve to the approximate geographic location of the sampling point referencing the
All reported Sample(s) shall be used within at least one SamplingPoint
Each aqd:AQD_Sample reported within the XML shall be xlinked (at least once) via aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest@xlink
Sample(s) are included which are not part of any measurement configuration
All reported SamplingPointProcess(es) shall be used wihtin at least one SamplingPoint
Each aqd:AQD_SamplingPointProcess reported within the XML shall be xlinked (at least once) via /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:procedure@xlink
SamplingPointProcess(es) are included which are not part of any measurement configuration
All reported Station(s) shall be used within at least one SamplingPoint
Each aqd:AQD_Station reported within the XML shall be xlinked (at least once) via aqd:AQD_SamplingPoint/ef:broader@xlink
Station(s) are included which are not part of any measurement configuration
All reported Networks shall be used within at least one SamplingPoint or one Station
Each aqd:AQD_Netwok reported within the XML shall be xlinked (at least once) via /aqd:AQD_SamplingPoint/ef:belongsTo@xlink or /aqd:AQD_Station/ef:belongsTo@xlink
Network(s) are included which are not part of any measurement configuration
Sampling point should belong to the same station as previous deliveries
Sampling points location is not expected to change compared to previous deliveries
Sampling points location is not expected to change compared to previous deliveries (latest reported).
Sampling point classification (Traffic, background, industrial ...) is not expected to change compared to previous year submission.
Sampling point aqd:stationClassification elements (Traffic, background, industrial ...) shall not be different from what was reported in previous year for the same sampling point.
Station area classification (Rural, sub-urban, urban...) is not expected to change compared to previous year submission.
Station aqd:areaClassification elements shall not be different from what was reported in previous year for the same station
Total number Observations within this XML Document
Compile & feedback upon the total number of observations included in the delivery
GML identifier for om:OM_Observation attribute shall be unique code
/om:OM_Observation gml:id attribute shall be unique code for the group of observations enclosed by /OM_Observation within the delivery. Please note that the om:OM_Observation do not have INSPIRE ID like all other elments with namespace & localId
Start time must be less than end time (phenomenonTime)
./om:phenomenonTime/gml:TimePeriod/gml:beginPosition shall be LESS THAN ./om:phenomenonTime/gml:TimePeriod/gml:endPosition.
The resultTime must be after the phenomenonTime
./om:resultTime/gml:TimeInstant/gml:timePosition shall be GREATER THAN ./om:phenomenonTime/gml:TimePeriod/gml:endPosition
Observation must link to a valid AQD_SamplingPointProcess in dataflow D (via om:procedure)
All om:OM_Observation/ must provide a valid /om:procedure xlink (can not be empty) & ./om:procedure xlink:href attribute shall resolve to a traversable link process configuration in Data flow D: /aqd:AQD_SamplingPointProcess/ompr:inspireld/base:Identifier/base:localId
[Crucial]: - IPR requirement (Annex II-E-7)
Observation must provide a link to SamplingPoint
A valid delivery MUST provide an om:parameter with om:name xlink:href to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/SamplingPoint
[Crucial]: Yes - IPR requirement (Annex II-E-)
Observation must link to a valid AQD_SamplingPoint in dataflow D (via om:parameter/...)
If ./om:parameter/om:NamedValue/om:name xlink:href resolves to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/SamplingPoint /om:parameter/om:NamedValue/om:value xlink:href attribute shall resolve to a traversable link to a unique AQD_SamplingPoint (“namespace/localId” of the object)
[Crucial]: Yes - IPR requirement (Annex II-E-7)
Observation should provide link to Assessment Type
A valid delivery should provide an om:parameter with om:name xlink:href to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/AssessmentType
[Crucial]: Yes - IPR requirement (Annex II-E-6)
Observation must provide a correct link to AssessmentType vocabulary
If ./om:parameter/om:NamedValue/om:name links to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/AssessmentType /om:parameter/om:NamedValue/om:value xlink:href attribute shall resolve to valid code for http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/
All observation paramater should link to be registered under vocabulary
OM observations shall contain several om:parameters to further define the observations. ./om:parameter/om:NamedValue/om:name xlink:href attribute shall resolve to a traversable link to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/
Pollutant must be a registered under vocabulary
./om:parameter/om:NamedValue/om:name xlink:href attribute shall resolve to a traversable link to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/
The pollutant for the observation must match the pollutant of the SamplingPoint
The pollutant xlinked via /om:observedProperty must match the pollutant code declared via /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:observedProperty (See E6 on linkages between the Observations & the SamplingPoint)
Mismatch between pollutant reported under Obseration and pollutant declared at SamplingPoint level
Observation must link to a valid AQD_Sample in dataflow D (via om:featureOfInterest)
All om:OM_Observation/ must provide a valid /om:featureOfInterest xlink (can not be empty)& /om:featureOfInterest xlink:href attribute shall resolve to a traversable link to /aqd:AQD_Sample/ompr:inspireld/base:Identifier/base:localId
Incorrect link between observation(s) and Sample(s)
The temporal envelopes of ./om:phenomenonTime/gml:TimePeriod/gml:beginPosition shall reconcile with /aqd:AQD_SamplingPoint/ef:operationalActivityPeriod/ef:OperationalActivityPeriod associated with the citations via /om:parameter/om:value xlink:href attribute AND /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:observingTime/gml:TimePeriod/ associated with /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:procedure the citations via /om:procedure xlink:href attribute
./om:result/swe:DataArray/swe:elementCount/swe:Count/swe:value shall resolve to the count of observations in /om:result/swe:DataArray/swe:values
IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="startTime" attribute THEN swe:Time definition=http://www.opengis.net/def/property/OGC/0/SamplingTime swe:uom xlink:href=http://www.opengis.net/def/uom/ISO-8601/0/Gregorian
Codelist for startTime definition requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-E-8)
IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="endTime" attribute THEN swe:Time definition=http://www.opengis.net/def/property/OGC/0/SamplingTime swe:uom xlink:href=http://www.opengis.net/def/uom/ISO-8601/0/Gregorian
Codelist for endTime definition requires revision: EEA codelist is required
Check valid definition for observation validity
IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="validity" attribute THEN swe:Category definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/observationvalidity
Codelist for observation Validity requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-E-12)
Check valid definition for observation verification
IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="verification" attribute THEN swe:Category definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/observationverification
Codelist for observation Verification requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-E-13)
Check valid definition for the observation values (primaryObservation code & concentration)
IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="Value" attribute THEN swe:Quantity definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/[code] & the swe:uom resolves to an xlink to http://dd.eionet.europa.eu/vocabulary/uom/concentration/[code]
Codelist for primaryObservations and/or concentration requires revision: EEA codelist is required
[Crucial]: Yes - IPR requirement (Annex II-E-5)
Check primaryObservation definition for the observation values are defined as /hour /day or /var
IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="Value" attribute THEN swe:Quantity definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/[code] & code should only be hour, day or var. Other definitions will be automatically converted to /var for aggregation purposes.
Check if data is provided using the recommended unit according to vocabulary. Important note: aggregates will not be calculated.
Check if the unit of measure reporting via (swe:uom) corresponds to the recommended unit of measure in vocabulary http://dd.eionet.europa.eu/vocabulary/uom/concentration/[code] depending on pollutant reported via /om:observedProperty . Important note: aggregates will not be calculated for those timeseries not using the recommended unit.
Check if data is provided using the recommended unit according to vocabulary
Check if data is provided using the mandatory unit according to vocabulary
Check if the unit of measure reporting via (swe:uom) corresponds to the mandatory unit of measure in vocabulary http://dd.eionet.europa.eu/vocabulary/uom/concentration/[code] depending on pollutant reported via /om:observedProperty
Check consistency of primaryObservatin (hour/day/var) with data already reported for same SamplingPoint
Check primaryObservation definition for the observation values (hour /day or /var) against Cadence/Duration reported in meta-data (D)
Check valid definition for the data coverage element (if provided)
A fifth element might be included. IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="DataCapture" attribute THEN swe:Category definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/dc & the swe:uom resolves to an xlink to http://dd.eionet.europa.eu/vocabulary/uom/statistics/percentage
Codelist for data coverage definition requires revision: EEA codelist is required
Check valid TextEncoding (decimalSeparator="." tokenSeparator=“”SEMICOLON”” blockSeparator="@@")
/om:result/swe:DataArray/swe:encoding/swe:TextEncoding shall resolve to decimalSeparator="." tokenSeparator=“”SEMICOLON”” blockSeparator="@@"
The primary data text encoding differs. Please revise if this causes a problem when processing data
The order of the fields within individual data blocks must correspond to the order described.
The order of the fields within individual data blocks (swe:values) must correspond to the order described within the swe:DataRecord/swe:field(multiple).
[Crucial]: Yes - System requirement (processing)
The count of values provided for observation should match the count declared and should not be 0.
The count of elements under <swe:elementCount><swe:Count><swe:value> should match the count of data blocks under <swe:values> and must be greater than 0.
The count of values provided for observation should match the count declared.
The primaryObsevation value can not be empty (NULL)
The primaryObsevation value provided in the swe:array can not be empty (NULL). This is incorrect: 2019-01-01T00:00:00+01:00,2019-01-01T01:00:00+01:00,1,-1,@@
Difference between endTime & startTime must correspond to the definition under <swe:field name="Value"><swe:Quantity definition=>.
Difference between endTime & startTime must correspond to the definition under <swe:field name="Value"><swe:Quantity definition=> .Difference between endTime & startTime must correspond to the definition: http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/hour must be 1 h or http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/day must be 24 hoursor http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/year must be 8760 hours or 8784 http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/var can be anything
All reported dates within the data array must be fully ISO
The temporal envelopes of the swe:values (reported via starTime and EndTime) shall reconcile with ./om:phenomenonTime/gml:TimePeriod/gml:beginPosition
The date-time of the primary data must be within the Reporting Year.
The /om:phenomenonTime/gml:TimePeriod/gml:beginPosition & gml:endPosition must correspond to the Reporting Year (For hourly and daily data, data must be within +/- 1 day. For var data, date-time must be within +/- 1 month)
The combination of SamplingPoint, SamplingPointProcess, Sample and Pollutant must be valid compared to latest Assessment Methods (D) reported
Check valid “constellation”: The combination of SamplingPoint, SamplingPointProcess, Sample and Pollutant must be valid compared to latest Assessment Methods (D) reported /om:parameter/om:NamedValue/om:value xlink:href attribute when /om:parameter/om:NamedValue/om:name xlink:href resolves to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/SamplingPoint + /om:procedure xlink:href attribute + /om:featureOfInterest xlink:href attribute + om:observedProperty xlink:href attribute must be found in latest metadata (D) as /aqd:AQD_SamplingPoint/ef:inspireId/base:localId (note xlink above include “namespace”) + /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:procedure + /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest + /aqd:AQD_SamplingPoint/ef:observingCapability/ef:ObservingCapability/ef:observedProperty
Incorrect link between observation(s) and SamplingPoint/SamplingPointProcess/Sample/Pollutant
The Assessment Methods must be operational for the reported primary data
The primary data reported within the XML file must correspond to a period when the assessment method is fully operational.
Check that all values (between @@) include as many fields as declared under swe:DataRecord
Incorrect number of values within data blocks (or incorrect format/codelist)
The data array should not end with "@@". Please note that @@ is a block separator.
Data array are not expected to end with @@""
Data array are not expected to end with "@@"
Check for unexpected spaces around all values (between comma separator) under swe:values
Unexpected spaces around data values are found. Please revise
Check for possible outliers reported. List of valid values found outside the range according to http://dd.eionet.europa.eu/vocabulary/aq/primaryObservationRange/
Please revise possible outliers on your primary validated data.
[Crucial]: Yes - System requirement (processing) - ErrorType downgraded to Warning on 25.07.2017
Check for possible outliers reported taking into account both country specific and general ranges.
Check for possible outliers reported. List of valid values found outside the range according to http://dd.eionet.europa.eu/vocabulary/aq/primaryObservationRange/ and http://dd.eionet.europa.eu/vocabulary/aq/primaryObservationRangeCountry/
Check for possible outliers reported taking into account country specific ranges.
Check for possible outliers reported taking into account country specific ranges. List of valid values found outside the range according to http://dd.eionet.europa.eu/vocabulary/aq/primaryObservationRangeCountry/
Check for date overlaps between consecutive data blocks within swe:values
Unexpected DATE overlaps are found in primary data. Please revise as this prevents correct harvesting.
[Crucial]: - Information to data provider - Label corrected on 26.07.2017
Check that all data submitted via CDR has been fully verified (flag 1)
Check that all data submitted via CDR has been fully verified. The verification flag must be 1 for all data.
Please revise verification status of data submitted as data is not completely fully verified.
[Crucial]: - Information to data provider
The average of valid data should not be 0 or negative
The average of valid data within individual swe:array MUST be above 0 (Negative or 0 averages are not expected).
The average of valid data is expected to be within 70 - 130% when comparing with the previous year
The average of valid data within each data:array is compared with the annual mean from previous year. In order to catch possible outliers, the data is expected to be within 70 - 130% when comparing with the previous year.
The average of valid data per timeseries reported.
Check if data's resultTime is newer than previously reported data for same SamplingPoint/Year
Check if the om:resultTime within the XML is newer than previously reported data for same SamplingPoint and reporting period (om:phenomenonPeriod)
Check that reported data is evenly distributed over the year in order to avoid skewing of results.Evaluate the spread of data.
Check that reported data is evenly distributed over the year in order to avoid skewing of results.
Observation must link to a valid AQD_ModelProcess in dataflow D (via om:procedure)
All om:OM_Observation/ must provide a valid /om:procedure xlink (can not be empty) & ./om:procedure xlink:href attribute shall resolve to a traversable link process configuration in Data flow D1b: /aqd:AQD_ModelProcess/ompr:inspireld/base:Identifier/base:localId
Observation must provide a link to Model or Objective
A valid delivery MUST provide an om:parameter/om:NamedValue/om:name xlink:href to either http://dd.eionet.europa.eu/vocabulary/aq/processparameter/model or http://dd.eionet.europa.eu/vocabulary/aq/processparameter/objective
Observation must link to a valid AQD_Model in dataflow D (via om:parameter/...)
If ./om:parameter/om:NamedValue/om:name xlink:href resolves to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/model or .../objective /om:parameter/om:NamedValue/om:value xlink:href attribute shall resolve to a traversable link to a unique AQD_Model (“namespace/localId” of the object)
Assessment type declared in Observation for a given Model/Objective Estimation should correspond to assessment type declared for that Model/Objective Estimation in Assessment Regimes (data set C).
Value of AssessmentType parameter in Observation should correspond with declaration given in aqd:assessmentType as xlink:href to http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/ in Assessment Regimes.
All the results paramater should link to be registered under vocabulary
OM observations shall contain several om:parameters to further define the model/objective estimation results ./om:parameter/om:NamedValue/om:name xlink:href attribute shall resolve to a traversable link to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/
. /om:observedProperty xlink:href attribute shall resolve to a traversable link to http://dd.eionet.europa.eu/vocabulary/aq/pollutant/
The pollutant for the observation must match the pollutant of the Model
The pollutant xlinked via /om:observedProperty must match the pollutant code declared via /aqd:AQD_Model/ef:observingCapability/ef:ObservingCapability/ef:observedProperty (See Eb6 on linkages between the Observations & the SamplingPoint)
Observation must link to a valid AQD_modelArea in dataflow D1b (via om:featureOfInterest)
All om:OM_Observation/ must provide a valid /om:featureOfInterest xlink (can not be empty)& /om:featureOfInterest xlink:href attribute shall resolve to a traversable link to /aqd:AQD_modelArea/ompr:inspireld/base:Identifier/base:localId
Results must provide result encoding (Inline or using external file)
A valid delivery MUST provide an om:parameter/om:NamedValue/om:name xlink:href to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/resultencoding & om:parameter/om:NamedValue/om:value xlink:href attribute shall resolve to valid code for http://dd.eionet.europa.eu/vocabulary/aq/ resultencoding/
Results must provide result format (swe array, shape file, geo tiff or Ascii grid)
A valid delivery MUST provide an om:parameter/om:NamedValue/om:name xlink:href to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/resultformat & om:parameter/om:NamedValue/om:value xlink:href attribute attribute shall resolve to valid code for http://dd.eionet.europa.eu/vocabulary/aq/resultformat/
Results must be provided using right combination between encoding & format and using the correct elements with XML
IF resultencoding = inline, resultformat can only be http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array & results reported under swe:array IF resultencoding = external resultformat can only be http://dd.eionet.europa.eu/vocabulary/aq/resultformat/ascii-grid , http://dd.eionet.europa.eu/vocabulary/aq/resultformat/esri-shp or http://dd.eionet.europa.eu/vocabulary/aq/resultformat/geotiff and results reported gml:File
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="startTime" attribute THEN swe:Time definition=http://www.opengis.net/def/property/OGC/0/SamplingTime swe:uom xlink:href=http://www.opengis.net/def/uom/ISO-8601/0/Gregorian
Check valid definition for startTime
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="endTime" attribute THEN swe:Time definition=http://www.opengis.net/def/property/OGC/0/SamplingTime swe:uom xlink:href=http://www.opengis.net/def/uom/ISO-8601/0/Gregorian
Check valid definition for endTime
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="validity" attribute THEN swe:Category definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/observationvalidity
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="verification" attribute THEN swe:Category definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/observationverification
Check valid definition for the observation values (primaryObservation/aggregationProcess code & concentration)
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="Value" attribute THEN swe:Quantity definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/[code] or http://dd.eionet.europa.eu/vocabulary/aq/aggregationprocess/[code] & the swe:uom resolves to an xlink to http://dd.eionet.europa.eu/vocabulary/uom/concentration/[code]
Check if the unit of measure reporting via (swe:uom) corresponds to the recommended unit of measure in vocabulary http://dd.eionet.europa.eu/vocabulary/uom/concentration/[code] depending on pollutant reported via /om:observedProperty
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then a fifth element might be included. IF ./om:result/swe:DataArray/swe:elementType/swe:DataRecord/swe:field name="DataCapture" attribute THEN swe:Category definition is defined by http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/dc & the swe:uom resolves to an xlink to http://dd.eionet.europa.eu/vocabulary/uom/statistics/percentage
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then /om:result/swe:DataArray/swe:encoding/swe:TextEncoding shall resolve to decimalSeparator="." tokenSeparator=“”SEMICOLON”” blockSeparator="@@"
Check valid TextEncoding of data array
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then the order of the fields within individual data blocks (swe:values) must correspond to the order described within the swe:DataRecord/swe:field(multiple).
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then the count of elements under <swe:elementCount><swe:Count><swe:value> should match the count of data blocks under <swe:values>.
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then difference between endTime & startTime must correspond to the definition under <swe:field name="Value"><swe:Quantity definition=> .Difference between endTime & startTime must correspond to the definition: http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/hour must be 1 h http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/day must be 24 hours http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/year must be 8760 hours or 8784 http://dd.eionet.europa.eu/vocabulary/aq/primaryObservation/var can be anything
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then the temporal envelopes of the swe:values (reported via starTime and EndTime) shall reconcile with ./om:phenomenonTime/gml:TimePeriod/gml:beginPosition
The combination of Model, ModelProcess, ModelArea (optional) and Pollutant must be valid compared to Assessment Methods (D1b), yearly specific, reported
Check valid “constellation”: The combination of Model – ModelProcess - (ModelArea) and Pollutant must be valid compared to latest Assessment Methods (D1b) reported /om:parameter/om:NamedValue/om:value xlink:href attribute when /om:parameter/om:NamedValue/om:name xlink:href resolves to http://dd.eionet.europa.eu/vocabulary/aq/processparameter/model or /objective + /om:procedure xlink:href attribute + /om:featureOfInterest xlink:href attribute (optional) + om:observedProperty xlink:href attribute must be found in metadata (D1b) year specific as /aqd:AQD_Model/ef:inspireId/base:localId (note xlink above include “namespace”) + /aqd:AQD_Model/ef:observingCapability/ef:ObservingCapability/ef:procedure + /aqd:AQD_Model/ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest (optional) + /aqd:AQD_Model/ef:observingCapability/ef:ObservingCapability/ef:observedProperty
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then check that all values (between @@) include as many fields as declared under swe:DataRecord
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then the data array should not end with "@@". Please note that @@ is a block separator.
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then check for unexpected spaces around all values (between comma separator) under swe:values
Empty
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then check for date overlaps between consecutive data blocks within swe:values
[Crucial]: Yes - Information to data provider
IF resultformat is http://dd.eionet.europa.eu/vocabulary/aq/resultformat/swe-array (Eb14) then check that all data submitted via CDR has been fully verified. The verification flag must be 1 for all data.
rangeParameters must be provided when reporting ascii grids - shape files or GeoTiff
IF resultformat is ascii-grid esri-shp or geotiff (Eb14) then ./om:result/gml:File/gml:rangeParameters MUST be populated
Aggregation process of the results must be provided and must match EEA vocabulary
IF resultformat is ascii-grid esri-shp or geotiff (Eb14) then ./om:result/gml:File/gml:rangeParameters/swe:Quantity@Definition MUST match a code under http://dd.eionet.europa.eu/vocabulary/aq/aggregationprocess/
A user-friendly label should be provided
IF resultformat is ascii-grid esri-shp or geotiff (Eb14) then ./om:result/gml:File/gml:rangeParameters/swe:label should be populated
A clear description of the results provided MUST be provided
IF resultformat is ascii-grid esri-shp or geotiff (Eb14) then ./om:result/gml:File/gml:rangeParameters/swe:description MUST be provided
Unit of the results must be provided and must match EEA vocabulary
IF resultformat is ascii-grid esri-shp or geotiff (Eb14) then ./om:result/gml:File/gml:rangeParameters/swe:Quantity/swe:uom xlink MUST match a code under http://dd.eionet.europa.eu/vocabulary/uom/concentration/ or http://dd.eionet.europa.eu/vocabulary/uom/statistics/
Check if the unit of measure reporting via (/om:result/gml:File/gml:rangeParameters/swe:uom) corresponds to the recommended unit of measure in vocabulary http://dd.eionet.europa.eu/vocabulary/uom/concentration/[code] depending on pollutant reported via /om:observedProperty
When reporting results using ASCII grid shape file or GeoTiff a reference must be provided to the result file
IF resultformat is ascii-grid esri-shp or geotiff (Eb14) then ./om:result/gml:File/gml:fileReference MUST be provided
When reporting results using ASCII grid, shape file or GeoTiff a reference must be provided to the result file
The result file (*.zip, *.shp ; *.tiff, *.asc) must follow this format: A valid cdr URL matching location of XML + File including extension + Variable using a # (e.g. #no2)
./om:result/gml:File/gml:fileReference MUST provide appropiate reference following this format: A valid cdr URL matching the cdr location where the XML files is located (e.g. http://cdr.eionet.europa.eu/es/eu/aqd/e1b/.../) + File including extension (e.g. model.zip) + Variable using a # (e.g. #no2). ONLY the following extensions are allowed: *.zip, *.shp ; *.tiff, *.asc
The result file must follow this format: A valid cdr URL matching location of XML + File including extension + Variable using a # (e.g. #no2)
When results are provided via an external file and the external file is ESRI shapefile, it must include the *.prj file
IF resultencoding = external resultformat, AND resultformat = esri-shp, THEN the external results provided must include the correct projection file. [Example: if results provided via gml:fileReference (http://cdr.eionet.europa.eu/es/eu/aqd/e1b/envxta1qq/ES_CIEMAT_O3_V_TV_AOT40c-5yr_2018.shp), the same envelope must include file ES_CIEMAT_O3_V_TV_AOT40c-5yr_2018.prj]
When results are provided via an external file, the XML must include an om:parameter with the modelprojection via EEA vocabulary, using SRID number directly or one of the following references: http://dd.eionet.europa.eu/vocabulary/common/epsg/, https://spatialreference.org/ref/epsg/ or https://epsg.io/
IF resultencoding = external resultformat, the XML must include an om:parameter with modelprojection <om:parameter> <om:NamedValue> <om:name xlink:href="https://dd.eionet.europa.eu/vocabulary/aq/modelparameter/projection"/> <om:value xlink:href="http://dd.eionet.europa.eu/vocabulary/common/epsg/4326"/> </om:NamedValue> </om:parameter> or <om:parameter> <om:NamedValue> <om:name xlink:href="http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/projection"/> <om:value xlink:href="https://spatialreference.org/ref/epsg/4326/"/> </om:NamedValue> </om:parameter> or <om:parameter> <om:NamedValue> <om:name xlink:href="http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/projection"/> <om:value xlink:href="https://epsg.io/4326"/> </om:NamedValue> </om:parameter> or <om:parameter> <om:NamedValue> <om:name xlink:href="http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/projection"/> <om:value xlink:href="4326"/> </om:NamedValue> </om:parameter>
When results are provided via an external file, the XML must include an om:parameter including the modelresolution via EEA vocabulary
IF resultencoding = external resultformat, the XML must include an om:parameter with modelresolution <om:parameter> <om:NamedValue> <om:name xlink:href="http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/resolution"/> <om:value xlink:href="http://dd.eionet.europa.eu/vocabulary/aq/modelresolution/5kmx5km"/> </om:NamedValue> </om:parameter>
When results are provided via an external file (compressed in a zip file), the compressed file can only contain one external result (i.e only one shape file for each zip file)
1. scan envelope to find all files with *.zip extension, 2. within each zip file count number of files with extensions such as: *.shp or *.tiff or *.tif or *.asc, 3. return BLOCKER if the count > 1 (ie each zip file should not contain more than 1 *.shp files, neither e.g. *.shp and *.asc).
When results are provided via an external file, all reported files (*.zip, *.shp ; *.tiff, *.tif, *.asc) must be referenced via gml:fileReference
All external files containing model results with allowed extensions (*.zip, *.shp ; *.tiff, *.tif, *.asc) must be referenced via gml:fileReference. Blocker will return if files are submitted which are not referenced in the XML.
When results are provided via an external file, definition of quantity must be provided and must match EEA vocabulary of aggregation processes.
./om:result/gml:File/gml:rangeParameters/swe:Quantity must refer to the correct vocabulary which is https://dd.eionet.europa.eu/vocabulary/aq/aggregationprocess, e.g.: <swe:Quantity definition ="http://dd.eionet.europa.eu/vocabulary/aq/aggregationprocess/P1Y">
When results are provided via an external file, the combinations of file#variable declared in XML must be unique, and the variables declared in XML after a # should be unique. QC should return WARNING if the variables are not unique. QC should return BLOCKER if the combinations of file#variable are not unique.
/om:result/gml:File/gml:fileReference#variable MUST provide unique combinations; #variable should be unique: - if the variables declared in ./om:result/gml:File/gml:fileReference after a # are unique (WARNING), - if the combinations of file#variable declared in ./om:result/gml:File/gml:fileReference are unique (BLOCKER)
Each E1b observation must point to unique combination of formed by model + procedure + observedProperty + featureOfInterest + definition.
Each <gml:featureMember><om:OM_Observation>...</om:OM_Observation></gml:featureMember> must contain unique set of identifiers/items for <om:name xlink:href="http://dd.eionet.europa.eu/vocabulary/aq/processparameter/model"/><om:value/>,<om:procedure/>,<om:observedProperty/>, <om:featureOfInterest /> and <swe:Quantity definition="http://dd.eionet.europa.eu/vocabulary/aq/aggregationprocess/...">
Declaration of aggregation process in E1b must match with reporting metric in C.
Declaration of aggregation process in E1b must match with aggregation process corresponding to reporting metric, objective, protection target and pollutant declared in C, for assessment regime where the model/objective estimation is used as assessment method.
Values provided within the data array must be interpretable and logically possible.
Values provided within data array must be below 100000. They should be provided as number or as indication of a value below certain threshold, e.g.: < 10 or <= 10
Combination of pollutant and aggregation process must match the one allowed in https://dd.eionet.europa.eu/vocabulary/aq/aggregationprocess
Combination of pollutant declared in <om:observedProperty.../> and aggregation process declared in <swe:Quantity definition=...> must match the one allowed in https://dd.eionet.europa.eu/vocabulary/aq/aggregationprocess (P1Y, P1M and P1D are exceptions matching all pollutants).
Attribute names specified in XML with url of external file must correspond univocally with the attribute names which can be found in dbf file of ESRI shapefile.
If there is one, unique attribute name in dbf, which is exactly the same as the one in XML, the test is passed. If there is no attribute name in dbf which is exactly the same or at least starts with string of attribute name specified in XML, the test will return BLOCKER. If there is more than one attribute name in dbf, which is exactly the same as the one in XML, the test will fail with BLOCKER. If there is one, unique attribute name in dbf which starts with string of attribute name specified in XML, but has more characters, the test will return ERROR. If there is more than one attribute name in dbf which starts with string of attribute name specified in XML, but has more characters, the test will fail with BLOCKER.
Compile & feedback upon the total number of attainment records included in the delivery
Number of Attainments reported
Number of new Attainments compared to previous report. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries
Compile & feedback upon the total number of new attainment records included in the delivery. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries.
Number of existing Attainment compared to previous report. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
Compile & feedback upon the total number of updated attainment records included in the delivery. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
List of unique identifier information for all attainment records. Blocker if no attainments
Compile & feedback a list of the unique identifier information for all attainment records included in the delivery. Feedback report shall include the gml:id attribute ./aqd:inspireId ./aqd:pollutant ./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType ./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:reportingMetric ./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget ./aqd:zone /aqd:assessment elements as available.
Compile & feedback a list of the exceedances situations when aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedance is TRUE
List number of final exceedances (TRUE)
Check and provide a list of those attainment records with a time extension
Compile & feedback a list of attainment records that have been assessed against the objectiveType for zones with time extensions ./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType/@xlink:href – “LVmaxMOT” link via ./aqd:zone to /aqd:AQD_Zone record & present the /aqd:AQD_Zone/aqd:timeExtensionExemption info. Feedback report shall include ./aqd:inspireId, ./aqd:pollutant, ./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType, ./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:reportingMetric, ./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget, ./aqd:zone, ./aqd:pollutant, /aqd:AQD_Zone/aqd:timeExtensionExemption
All gml ID attributes shall have unique code
Local Id must be unique for the attainment records
./aqd:inspireId/base:Identifier/base:localId must be unique code for the attainment records
The Attainment Pollutant must be one of the following: SO2, O3, NO2, NOX, PM10, PM2.5, CO, Pb in PM10, Cd in PM10, Ni in PM10, As in PM10, BaP in PM10
The content of ./aqd:pollutant xlink:href attribute shall resolve to one of http://dd.eionet.europa.eu/vocabulary/aq/pollutant/1 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/7 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/8 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/9 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/6001 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/10 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/20 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5012 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5014 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5015 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5018 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5029
Attainment has been provided for an unexpected pollutant.
[Crucial]: Yes - IPR requirement (Annex II-G-6)
INF and ALT thresholds - COUNT number zone-pollutant-target combination to match those in dataset B and dataset C for the same reporting Year
COUNT number zone-pollutant-target combination to match those in dataset B and dataset C for the same reporting Year & compare it with Attainment. Sulphur dioxide (1) + health (B vs C) & Ozone (7) + health (B vs C) & Nitrogen dioxide (8) + health (B vs C)
Exceedance Description Base is only expected for the following pollutants: SO2, PM10, PM2.5, CO
Element ./aqd:exceedanceDescriptionBase may only be used WHERE ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/1 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/6001 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/10
Attainment has been provided with a base scenario for an unexpected pollutant
Exceedance Description Adjustment is only expected for the following pollutants: SO2, PM10, PM2.5, CO
Element ./aqd:exceedanceDescriptionAdjustment can only be used WHERE ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/1 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/5 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/6001 http://dd.eionet.europa.eu/vocabulary/aq/pollutant/10
Attainment has been provided with an adjustment for an unexpected pollutant
Attainment should link to a valid assessment regime with matching Pollutant and Objetive Type
./aqd:assessment xlink:href attribute shall resolve to a valid assessment regime within / qd:AQD_AssessmentRegime AND /aqd:AQD_AssessmentRegime/aqd:pollutant, aqd:AQD_AssessmentRegime/aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType EQUAL to aqd:AQD_Attainment/aqd:pollutant aqd:AQD_Attainment/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType
Incorrect link between Attainment and Assessment Regime (including match Pollutant & ObjectiveType)
[Crucial]: Yes - IPR requirement (Annex II-G-7)
Attainment must link to a valid assessment regime with matching Pollutant and Protection Target
./aqd:assessment xlink:href attribute shall resolve to a valid assessment regime within / qd:AQD_AssessmentRegime AND /aqd:AQD_AssessmentRegime/aqd:pollutant, aqd:AQD_AssessmentRegime/aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget EQUAL to aqd:AQD_Attainment/aqd:pollutant aqd:AQD_Attainment/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget
Pollutant/ProtectionTarget mismatch between AssessmentRegime and Attainment. Please revise as this will cause problems when processing deliveries
Attainment should link to a valid assessment regime with matching Pollutant/Objective Type/ReportingMetric/ProtectionTarget/
aqd:AQD_Attainment/aqd:pollutant aqd:AQD_Attainment/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType aqd:AQD_Attainment/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:reportingMetric aqd:AQD_Attainment/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget should correspond with aqd:AQD_AssessmentRegime/aqd:pollutant aqd:AQD_AssessmentRegime/aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType aqd:AQD_AssessmentRegime/aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:reportingMetric aqd:AQD_AssessmentRegime/aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget
Environmental Objective mismatch between AssessmentRegime and Attainment. Please revise as this will cause problems when processing deliveries
COUNT number zone-pollutant-target combination to match those in dataset B and dataset C for the same reporting Year
COUNT number zone-pollutant-target combination to match those in dataset B and dataset C for the same reporting Year & compare it with Attainment. aqd:AQD_Attainment/aqd:pollutant xlink + aqd:AQD_Attainment/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget + aqd:AQD_Attainment/aqd:zone .aqd:assessmentThreshold/aqd:AssessmentThreshold/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:protectionTarget + ./aqd:pollutant + /aqd:zone combinations shall reconcile to corresponding information within /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:protectionTarget , /aqd:AQD_Zone/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode + /aqd:AQD_Zone/am:inspireId/base:Identifier/base:localId
Mismatch in the count of unique zone-pollutant-protectionTarget combinations between Attainment, AssessmentRegime and Zones
Changed to REGERROR following coordination meeting 12/02/2024
[Crucial]: Yes (crosscheck) - Important content check
All the /aqd:AQD_AssessmentRegime reported under latest dataflow C must be xlinked once at one Attainment (with exception of /MO)
For the same reporting year, all the /aqd:AQD_AssessmentRegime reported under dataflow C, must be xlinked once at /aqd:AQD_Attainment /aqd:assessment xlink:href attribute
Assessment Regimes are missing in Attainment. Please revise
The subject of ./aqd:zone xlink:href attribute shall resolve to a valid AQ zone with /aqd:AQD_Zone
Incorrect link between Attainment and Zone(s)
[Crucial]: Yes - IPR requirement (Annex II-G-4)
The attainment(s) for PM2.5 AEI (both ECO & ERT) MUST not link to any specific zone.
The attaniment(s) for PM2.5 AEI (both ECO & ERT) MUST not link to any specific zone. Specific syntax in XML is: <aqd:zone nilReason="inapplicable"/>
Linked zones must contain same pollutant as the Attainment
The subject of the ./aqd: zone xlink:href attribute shall contain a /aqd:AQD_Zone/aqd:pollutant EQUAL to ./aqd:pollutan
Mismtach between Attainment's pollutant and Zone's pollutant
Any attainment for LVmaxMOT should link to a zone with a time extension
The subject of the ./aqd: zone xlink:href attribute shall contain a /aqd:AQD_Zone/aqd:timeExtensionExemption shall NOT EQUAL http://dd.eionet.europa.eu/vocabulary/aq/timeextensiontypes/none WHERE ./aqd:exceedanceDescription_Final/aqd:ExceedanceDescription/aqd:environmentalObj ective/aqd:EnvironmentalObjective/aqd:objectiveType xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/LVmaxMOT
Objective Type must use one of the following: TV LV CL LVMOT LVmaxMOT INT ALT LTO ECO
./aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:objectiveType xlink:href attribute shall resolve to one of http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/LV http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/TV http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/LVMOT http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/LVmaxMOT http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/CL http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/LTO http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/ECO http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/INT http://dd.eionet.europa.eu/vocabulary/aq/objectivetype/ALT
Codelist for objective type requires revision (EEA codelist is required) or unexpected option
The Exceedence description must use an approved reporting metric, These are: Three consecutive hours in exceedance Annual mean / average , Winter Mean, Hours in exceedance in a calendar year, Days in exceedance in a calendar year, Days in exceedance averaged over 3 calendar years, Accumulated Ozone Exposure , Accumulated Ozone Exposure averaged over 5 years, Average Exposure Indicator
The content of ./aqd:EnvironmentalObjective/aqd:reportingMetric shall resolve to a valid concept in http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/ that must be one of http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/3hAbove http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/aMean http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/wMean http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/hrsAbove http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/daysAbove http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/daysAbove-3yr http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/maxd8hrMean http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/AOT40c http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/AOT40c-5yr http://dd.eionet.europa.eu/vocabulary/aq/reportingmetric/AEI
Codelist for reporting metric requires revision (EEA codelist is required) or unexpected option
The protection target must use the approved vocabulary
If ./aqd:protectionTarget shall resolve to a register vocabulary under http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/[Code]
Codelist for protection target requires revision (EEA codelist is required) or unexpected option
Check and list any invalid combination of pollutant & environmental objective
Invalid Environmental Objective combination found
All occurrences of the srsDimension attribute in ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:spatialExtent shall EQUAL “2”
All occurrences of the srsName attribute in ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:spatialExtent shall resolve to a valid spatial reference system URN or URI
/aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:surfaceArea uom attribute shall resolve to http://dd.eionet.europa.eu/vocabulary/uom/area/km2
/aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:roadLength uom attribute shall be http://dd.eionet.europa.eu/vocabulary/uom/length/km
Classification type must be one of the following: rural rural-nearcity rural-regional rural-remote urban suburban
The content of /aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:areaClassification xlink:xref shall resolve to a areaClassification in http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/ that must be one of Hide items http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-nearcity http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-regional http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-remote http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/urban http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/suburban
Codelist for classificationType requires revision: EEA codelist is required
The exceeding AQ_Model shall resolve to a traversable local of global URL.
./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute shall resolve to a model description in /aqd:AQD_Model
Incorrect link between attainment(s) and model(s)
The exceeding AQ_Model must be included in the corresponding AssessmentRegime
The subject of ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/ aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
Model used under attainment not included in corresponding Assessment Regime
The exceeding SamplingPoint shall resolve to a traversable local of global URL.
./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationUsed xlink:href attribute shall resolve to a sampling point description in /aqd:AQD_SamplingPoint
Incorrect link between attainment(s) and samplingpoint(s)
The exceeding SamplingPoint must be included in the corresponding AssessmentRegime
The subject of ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationlUsed xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
SamplingPoint used under attainment not included in corresponding Assessment Regime
./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:referenceYear/gml:TimeInstant/gml:timePosition shall specify a year in yyyy format.
Baseline exceedance must be TRUE or FALSE (if provided)
./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedance shall EQUAL “true” or “false”
Baseline Exceedance invalid
If baseline exceedance is TRUE numericalExceedance or numberExceedances must be provided
If ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedance is TRUE EITHER ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:numericalExceedance OR ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:numberExceedances must be provided AS an integer number
BaselineExceedance (TRUE) do not include numericalExceedance or numberExceedances.
[Crucial]: Yes - IPR requirement (Annex II-G-8+9)
If baseline exceedance is FALSE the provision of numericalExceedance or numberExceedances is useful
If ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:exceedance is FALSE EITHER ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:numericalExceedance OR ./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:numberExceedances must be provided AS an integer number
Deduction is not allowed when providing Baseline Exceedance
./aqd:exceedanceDescriptionBase/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:adjustmentType xlink:href attribute shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/adjustmenttype/noneApplied
When reporting aqd:exceedanceDescriptionBase, a correspoding aqd:exceedanceDescriptionAdjustment is expected
All occurrences of the srsName attribute in ./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:spatialExtent shall resolve to a valid spatial reference system URN or URI
/aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:surfaceArea uom attribute shall resolve to http://dd.eionet.europa.eu/vocabulary/uom/area/km2
/aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:roadLength uom attribute shall be http://dd.eionet.europa.eu/vocabulary/uom/length/km
./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute shall resolve to a model description in aqd:AQD_Model
The subject of ./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationUsed xlink:href attribute shall resolve to a sampling point description in /aqd:AQD_SamplingPoint
The subject of ./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationlUsed xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
If provided unde Adjustment Exceedance, area classification must be one of the following: rural rural-nearcity rural-regional rural-remote urban suburban
The content of /aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:environmentalObjective/aqd:EnvironmentalObjective/aqd:areaClassification xlink:xref shall resolve to a areaClassification in http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/ that must be one of Hide items http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-nearcity http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-regional http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-remote http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/urban http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/suburban
Codelist for area classification requires revision: EEA codelist is required
./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:referenceYear/gml:TimeInstant/gml:timePosition shall specify a year in yyyy format.
Adjusment exceedance must be TRUE or FALSE
./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:exceedance shall EQUAL “true” or “false”
Adjustment Exceedance invalid
[Crucial]: Yes - IPR requirement (Annex II-G-10+11)
If adjustment exceedance is TRUE numericalExceedance or numberExceedances must be provided
./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:numericalExceedance shall be an integer number
AdjustmentExceedance (TRUE) do not include numericalExceedance or numberExceedances.
If adjustment exceedance is FALSE the provision of numericalExceedance or numberExceedances is useful
./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:numberExceedances shall be an integer number
The Adjustment Method type shall be 'Natural source correction' or 'Winter-sanding or -salting correction'
The content of /aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:adjustmentType xlink:xref shall resolve to a adjustmentType in http://dd.eionet.europa.eu/vocabulary/aq/adjustmenttype/ that must be one of Hide items http://dd.eionet.europa.eu/vocabulary/aq/adjustmenttype/nsCorrection http://dd.eionet.europa.eu/vocabulary/aq/adjustmenttype/wssCorrection
The Adjustment Source Type must be one of the registered vocabulary.
The content of /aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:adjustmenSource xlink:xref shall resolve to a adjustmenSource in http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/ that must be one of Hide items http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/A1 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/A2 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/B http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/B1 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/B2 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/C1 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/C2 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/D1 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/D2 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/E1 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/E2 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/F1 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/F2 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/G1 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/G2 http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype/H
Codelist for adjustement source type requires revision: EEA codelist is required
Assessment Type must be one of the following: fixed, model, indicative or objective estimation
The content of ./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/ aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:assessmentType shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/ that must be one of Hide items http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/fixed http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/model http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/indicative http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/objective
Codelist for assessment type requires revision: EEA codelist is required
If adjusting for NS/WSS correction, a correct link must be provided to the adjusment method (either Model or SamplingPoint)
When adusting for NS/WSS correction, aqd:exceedanceDescriptionAdjustment must contain, at least, a link to the adjustment method used (via /aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/[aqd:modelAssessmentMetadata or samplingPointAssessmentMetadata] xlink:href
Incorrect link between adjustment method and samplingpoint(s) and/or model(s)
If model(s) or samplingPoint(s) are used for adjusting for NS/WSS correction, a correct link must be provided
The subject of ./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/[aqd:modelAssessmentMetadata or aqd:samplingPointAssessmentMetadata] xlink:href attribute shall be reported in dataflow D
If the adjustment method(s) are Model(s), these must be found with the corresponding Assessment Regime (link to the Attainment)
The subject of ./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:modelAssessmentMetadata xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
Model(s) used for adjustment not included in corresponding Assessment Regime
If the adjustment method(s) are SamplingPoint(s), these must be found with the corresponding Assessment Regime (link to the Attainment)
The subject of ./aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd: samplingPointAssessmentMetadata xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
SamplingPoint(s) used for adjustment not included in corresponding Assessment Regime
When reporting aqd:exceedanceDescriptionAdjustment, a correspoding aqd:exceedanceDescriptionBase is expected
Ensure that documentation is provided for Adjustments of Natural Source and/or Winter Sanding. Under /aqd:AQD_Attainment/aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:comment the full name of a pdf document attached to the G envelope must be provided
Ensure that documentation is provided for Adjustments of Natural Source and/or Winter Sanding. Under /aqd:AQD_Attainment/aqd:exceedanceDescriptionAdjustment/aqd:ExceedanceDescription/aqd:comment the full name of a pdf document attached to the G envelope must be provided (example: <aqd:comment>Spanish_adjustment_natural_contribution_2022.pdf</aqd:comment>
Exceedence area uom attribute must be in Square kilometers.
/aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:surfaceArea uom attribute shall resolve to http://dd.eionet.europa.eu/vocabulary/uom/area/km2
Codelist for exceedance area requires revision: EEA codelist is required
Road Length attribute must be in kilometers.
/aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:roadLength uom attribute shall be http://dd.eionet.europa.eu/vocabulary/uom/length/km
Codelist for road length requires revision: EEA codelist is required
Area Classification must be one of the following: rural rural-nearcity rural-regional rural-remote urban suburban
The content of /aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:areaClassification xlink:xref shall resolve to a areaClassification in http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/ that must be one of Hide items http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-nearcity http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-regional http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/rural-remote http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/urban http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/suburban
./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute shall resolve to a model description in /aqd:AQD_Model
The subject of ./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationUsed xlink:href attribute shall resolve to a sampling point description in /aqd:AQD_SamplingPoint
The subject of ./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationlUsed xlink:href attribute shall be found in /aqd:AQD_AssessmentRegime/aqd:assessmentMethods/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata xlink:href attribute for the AQD_AssessmentRegime record cited by ./aqd:assessment
./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:referenceYear/gml:TimeInstant/gml:timePosition shall specify a year in yyyy format.
./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedance shall EQUAL “true” or “false”
Final Exceedance invalid
[Crucial]: Yes - IPR requirement (Annex II-G-13)
If Final exceedance is TRUE numericalExceedance or numberExceedances must be provided
./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:numericalExceedance shall be an integer number
Final exceedance (TRUE) do not include numericalExceedance or numberExceedances.
[Crucial]: Yes - IPR requirement (Annex II-G-13
If Final exceedance is FALSE the provision of numericalExceedance or numberExceedances is useful
./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:numberExceedances shall be an integer number
Attainment(s) with NO exceedance do not include numericalExceedance or numberExceedances. This information is very useful, please provide.
aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod must be 'Fully corrected" when base/adjustment are provided.'
./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:adjustmentType xlink:href attribute shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/adjustmenttype/fullyCorrected when the attainment includes aqd:exceedanceDescriptionBase & aqd:exceedanceDescriptionAdjustment
Adjustment method (at Final exceedance) must be fully corrected
For each individual attainment, only 1 of the following elements is expected: numericalExceedance or numberExceedances (not BOTH)
Evaluate that the exceedance is correctly reported according to the particular Environmental Objective (aqd:numericalExceedance vs aqd:numberExceedance)
According to IPR decision, each Environmental Objective is defined by a particular reporting metric. Depending on the reporting metric, within Attainment declaration, a user will use either aqd:numericalExceedance for means, percentiles or AOT and aqd:numberExceedances for hoursAbove or daysAbove.
ExceedanceDescriptionBase, exceedanceDescriptionAdjustment and exceedanceDescriptionFinal should be consistent in terms of numericalExceedance or numberExceedance
Evaluate that the exceedanceDescriptionBase, exceedanceDescriptionAdjustment and exceedanceDescriptionFinal are consistently reported. aqd:numericalExceedance or aqd:numberExceedance consistent in the 3 elements.
Check if exceedance (TRUE/FALSE) correspond to the reported value aqd:numericalExceedance/aqd:numberExceedances/...
If exceedance is TRUE, a link to the exceeding SamplingPoint(s) and/or Model(s) must be provided [at least one]
WHERE ./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedance shall EQUAL “true” ./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationUsed OR ./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed shall be populated
Final exceedance (TRUE) do not include link to exceeding SamplingPoint(s) and/or Model(s)
If SamplingPoint(s) and/or Model(s) are provided, these must be valid
If, aqd:stationUsed and/or aqd:modelUsed are populated, these must be valid elements stationUsed must link To SamplingPoint via namespace/localid modelUsed must link to AQD_Model via namespace/ localid
Incorrect link between Attainment and exceeding SamplingPoin(s) and/or Model(s)
If exceedance is TRUE, information on population exposed must be provided
WHERE ./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedance shall EQUAL “true” /aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:populationExposed shall be populated
If exceedance is TRUE, information on area exposed must be provided
WHERE ./aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedance shall EQUAL “true”/aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:ecosystemAreaExposed shall be populated
Primary validated data (both E1a and/or E1b) must be submitted for all declared methods under Assessment Regime before releasing the Attainment.
Count the number of Sampling Points and Models in different dataflows such as E1a, E1b, C and G
Compare attainment results to previous year submission
When G report is submitted, compare the compliance status of each Attainment compared to previous reported information (for previous year).
Compare attainment results compared to current year (if an update)
When G report is updated, compare the compliance status of each Attainment compared to previous reported information (for same year).
For all attainments, numericalExceedance < -1 or numberExceedances < 0
aqd:numericalExceedance must be greater or equal to -1 & aqd:numberExceedance must be greater or equal to 0
An attainment for PM2.5 Exposure concentration obligationMUST be provided, it is has to be unique and the exceedance value reported via a unique element numericalExceedance. The reported AEI CANNOT be 0.
In order to ensure correct reporting of the AEI compliance, the unique attainment for PM2.5 Average Exposure Indicator must provide a unique element numericalExceedance. This will be the calculated AEI and CANNOT be 0.
An attainment for PM2.5 Exposure Reduction Target SHOULD be provided, it is has to be unique and the exceedance value reported via a unique element numericalExceedance. The reported AEI CANNOT be 0.
In order to ensure correct reporting of the ERT compliance, the unique attainment for PM2.5 Average Exposure Indicator must provide a unique element numericalExceedance. This will be the calculated AEI and CANNOT be 0.
Check PM2.5 Compliance against National Exposure Reduction Target
Check if at least one of the following combinations is reported (O3-INT, O3-ALT, NO2-ALT & SO2-ALT)
Check if at least there is on Attainment for the following combinations in the XML (O3-INT, O3-ALT, NO2-ALT & SO2-ALT)
Compile & feedback upon the total number of plans records included in the delivery
Compile & feedback upon the total number of new plans records included in the delivery (compared to any delivery for the same reporting year)
Number of new Plans compared to previous report(s).
Compile & feedback upon the total number of updated plans records included in the delivery. BLOCKER will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
Number of existing Plans compared to previous report (same reporting year). BLOCKER will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
List of unique identifier information for all Plan records. Error will be returned if no Plans are reported.
Compile & feedback a list of the unique identifier information for all Plans records included in the delivery. Feedback report shall include the gml:id attribute- ./aqd:inspireId- ./aqd:pollutant - ./aqd:protectionTarget - /gml:FeatureCollection/gml:featureMember/aqd:AQD_Plan/aqd:firstExceedanceYear -
Your plan should be for an expected pollutant and correctly use one of pollutants listed at http://dd.eionet.europa.eu/vocabulary/aq/pollutant/
aqd:AQD_Plan/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode xlink:href attribute shall resolve to one of http://dd.eionet.europa.eu/vocabulary/aq/pollutant/
Your plan should use one of pollutants listed at http://dd.eionet.europa.eu/vocabulary/aq/pollutant/
Reserved
All gml:id attributes - ef:inspireId and aqd:inspireId elements shall have unique content
./aqd:inspireId/base:Identifier/base:localId must be unique code for the Plans records
Local Id of the Plans must be unique.
Check if namespace is registered in vocabulary (http://dd.eionet.europa.eu/vocabulary/aq/namespace/view)
AQ Plan must link to a valid exceedance situation (G)
If aqd:AQD_ReportingHeader/aqd:reportingPeriod => 2013 aqd:AQD_Plan/aqd:exceedanceSituation@xlink:href attribute shall resolve to at least one exceedance situation in dataset G via namespace/localId.
AQ must link to a valid exceedande situation (G) if reporting period equal or greater than 2013.
aqd:comment should be provided if reporting period before than 2013 and a valid exceedande situation is not provided.
If aqd:reportingPeriod < 2013 and aqd:AQD_Plan/aqd:exceedanceSituation is empty aqd:comment must be populated
We recommend you start you codes with the 2-digit country code according to ISO 3166-1.
aqd:AQD_Plan/aqd:code should begin with with the 2-digit country code according to ISO 3166-1.
aqd:code must be populated & unique within the XML
aqd:code can not be EMPTY & the code provided must be unique within the XML delivered
You must provide the name of the organisation responsible for the Plan.
aqd:AQD_Plan/aqd:competentAuthority/base2:RelatedParty/base2:organisationName/gco:CharacterString shall not be NULL or voided
You should provide a contact point within the organisation responsible for the plan. This should be a generic contact point.
aqd:AQD_Plan/aqd:competentAuthority/base2:RelatedParty/base2:individualName/gco:CharacterString shall not be NULL or voided
You should provide an email address for the contact point within the organisation responsible for the plan (This should be a generic email address).
aqd:AQD_Plan/aqd:competentAuthority/base2:RelatedParty/base2:contact/base2:Contact/base2:electronicMailAddress shall not be NULL or voided
Your reference year must be in yyyy format.
aqd:AQD_Plan/aqd:firstExceedanceYear/gml:TimeInstant/gml:timePosition shall not be voided - NULL or an empty tag & shall contain content in yyyy format
Your plan status should use one of those listed at http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/
aqd:AQD_Plan/aqd:status xlink:href attribute shall resolve to one of http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/
Your plan should use one of protection targets listed at http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/
aqd:AQD_Plan/aqd:pollutants/aqd:Pollutant/aqd:protectionTarget xlink:href attribute shall resolve to one of http://dd.eionet.europa.eu/vocabulary/aq/protectiontarget/
Check and count expected combinations of Pollutant and ProtectionTarget at /gml:FeatureCollection/gml:featureMember/aqd:AQD_Plan/aqd:pollutants/aqd:Pollutant Sulphur dioxide (1) + health Sulphur dioxide (1) + vegetation Ozone (7) + health Ozone (7) + vegetation Nitrogen dioxide (8) + health Nitrogen oxides (9) + vegetation Particulate matter < 10 µm (5) + health Particulate matter < 2.5 µm (6001) + health Carbon monoxide (10) + health Benzene (20) + health Lead in PM10 (5012) + health Arsenic in PM10 (5018) + health Cadmium in PM10 (5014) + health Nickel in PM10 (5015) + health Benzo(a)pyrene in PM10 (5029) + health
AQ plan pollutant's should match those in the exceedance situation (G).
aqd:AQD_Plan/aqd:pollutants/aqd:Pollutant/aqd:pollutantCode xlink:href attribute (may be multiple) shall be the same as those in the referenced data flow G xlinked via aqd:AQD_Plan/aqd:exceedanceSituation@xlink:href attribute (maybe multiple)
Your reference year must be in yyyy-mm-dd format.
aqd:AQD_Plan/aqd:adoptionDate/gml:TimeInstant/gml:timePosition MUST be populated and its content in yyyy-mm-dd format if /gml:FeatureCollection/gml:featureMember/aqd:AQD_Plan/aqd:status xlink:href attribute not equal http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/preparation - http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/adoption-process or http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/under-revision
Plan adoption date should not be populated if plan is in preparation, under revision or in adoption process.
if /gml:FeatureCollection/gml:featureMember/aqd:AQD_Plan/aqd:status xlink:href attribute equal http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/preparation - http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/adoption-process or http://dd.eionet.europa.eu/vocabulary/aq/statusaqplan/under-revision aqd:AQD_Plan/aqd:adoptionDate/gml:TimeInstant/gml:timePosition should not be populated
You should report a short textual description of timetable for the implementation of the air quality plan.
aqd:AQD_Plan/aqd:timeTable shal contain a text string
You should report a URL to document or web resource describing the last version of full air quality plan.
aqd:AQD_Plan/aqd:referenceImplementation shall contain a URL to document or web resource describing the latest version of full air quality plan. This MUST be valid.
You should report a URL to a document or web resource where information about the implementation of the air quality plan can be found.
aqd:AQD_Plan/aqd:referenceImplementation must contain a URL to a document or web resource where information about the implementation of the air quality plan can be found.
Brief textual description of the published AQ Plan should be provided. Include the ISBN number (If available)
aqd:AQD_Plan/aqd:publication/aqd:Publication/aqd:description must contain a text string describing the publication
You should provide title as written in the published AQ Plan.
aqd:AQD_Plan/aqd:publication/aqd:Publication/aqd:title must contain the title of the publication
Author information for the AQ Plan report - multiple entries can be provided as a comma separate list.
aqd:AQD_Plan/aqd:publication/aqd:Publication/aqd:author must contain the author(s) of the publication
Author(s) should be provided as text (Please provide in one field separated by commas if there are multiple authors).
The publication date of the AQ Plan should be provided in yyyy or yyyy-mm-dd format
aqd:AQD_Plan/aqd:publication/aqd:Publication/aqd:publicationDate/gml:TimeInstant/gml:timePosition must contaong the date of publication in yyyy-mm-dd format
Publisher should be provided as a text (Publishing institution - academic jourmal – etc.)
aqd:AQD_Plan/aqd:publication/aqd:Publication/aqd:publisher must container a text string describing the publisher
Provided url to the published AQ Plan should be valid.
aqd:AQD_Plan/aqd:publication/aqd:Publication/aqd:webLink must contain a URL to document or web resource describing the last version of full air quality plan
Check if the delivery is a new or an update delivery (based on reporting year)
Check if the delivery is a new or an update delivery. If the system already includes a submission for the same data flow I for the same year, this will be considered as an update.
Number of source apportionment records in this delivery
Compile & feedback upon the total number of Source Apportionments included in the delivery
You must provide a reference to a plan document from data flow H via its namespace & localId. The plan document must have the same reporting year as the source apportionment document.
aqd:AQD_SourceApportionment/aqd:usedInPlan shall reference an existing H document for the same reporting year same year via namespace/localId
You must provide a reference to an exceedance situation from data flow G. The exceedance situation must have the same reporting year as the source apportionment and refer to the same pollutant.
aqd:AQD_SourceApportionment/aqd:parentExceedanceSituation shall reference an existing exceedance situation delivered within a data flow G and the reporting year of G & I shall be the same year via namespace/localId.
The exceedanceSituation linked (G) in this Source Apportionment (I) must be listed in the linked AQ Plan (H) for the same Source Apportionment (I)
HINT: Please ensure that the exceedanceSituation listed in the Source Apportionment listed (if there is an error), is also listed in the released AQ Plan (H) which the Source Apportionment also links too.
Reference year must be a calendar year in yyyy format.
aqd:AQD_SourceApportionment/aqd:referenceYear/gml:TimeInstant/gml:timePosition shall be a calendar year in yyyy format
Source apportionments values should be provided as a number.
Across all the delivery: check that the element aqd:QuantityCommented/aqd:quantity is number greater or equal to zero (>= 0) if attribute xsi:nil="false" (example: <aqd:quantity uom="http://dd.eionet.europa.eu/vocabulary/uom/concentration/ug.m-3" xsi:nil="false">4.03038</aqd:quantity>)
Source apportionments should be provided as an integer.
If quantification is either "unpopulated" or "unknown" or "withheld" the element should be empty.
Across all the delivery: check that the element aqd:QuantityCommented/aqd:quantity is empty if attribute xsi:nil="unpopulated" or "unknown" or "withheld" (example: <aqd:quantity uom="Unknown" nilReason="Unpopulated" xsi:nil="true"/>)
If the quantification is voided an explanation is required in aqd:comment.
Across all the delivery: If aqd:QuantityCommented/aqd:quantity attribute xsi:nil="true" aqd:QuantityCommented/aqd:comment must be populated
The unit of measurement of the Source Apportioment must match recommended unit for the pollutant.
Across all the delivery: check that the unit attribute (.../aqd:QuantityCommented/aqd:quantity@uom) corresponds to the recommended unit (via vocabulary) of the pollutant found at aqd:AQD_Attainment/aqd:pollutant xlink:href attribute for the AQD_Attainment record cited by ./aqd:parentExceedanceSituation
The total regional background source contribution must be equal to the sum of its components.
aqd:AQD_SourceApportionment/aqd:regionalBackground/aqd:RegionalBackground/aqd:total/aqd:QuantityCommented/aqd:quantity must equal to the sum of aqd:regionalBackground/aqd:RegionalBackground/aqd:fromWithinMS/aqd:QuantityCommented/aqd:quantity + aqd:regionalBackground/aqd:RegionalBackground/aqd:transboundary/aqd:QuantityCommented/aqd:quantity + aqd:regionalBackground/aqd:RegionalBackground/aqd:natural /aqd:QuantityCommented/aqd:quantity + aqd:regionalBackground/aqd:RegionalBackground/aqd:other/aqd:QuantityCommented/aqd:quantity
Number of NEW source apportionment records in this delivery.
Compile & feedback upon the total number of new Source Apportionments records included in the delivery. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries.
Number of new Source Apportionments compared to previous report. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries.
The total urban background source contribution must be equal to the sum of its components.
aqd:AQD_SourceApportionment/aqd:urbanBackground/aqd:UrbanBackground/aqd:total/aqd:QuantityCommented/aqd:quantity must equal the sum of aqd:urbanBackground/aqd:UrbanBackground/aqd:traffic/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:heatAndPowerProduction/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:agriculture/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:commercialAndResidential/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:shipping/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:offRoadMobileMachinery/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:natural/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:transboundary/aqd:QuantityCommented/aqd:quantity + aqd:urbanBackground/aqd:UrbanBackground/aqd:other/aqd:QuantityCommented/aqd:quantity
The total local increment source contribution must be equal to the sum of its components.
aqd:AQD_SourceApportionment/aqd:localIncrement/aqd:LocalIncrement/aqd:total/aqd:QuantityCommented/aqd:quantity must equal to the sum of aqd:localIncrement/aqd:LocalIncrement/aqd:traffic/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:heatAndPowerProduction/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:agriculture/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:commercialAndResidential/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:shipping/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:offRoadMobileMachinery/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:natural/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:transboundary/aqd:QuantityCommented/aqd:quantity + aqd:localIncrement/aqd:LocalIncrement/aqd:other/aqd:QuantityCommented/aqd:quantity
The macro exceedance situation relevant to the source apportionment must be populated.
aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation must be presented and must not be an empty tag
numericalExceedance or numberExceedances must be provided
Either aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:numericalExceedance OR aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:numberExceedances must be provided (just one or the other) AS an integer or floating point numeric > 0 (no more that 2 decimal places expected)
Area Classification is mandatory and must conform to vocabulary.
The content of /aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:areaClassification xlink:xref must be provided and must resolve to a areaClassification in http://dd.eionet.europa.eu/vocabulary/aq/areaclassification/
Area classification should match classification declared in the corresponding Attainment.
aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:areaClassification xlink:href attribute shall match those /aqd:AQD_Attainment/aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:areaClassification xlink:href attribute for the AQD_Attainment record cited by ./aqd:parentExceedanceSituation
Exceedence area uom attribute must be in Square kilometers (use http://dd.eionet.europa.eu/vocabulary/uom/area/km2).
/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:surfaceArea uom attribute shall resolve to http://dd.eionet.europa.eu/vocabulary/uom/area/km2
Road Length attribute must be in kilometers (use http://dd.eionet.europa.eu/vocabulary/uom/length/km).
/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:roadLength uom attribute shall be http://dd.eionet.europa.eu/vocabulary/uom/length/km
A link to the exceeding SamplingPoint(s) and/or Model(s) must be provided [at least one].
./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationUsed OR ./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed must be populated If using PAPERS, please ensure that A.2.5.6(a) or A.2.5.6(b) are filled in. For "Station used" ensure that you link to the SAMPLINGPOINT localId
Number of existing Plans compared to previous report. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
Compile & feedback upon the total number of updated Source Apportionments included in the delivery. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
If SamplingPoint(s) and/or Model(s) are provided these must be valid.
If aqd:stationUsed and/or aqd:modelUsed are populated these must be valid elementsstationUsed must link To SamplingPoint via namespace/localidmodelUsed must link to AQD_Model via namespace/ localidIf aqd:station
The models referenced here must be found in the Attainment document (dataflow G). The following models do not appear in the Attainment documents deliver for this reporting year.
The subject of ./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute shall be found in /aqd:AQD_Attainment/aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute for the AQD_Attainment record cited by ./aqd:parentExceedanceSituation
The exceeding AQ_Model must be included in the corresponding Attainment.
The link to sampling points referenced here must be found in the Attainment document (dataflow G). The following sampling points do not appear in the linked Attainment. Hint: do not xlink to station eiocode/localId
THIS CHECK IS NOT WORKING 100% HINT: Ensure the link is to a Sampling Point localId, NOT a station nor station EOICODE. The subject of ./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:stationlUsed xlink:href attribute shall be found in /aqd:AQD_Attainment/aqd:exceedanceDescriptionFinal/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:modelUsed xlink:href attribute for the AQD_Attainment record cited by ./aqd:parentExceedanceSituation
The exceeding SamplingPoint must be included in the corresponding Attainment.
Spatial extent or administrative unit may be provided.
./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:spatalExtent OR./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:administrativeUnit shall be populated
Information on surface area or road length shall be provided.
./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:surfaceArea OR./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceArea/aqd:ExceedanceArea/aqd:roadLength shall be populated
If exceedance is TRUE: information on population exposed must be provided.
WHERE./aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedance shall EQUAL “true” /aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:populationExposed shall be populated
If exceedance is TRUE: information on area exposed must be provided.
/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:ecosystemAreaExposed shall be populated
Reference year for the population/exposure data in yyyy format.
aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:ExceedanceExposure/aqd:referenceYear/gml:TimeInstant/gml:timePosition shall be a calendar year in yyyy format
Exceedance reason must match vocabulary.
aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:exceedanceExposure/aqd:reason shall conform to vocabulary http://dd.eionet.europa.eu/vocabulary/aq/exceedancereason/
If the pollutant is SO2 / PM10 / PM2.5 or CO, deduction assessment methods may be populated.
/aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod may be populated if ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/[1/5/10/6001] (via …/aqd:parentExceedanceSituation)
List of unique identifier information for all Source Apportionments records. ERROR will be returned if no SA(s) are provided.
Compile & feedback a list of the unique identifier information for all Source Apportionments records included in the delivery. Feedback report shall include the gml:id attribute - ./aqd:inspireId - aqd:AQD_Plan (via ./usedInPlan) - aqd:AQD_Attainment (via aqd:parentExceedanceSituation) - aqd:pollutant (via Attainment link under aqd:parentExceedanceSituation)
If the pollutant is SO2 / PM10 / PM2.5 or CO, the aqd:adjustmentType MUST be either (fullyCorrected noneApplicable noneApplied) under aqd:deductionAssessmentMethod
WHERE ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/[1/5/10/6001] (via …/aqd:parentExceedanceSituation then /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:adjustmentType must conform to http://dd.eionet.europa.eu/vocabulary/aq/adjustmenttype (fullyCorrected noneApplicable noneApplied)
If the pollutant is SO2 / PM10 / PM2.5 or CO, a description of the assessment type is expected.
WHERE ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/[1/5/10/6001] (via …/aqd:parentExceedanceSituation then /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:assessmentTypeDescription must be populated.
If the pollutant is SO2 / PM10 / PM2.5 or CO and deductionAssessmentMethod is populated, adjustmentType must be "fullyCorrected" (else "noneApplicable").
If aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:adjustmentType is populated WHERE ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/[1/5/10/6001] (via …/aqd:parentExceedanceSituation) the xlink:href must be "fullyCorrected" if another pollutant it must be "noneApplicable"
If the pollutant is SO2 / PM10 / PM2.5 or CO and deductionAssessmentMethod is populated, adjustmentSource must conform with vocabulary (else "noneApplicable").
WHERE ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/[1/5/10/6001] (via …/aqd:parentExceedanceSituation) then /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:adjustmentSource must be populated & the content of the xlink:href shall conform to http://dd.eionet.europa.eu/vocabulary/aq/adjustmentsourcetype (else this element must not be populated
If the pollutant is SO2 / PM10 / PM2.5 or CO and deductionAssessmentMethod is populated, adjustmentSource must conform with vocabulary (else
If the pollutant is SO2 / PM10 / PM2.5 or CO, a link to the assessment method in D or D1b is required via xlink:href attribute.
WHERE ./aqd:pollutant xlink:href attribute EQUALs http://dd.eionet.europa.eu/vocabulary/aq/pollutant/[1/5/10/6001] (via …/aqd:parentExceedanceSituation) at least one of /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata/@xlink:hrefor/aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:modelAssessmentMetadata/@xlink:href must be populated and correctly link to D/D1b. Cross check the links provided against D – all assessment methods must exist in D
If the pollutant is NOT SO2 / PM10 / PM2.5 or CO, the following elements are not expected: assessmentType link to adjusting sampling point/model, assessmentTypeDescription, assessmentType.
WHERE ./aqd:pollutant xlink:href attribute does NOT EQUAL http://dd.eionet.europa.eu/vocabulary/aq/pollutant/[1/5/10/6001] (via …/aqd:parentExceedanceSituatio) the following elments must be empty or not provided: /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:assessmentType ; /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:samplingPointAssessmentMetadata/@xlink:href ; /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:modelAssessmentMetadata/@xlink:href ; /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:assessmentTypeDescription ; /aqd:AQD_SourceApportionment/aqd:macroExceedanceSituation/aqd:ExceedanceDescription/aqd:deductionAssessmentMethod/aqd:AdjustmentMethod/aqd:assessmentMethod/aqd:AssessmentMethods/aqd:assessmentType
Local Id of the Source Apportionments must be unique.
List unique namespaces and count number of elements.
Compile & feedback upon the total number of scenario records included in the delivery
You must provide a reference to a plan document from data flow H via its namespace & localId. The plan document must have the same reporting year as the scenario document.
aqd:AQD_EvaluationScenario/aqd:usedInPlan shall reference an existing AQD_Plan (H) document for the same reporting year same year via namespace/localId
You must provide a link to a Source Apportionment (I) document from data flow I via its namespace & localId (for the same reporting year).
aqd:AQD_EvaluationScenario/aqd:sourceApportionment MUST reference an existing AQD_SourceApportionment (I) document via namespace/localId record for the same reporting year .
A code of the scenario should be provided as an alpha-numeric code starting with the country ISO code.
aqd:AQD_EvaluationScenario/aqd:codeOfScenario should begin with with the 2-digit country code according to ISO 3166-1.
Short textul description of the publication should be provided. Include the ISBN number if available.
aqd:AQD_EvaluationScenario/aqd:publication/aqd:Publication/aqd:description shall be a text string
You should provide title as written in the publication.
aqd:AQD_EvaluationScenario/aqd:publication/aqd:Publication/aqd:title shall be a text string
aqd:AQD_EvaluationScenario/aqd:publication/aqd:Publication/aqd:author shall be a text string (if provided)
The publication date should be provided in yyyy or yyyy-mm-dd format.
aqd:AQD_EvaluationScenario/aqd:publication/aqd:Publication/aqd:publicationDate/gml:TimeInstant/gml:timePosition may be a data in yyyy or yyyy-mm-dd format
Publisher should be provided as a text (Publishing institution / academic journal / etc.)
aqd:AQD_EvaluationScenario/aqd:publication/aqd:Publication/aqd:publisher shall be a text string
Url to the published AQ Scenario should be valid (if provided).
aqd:AQD_EvaluationScenario/aqd:publication/aqd:Publication/aqd:webLink as a valid url (if provided)
Number of new EvaluationScenarios compared to previous report.
Compile & feedback upon the total number of new EvaluationScenarios records included in the delivery. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries.
The year for which the projections are developed must be provided and the yyyy format must be used.
aqd:AQD_EvaluationScenario/aqd:attainmentYear/gml:TimeInstant/gml:timePosition must be provided and must conform to yyyy format
Reference year from which the projections started and for which the scenario is available must be provided and must conform to yyyy format.
aqd:AQD_EvaluationScenario/aqd:startYear/gml:TimeInstant/gml:timePosition must be provided and must conform to yyyy format
Check if start year of the evaluation scenario is the same as the source apportionment reference year.
Check aqd:AQD_EvaluationScenario/aqd:startYear/gml:TimeInstant/gml:timePosition must be equal to aqd:AQD_SourceApportionment/aqd:referenceYear/gml:TimeInstant/gml:timePosition referenced via the xlink of (aqd:AQD_EvaluationScenario/aqd:sourceApportionment)
A description of the emission scenario used for the baseline analysis should be provided as text.
aqd:AQD_EvaluationScenario/aqd:baselineScenario/aqd:Scenario/aqd:description shall be a text string
The baseline total emissions should be provided as integer with correct unit.
Check that the element aqd:AQD_EvaluationScenario/aqd:baselineScenario/aqd:Scenario/aqd:totalEmissions is an integer or floating point numeric >= 0 and the unit (@uom) shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/uom/emission/kt.year-1
The expected concentration (under baseline scenario) should be provided as an integer and its unit should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/concentration/).
Check that the element aqd:AQD_EvaluationScenario/aqd:baselineScenario/aqd:AQD_Scenario/aqd:expectedConcentration is an integer or floating point numeric >= 0 and the unit (@uom) shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/uom/concentration/
The number of exceecedance expected (under baseline scenario) should be provided as an integer
Check that the element aqd:AQD_EvaluationScenario/aqd:baselineScenario/aqd:AQD_Scenario/aqd:expectedExceedances is an integer or floating point numeric >= 0
The number of exceecedance expected (under baseline scenario) should be provided as an integer and its unit should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/statistics).
Measures identified in the AQ Plan that are included in this baseline scenario should be provided (link to dataflow K).
aqd:AQD_EvaluationScenario/aqd:baselineScenario/aqd:Scenario/aqd:measuresApplied shall reference an existing AQD_Measures delivered within a data flow K and the reporting year of K & J shall be the same year via namespace/localId.
A description of the emission scenario used for the projection analysis should be provided as text.
aqd:AQD_EvaluationScenario/aqd:projectionScenario/aqd:Scenario/aqd:description shall be a text string
The projection total emissions should be provided as integer with correct unit.
Check that the element aqd:AQD_EvaluationScenario/aqd:projectionScenario/aqd:Scenario/aqd:totalEmissions is an integer or floating point numeric >= 0 and the unit (@uom) shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/uom/emission/kt.year-1
Number of existing EvaluationScenarios compared to previous report. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
Compile & feedback upon the total number of updated EvaluationScenarios records included in the delivery. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
The expected concentration (under projection scenario) should be provided as an integer and its unit should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/concentration/).
Check that the element aqd:AQD_EvaluationScenario/aqd:projectionScenario/aqd:AQD_Scenario/aqd:expectedConcentration is an integer or floating point numeric >= 0 and the unit (@uom) shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/uom/concentration/
The number of exceecedance expected (under projection scenario) should be provided as an integer a
Check that the element aqd:AQD_EvaluationScenario/aqd:projectionScenario/aqd:AQD_Scenario/aqd:expectedExceedances is an integer or floating point numeric >= 0
The number of exceecedance expected (under projection scenario) should be provided as an integer and its unit should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/statistics).
Measures identified in the AQ Plan that are included in this projection should be provided (link to dataflow K).
aqd:AQD_EvaluationScenario/aqd:projectionScenario/aqd:Scenario/aqd:measuresApplied shall reference an existing AQD_Measures delivered within a data flow K and the reporting year of K & J shall be the same year via namespace/localId.
List of unique identifier information for all EvaluationScenarios records. It returns BLOCKER if no EvaluationScenarios are provided
List of evaluation scenario records in deliver & mandatory cross references. All evaluation scenarios must link to an AQ Plan document (H), a Source Apportionment record (I). A BLOCKER will return if either of these links are missing.
All gml:id attributes ef:inspireId and aqd:inspireId elements shall have unique content
Local Ids of the EvaluationScenarios must be unique & not empty
./aqd:inspireId/base:Identifier/base:localId must be unique code for the Scenario records & not empty
Local Ids of the EvaluationScenarios must be unique.
Lists unique namespaces and counts number of elements.
Compile & feedback upon the total number of Measures included in the delivery
Number of new Measures compared to previous report. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries.
Compile & feedback upon the total number of new Measures records included in the delivery. ERROR will be returned if XML is a new delivery and localId are not new compared to previous deliveries.
Number of existing Measures compared to previous report. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
Compile & feedback upon the total number of updated Measures included in the delivery. ERROR will be returned if XML is an update and ALL localId (100%) are different to previous delivery (for the same YEAR).
List of unique identifier information for all Measures records. It returns ERROR if no Measures are reported.
Compile & feedback a list of the unique identifier information for all Measures records included in the delivery. Feedback report shall include the gml:id attribute ./aqd:inspireId aqd:AQD_SourceApportionment (via ./exceedanceAffected) aqd:AQD_Scenario (via aqd:usedForScenario)
Local Ids of the Measures must be unique & not empty
./aqd:inspireId/base:Identifier/base:localId must be unique code for the Measure records & not empty
Lists unique namespaces used and counts number of elements.
You must provide a link to a source apportionment document from data flow I via its namespace & localId.
aqd:AQD_Measures/aqd:exceedanceAffected MUST reference an existing Source Apportionment (I) document via namespace/localId
A link may be provided to Evaluation Scenario (J). This must be valid via namespace & localId.
aqd:AQD_Measures/aqd:usedForScenario shall reference an existing Scenario delivered within a data flow J via namespace/localId.
Measure code should be a unique local identifier for each measure record. For convenience the same code as localId may be used.
aqd:AQD_Measures/aqd:code should be a unique local identifier for each measure record. For convenience the same code as localId may be used
You should provide a short name for the measure.
aqd:AQD_Measures/aqd:name must be populated with a text string
You should provide a short description of the measure.
aqd:AQD_Measures/aqd:description must be provided as a text string
Measure classification should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/aq/measureclassification/).
aqd:AQD_Measures/aqd:classification shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/aq/measureclassification/
Measure type should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/aq/measuretype/).
aqd:AQD_Measures/aqd:measureType shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/aq/measuretype/
Administrative level should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/aq/administrativelevel/).
aqd:AQD_Measures/aqd:administrativeLevel shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/aq/administrativelevel/
The measure's timescale should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/aq/timescale/).
aqd:AQD_Measures/aqd:timeScale shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/aq/timescale/
Information on the cost of the measure should be provided.
aqd:AQD_Measures/aqd:costs/ should be provided
The estimated total costs should be provided. If NOT an explanation on the reasons for not providing it should be included.
If aqd:costs provided aqd:AQD_Measures/aqd:costs/aqd:Costs/aqd:estimatedImplementationCosts should be an integer number. If voided /aqd:AQD_Measures/aqd:costs/aqd:Costs/aqd:comment must be populated with an explanation of why no costs are available.
If the final total costs of the measure is provided, it needs to be a number.
/aqd:AQD_Measures/aqd:costs/aqd:Costs/aqd:finalImplementationCosts should be an integer number if populated
The currency must be provided conforming to vocabulary (http://dd.eionet.europa.eu/vocabulary/common/currencies/), if estimated costs are provided.
If aqd:AQD_Measures/aqd:costs/aqd:Costs/aqd:estimatedImplementationCosts is populated aqd:AQD_Measures/aqd:costs/aqd:Costs/aqd:currency must be populated and shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/common/currencies/
Source sector should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/aq/sourcesectors/).
aqd:AQD_Measures/aqd:sourceSectors shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/aq/sourcesectors/
Spatial scale should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/aq/spatialscale/).
aqd:AQD_Measures/aqd:spatialScale shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/aq/spatialscale/
Measure Implementation Status should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/aq/measureimplementationstatus/).
aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:status shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/aq/measureimplementationstatus/
The planned start date for the measure should be provided in the right format.
aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:implementationPlannedTimePeriod/gml:TimePeriod/gml:beginPosition must be a date in full ISO date format
The planned end date for the measure should be provided in the right format. If unknown, it should be voided using indeterminatePosition="unknown".
If not voided aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:implementationPlannedTimePeriod/gml:TimePeriod/gml:endPosition must be a date in full ISO format and must be after aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:implementationPlannedTimePeriod/gml:TimePeriod/gml:beginPosition. If voided it should be indeterminatePosition="unknown"
The actual start date of the measure should be provided in the right format.
aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:implementationActualTimePeriod/gml:TimePeriod/gml:beginPosition must be a date in full ISO date format
The actual end date of the measure should be provided in the right format. If unknown, it should be voided using indeterminatePosition="unknown".
If not voided aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:implementationActualTimePeriod/gml:TimePeriod/gml:endPosition must be a date in full ISO format and must be after aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:implementationActualTimePeriod/gml:TimePeriod/gml:beginPosition. If voided it should be indeterminatePosition="unknown"
The full effect date of the measure must be provided and the format to be yyyy or yyyy-mm-dd.
aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:plannedFullEffectDate/gml:TimeInstant/gml:timePosition to be provided in the following format yyyy or yyyy-mm-dd
An explanation is expected under aqd:comment if monitoring progress indicators are not provided as text.
A text string may be provided under aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:monitoringProgressIndicators ; If voided an explanation of why this information unavailable shall be provided in /aqd:AQD_Measures/aqd:plannedImplementation/aqd:PlannedImplementation/aqd:comment
Reduction of emissions shall be provided as a number and unit should conform to vocabulary.
Check that the element aqd:AQD_Measures/aqd:reductionOfEmissions/aqd:QuantityCommented/aqd:quantity is an number or floating point numeric >= 0 if attribute xsi:nil="false" (example: <aqd:quantity uom="http://dd.eionet.europa.eu/vocabulary/uom/emission/t.year-1" xsi:nil="false">273</aqd:quantity>)
Reduction of emissions shall be provided as an integer and unit should conform to vocabulary.
If quantification is either "unpopulated" or "unknown" or "withheld" then the element should be empty.
Check that the element aqd:QuantityCommented/aqd:quantity is empty if attribute xsi:nil="unpopulated" or "unknown" or "withheld" (example: <aqd:quantity uom="Unknown" nilReason="Unpopulated" xsi:nil="true"/>)
If aqd:QuantityCommented/aqd:quantity attribute xsi:nil="true" aqd:QuantityCommented/aqd:comment must be populated
The quantification of reductionOfEmissions should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/emission).
The unit attribute (aqd:AQD_Measures/aqd:reductionOfEmissions/aqd:QuantityCommented/aqd:quantity/@UoM) shall correspond to http://dd.eionet.europa.eu/vocabulary/uom/emission
The level of concentration expected should be provided as an integer and its unit should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/concentration/).
Check that the element aqd:AQD_Measures/aqd:expectedImpact/aqd:ExpectedImpact/aqd:levelOfConcentration is an integer or floating point numeric >= 0 and the unit (@uom) shall resolve to the codelist http://dd.eionet.europa.eu/vocabulary/uom/concentration/
The number of exceecedance expected should be provided as an integer
Check that the element aqd:AQD_Measures/aqd:expectedImpact/aqd:ExpectedImpact/aqd:numberOfExceedances is an integer or floating point numeric >= 0
The number of exceecedance expected should be provided as an integer and its unit should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/statistics).
The specification of length should conform to vocabulary (use http://dd.eionet.europa.eu/vocabulary/uom/time/) and must be either /hour or /day.
Check that the element aqd:AQD_Measures/aqd:expectedImpact/aqd:ExpectedImpact/aqd:specificationOfHours xlinks to codelist http://dd.eionet.europa.eu/vocabulary/uom/time/ and the code is either /hour or /day
Total number of individual element reported within this XML Document for assessment methods (models/objective estimation)
Total number of new records for each feature type included in the delivery. Warning will be returned if all LocalIds are new.
Compile & feedback upon the total number of new records for each environmental monitoring feature types included in the delivery
Total number of updated records for each feature type included in the delivery. Warning will be returned if all LocalIds are new.
Compile & feedback upon the total number of modification to existing for each environmental monitoring feature types included in the delivery
./ef:inspireId/base:Identifier/base:localId shall be an unique code for AQD_Model and unique within the namespace. It is recommended to start with “MOD” and may include ISO2-country code (e.g.: MOD-ES0001)
List unique namespaces used and count number of Models used.
Count the number of unique AQD_Model (via localId) submitted within base:namespace.
Model name must be provided
The content of /ef:additionalDescription shall provide brief description for the model / objective estimation method
./ef:geometry shall contain a valid geometric property type, typically gml:Point, gml:MultiPoint, gml:Grid, gml:RectifiedGrid, gml:Polygon
Check if the operational period for the model is invalid or overlaps
.ef:observingCapability/ef:ObservingCapability/ef:observingTime/gml:TimePeriod/gml:beginPosition shall be equal to or less than ./ef:operationalActivityPeriod/ef:OperationalActivityPeriod/ef:activityTime/gml:TimePeriod /gml:endPosition - gml:TimePeriod within the multiple ef:observingCapability MUST NOT overlap which each other
Model has incorrect operation period
ef:processType must conform to codelist in the Inspire registry
./ef:observingCapability/ef:ObservingCapability/ef:processType shall resolve to “INSPIRE_OM_Process” via an XLINK: http://inspire.ec.europa.eu/codelist/ProcessTypeValue/process (currently resolves to 404 error)
ef:resultNature must conform to codelist in the Inspire registry
./ef:observingCapability/ef:ObservingCapability/ef:resultNature element shall resolve to http://inspire.ec.europa.eu/codelist/ResultNatureValue/simulated (currently resolves to 404 error)
./ef:observingCapability/ef:ObservingCapability/ef:observedProperty shall resolve to a valid code within http://dd.eionet.europa.eu/vocabulary/aq/pollutant/ Within a unique AQD_Model, multiple ef:observedProperty may be found. These MUST always resolve to the same code
Links between Model and ModelArea shall be traceable and valid
./ef:observingCapability/ef:ObservingCapability/ef:featureOfInterest shall resolve to a traversable link to a unique AQD_ModelArea (“namespace/localId” of the object)
Incorrect link between Model and ModelArea
Links between Model and ModelProcess shall be traceable and valid
./ef:observingCapability/ef:ObservingCapability/ef:procedure shall resolve to a traversable local of global URI to ../aqd:AQD_ModelProcess
Incorrect link between Model and ModelProcess
./ef:organisationLevel attribute shall resolve to a valid code in http://dd.eionet.europa.eu/vocabulary/aq/reportinglevel/ (e.g. http://dd.eionet.europa.eu/vocabulary/aq/reportinglevel/national
Number of invalid 3 elements in Model and Environmental Objective combinations:
Number of invalid 3 elements aqd:AQD_Model/aqd:environmentalObjective/aqd:EnvironmentalObjective/ combinations
The Environmental Objective combination declared under Model are invalid. Please revise.
Check that Assessment Type conforms to either Model or Objective
/aqd:assessmentType shall resolve to http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/ via xlink:href to either http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/model or http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/objective
If ./aqd:usedAQD equals “true”, the AQD_Model must be xlinked in at least at one /aqd:AQD_AssessmentRegime /aqd:assessmentMethods/aqd:AssessmentMethods/aqd:modelAssessmentMetadata (dataset C)
Check if there are any invalid link from Model to zone(s)
./aqd:zone shall resolve to a traversable local of global URI to AQD_Zones via xlink:href
Incorrect link between Model(s) and Zone(s)
ModelProcess localId must be unique within the namespace
./ompr:inspireId/base:Identifier/base:localId shall be an unique code for SamplingPointProcess and within the namespace
LocalId(s) for ModelProcess(es) are not unique
List unique namespaces used and count number of ModelProcess used.
./ompr:inspireld/base:Identifier/base:namespace shall be a unique namespace identifier for the data source (within an annual e-Reporting cycle). The namespace value will be owned by the data provider of the spatial object
./ompr:documentation/base2:DocumentationCitation/base2:link shall resolve to a traceable URL
./ompr:name shall resolve to provide a name for the model process configuration
ModelProcess requires a name. Please revise
Process parameter for both result-encoding and result-format must be provided
At least one ompr:processParameter/ompr:ProcessParameter/ompr:name MUST to be http://dd.eionet.europa.eu/vocabulary/aq/processparameter/resultencoding AND ompr:processParameter/ompr:ProcessParameter/ompr:description resolve to a text description and one ompr:processParameter/ompr:ProcessParameter/ompr:name MUST http://dd.eionet.europa.eu/vocabulary/aq/processparameter/resultformat AND ompr:processParameter/ompr:ProcessParameter/ompr:description resolve to a text description
[Crucial]: YES, key check - NEW - system requirement
ompr:processParameter/ompr:ProcessParameter/ompr:name shall resolve to a valid code within http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/ AND ompr:processParameter/ompr:ProcessParameter/ompr:description resolve to a text description of the model process -- e.g. <ompr:name xlink:href="http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/emissions"/> <ompr:description>NAEI2011 data, scaled forward to 2012 by linear interpolation between 2011 and projected (UEP45) 2012 data.</ompr:description>
Other model parameters may be reported
If the aqd:AQD_Model/aqd:assessmentType resolves to http://dd.eionet.europa.eu/vocabulary/aq/assessmenttype/model (please note that the link between AQD_Model and AQD_ModelProcess is made via an xlink with aqd:AQD_Model/ef:observingCapability/ef:ObservingCapability/ef:procedure - AQD_ModelProcess shall include a description of the following modelparameters: http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/chemistry http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/emissions http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/meterology http://dd.eionet.europa.eu/vocabulary/aq/modelparameter/topography
aqd:AQD_ModelProcess/aqd:description shall provide a free text description of the model - e.g. GIS-based dispersion kernel approach for 1x1km background concentrations from area source emissions, calibrated with monitoring. The contribution from point sources is estimated using a separate dispersion model and then included in the total. A bi-linear interpolation of corrected rural measurement data has been used to map regional background NOx concentrations throughout the UK.
ModelProcess requires a textual description. Please revise
The unit of the temporal resolution should be provided and conform with vocabulary
/aqd:AQD_ModelProcess/aqd:temporalResolution/aqd:TimeReferences/aqd:unit shall resolve to http://dd.eionet.europa.eu/vocabulary/uom/time/
Codelist for process time reference requires revision: EEA codelist is required
./aqd:spatialResolution shall provide a free text description of the spatial resolution of the model - e.g. 1x1km background concentrations
./dataQualityDescription shall provide a description of the quality of the model data / objective estimation in relation to the DQOs
Check Data Quality Report is provided via a traceable URL
./dataQualityReport shall provide a traceable URL (Note to data provider, the url should lead to a report describing the data quality equaluation process)
ModelArea localId must be unique within the namespace
./aqd:inspireId/base:Identifier/base:localId shall be an unique code for AQD_Sample and unique within the namespace
LocalId(s) for ModelArea(s) are not unique
List unique namespaces used and count number of ModelArea used.
./aqd:inspireId/base:Identifier/base:namespace shall be a unique namespace identifier for the data source (within an annual e-Reporting cycle). The namespace value will be owned by the data provider of the spatial object and will be registered in the INSPIRE External Object Identifier Namespaces Register
Check on ./sam:sampledFeature to be skipped. This element is not relevant and might contain xlink to http://sweet.jpl.nasa.gov/2.2/realm.owl or <sam:sampledFeature nilReason="inapplicable" xsi:nil="true"/>
The coordinate reference system for the ModelArea must be defined with a correct uniform resource name
/sams:shape/gml:Polygon, ./sams:shape/gml:Point, ./sams:shape/gml:MultiPoint, ./sams:shape/gml:MultiSurface, ./sams:shape/gml:Grid, ./sams:shape/gml:RectifiedGrid the srsName attribute shall be a recognisable URN. The following 3 srsNames are expected urn:ogc:def:crs:EPSG::3035 or urn:ogc:def:crs:EPSG::4258 or urn:ogc:def:crs:EPSG::4326
Coordinate system for ModelArea needs revision
./sams:shape shall contain a valid geometric property type typically gml:Point gml:MultiPoint gml:MultiSurface gml:Grid gml:RectifiedGrid OR gml:Polygon
./sams:shape shall contain a valid geometric property type, typically gml:Point, gml:MultiPoint, gml:MultiSurface, gml:Grid, gml:RectifiedGrid, gml:Polygon
.../gml:posList the count attribute shall resolve to the sum of y & x-coordinate doublets.
Coordinate provided for ModelArea needs revision as not all doublets
The coordinates must be ordered as latitude (y-axis) , longtitude (x-axis)
Check that the coordinates lists in .../gml:posList ar presented in lat / long (y-axis / x-axis) notation.
Coordinate provided for ModelArea needs revision as not latitude/Longitude
Check that the XML correctly provides XML's prefix/namespaces
Check prefix and namespaces of the gml:featureCollection according to expected root elements (More information at http://www.eionet.europa.eu/aqportal/datamodel)
gml:featureCollection requires revision
All EEA vocabulary links must be correctly constructed
Check through out the XML if any URL looks like "http://dd.eionet.europa.eu/vocabularyconcept/aq/". This should be BLOCKED as the EEA vocabulary should be: "http://dd.eionet.europa.eu/vocabulary/aq/"
All EEA vocabulary links must resolve to a correct link
All EEA vocabulary (starting like "http://dd.eionet.europa.eu/..." or ""https://dd.eionet.europa.eu/...") links must resolve to a correct link
XML validation to confirm that it is both well-formed and also "valid" in that it follows a defined structure. A well-formed document follows the basic syntactic rules of XML, which are the same for all XML documents.A valid document also respects the rules dictated by XML schema (http://dd.eionet.europa.eu/schemaset/id2011850eu-1.0/view)
XML failed to validate
Continuous/compact buildings along both sides of the street over more than 100 m. Average ratio of height of buildings to width of street > 0,5. (for this purpose "street" means the distance between the two facades of the buildings opposing each other, so including any pavements, gardens, etc.).
Detached buildings or one-sided compact buildings
Detached buildings on both sides of the street. Compact buildings on one side of the street, few buildings on the other side. Forest or groups or large trees in a surrounding of some 10 m
Summit, slope or saddle. Relative altitude of the station at least some 10 m related to surroundings of some 100 m. Monitoring stations located on towers or high buildings are not considered as “elevated”.
Flat area without large buildings or large trees in a surrounding of several 10 m
Area with relative altitudes above 1000 m on a scale of some 10 km, not located at the bottom of a valley or basin
Bottom of a basin (relative altitude less than 100 m) located at the border of mountains, surrounded by alpine or mountainous terrain on one side and flat or hilly terrain on the other side.
Bottom of a basin (relative altitude less than 100 m) in hilly terrain. A basin is characterized as flat or hilly terrain on a scale of 5 to some 10 km surrounded by hilly or mountainous terrain.
Bottom of a basin (relative altitude less than 100 m) in mountainous terrain.
Coast with mountainous terrain in interior
Marine coast with mountainous or alpine terrain (see above) in its interior
Marine coast with plane or hilly terrain (see above) in its interior
Area with relative altitudes between 100 and 300 m on a scale of several 10 km
Mountainous terrain – ridge, pass or summit
Area with relative altitudes between 300 and 1000 m on a scale of some 10 km.
Area with relative altitudes between 300 and 1000 m on a scale of some 10 km. Slope characterizes locations neither on valley bottom not on ridge, summit or pass.
Flat area on a scale of several 10 km with relative altitudes less than 100 m
Bottom of a valley (relative altitude less than 100 m) in hilly terrain
Bottom of a valley (relative altitude less than 100 m) in mountainous or alpine terrain
Fuel Combustion Activities - Energy Industries
Manufacturing Industries and Construction
Fuel Combustion Activities - Manufacturing Industries and Construction
Fuel Combustion Activities - Other sectors including: Commercial / Institutional Combustion, Residential & Agriculture / Forestry / Fishing.
Fuel Combustion Activities - Other (not elsewhere specified)
Fugitive Emissions from Fuels. Including Solid Fuels (1B1) and Oil & Natural Gas (1B2).
Industrial Processes including: Mineral Products (2A), Chemical Industry (2B), Metal Production (2C) and Other Production (2D).
Solvent and Other Product Use (Secondary solvents)
Solvent and Other Product Use including: Paint application (3A), Degreasing and Dry Cleaning (3B), Chemical Products, Manufacture and Processing (3C) and other (3D)
Agriculture. Including: Enteric Fermentation (4A), Manure Management (4B), Rice Cultivation (4C), Agricultural Soils (4D), Prescribed Burning of Savannas (4E), Field Burning of Agricultural (4F) or Other (4G).
Land use, land use change and forestry including: Forest land (5A), Cropland (5B), Grassland (5C), Wetlands (5D), Settlements (5E), Other land (5F) and other (5G)
Waste inclusing Solid Waste Disposal on Land (6A), Wastre-water Handling (6B), Waste Incineration (6C) and Other (6D).
Transport over distances of several 100 km, originating from sources which are distributed over a large area.
“Source” type which represent contributions not originating from identifiable sources
Secondary particles originating from gaseous pollutants, the sources of which are distributed over a large area.
AQD - Environmental objective combinations
Pollutant 1, Objective type LV, Metric hrsAbove, Target H
Pollutant 8, Objective type LV, Metric aMean, Target H
Pollutant 1771, Objective type MO, Metric NA, Target NA
Pollutant 1772, Objective type MO, Metric NA, Target NA
Pollutant 1629, Objective type MO, Metric NA, Target NA
Pollutant 1659, Objective type MO, Metric NA, Target NA
Pollutant 1657, Objective type MO, Metric NA, Target NA
Pollutant 1668, Objective type MO, Metric NA, Target NA
Pollutant 1631, Objective type MO, Metric NA, Target NA
Pollutant 2012, Objective type MO, Metric NA, Target NA
Pollutant 2014, Objective type MO, Metric NA, Target NA
Pollutant 2015, Objective type MO, Metric NA, Target NA
Pollutant 9, Objective type CL, Metric aMean, Target V
Pollutant 2018, Objective type MO, Metric NA, Target NA
Pollutant 7013, Objective type MO, Metric NA, Target NA
Pollutant 4013, Objective type MO, Metric NA, Target NA
Pollutant 4813, Objective type MO, Metric NA, Target NA
Pollutant 653, Objective type MO, Metric NA, Target NA
Pollutant 5013, Objective type MO, Metric NA, Target NA
Pollutant 5610, Objective type MO, Metric NA, Target NA
Pollutant 5617, Objective type MO, Metric NA, Target NA
Pollutant 5759, Objective type MO, Metric NA, Target NA
Pollutant 5626, Objective type MO, Metric NA, Target NA
Pollutant 5, Objective type LV, Metric daysAbove, Target H
Pollutant 5655, Objective type MO, Metric NA, Target NA
Pollutant 5763, Objective type MO, Metric NA, Target NA
Pollutant 7029, Objective type MO, Metric NA, Target NA
Pollutant 611, Objective type MO, Metric NA, Target NA
Pollutant 618, Objective type MO, Metric NA, Target NA
Pollutant 760, Objective type MO, Metric NA, Target NA
Pollutant 627, Objective type MO, Metric NA, Target NA
Pollutant 656, Objective type MO, Metric NA, Target NA
Pollutant 7419, Objective type MO, Metric NA, Target NA
Pollutant 20, Objective type MO, Metric NA, Target NA
Pollutant 5, Objective type LV, Metric aMean, Target H
Pollutant 428, Objective type MO, Metric NA, Target NA
Pollutant 430, Objective type MO, Metric NA, Target NA
Pollutant 432, Objective type MO, Metric NA, Target NA
Pollutant 503, Objective type MO, Metric NA, Target NA
Pollutant 505, Objective type MO, Metric NA, Target NA
Pollutant 394, Objective type MO, Metric NA, Target NA
Pollutant 447, Objective type MO, Metric NA, Target NA
Pollutant 6005, Objective type MO, Metric NA, Target NA
Pollutant 6006, Objective type MO, Metric NA, Target NA
Pollutant 6007, Objective type MO, Metric NA, Target NA
Pollutant 6001, Objective type ECO, Metric AEI, Target H
Pollutant 24, Objective type MO, Metric NA, Target NA
Pollutant 486, Objective type MO, Metric NA, Target NA
Pollutant 316, Objective type MO, Metric NA, Target NA
Pollutant 6008, Objective type MO, Metric NA, Target NA
Pollutant 6009, Objective type MO, Metric NA, Target NA
Pollutant 451, Objective type MO, Metric NA, Target NA
Pollutant 443, Objective type MO, Metric NA, Target NA
Pollutant 441, Objective type MO, Metric NA, Target NA
Pollutant 475, Objective type MO, Metric NA, Target NA
Pollutant 6001, Objective type LV, Metric aMean, Target H
Pollutant 449, Objective type MO, Metric NA, Target NA
Pollutant 21, Objective type MO, Metric NA, Target NA
Pollutant 431, Objective type MO, Metric NA, Target NA
Pollutant 464, Objective type MO, Metric NA, Target NA
Pollutant 482, Objective type MO, Metric NA, Target NA
Pollutant 6011, Objective type MO, Metric NA, Target NA
Pollutant 6012, Objective type MO, Metric NA, Target NA
Pollutant 32, Objective type MO, Metric NA, Target NA
Pollutant 25, Objective type MO, Metric NA, Target NA
Pollutant 8, Objective type MO, Metric NA, Target NA
Pollutant 10, Objective type LV, Metric daysAbove, Target H
Pollutant 5, Objective type MO, Metric NA, Target NA
Pollutant 6001, Objective type LV-S2, Metric aMean, Target H
in force from 2020 Note: Exceedance threshold (20 ugm-3) not included in vocabulary as it it not MANDATORY to report (prevent false error in QA)
Pollutant 9, Objective type MO, Metric NA, Target NA
Pollutant 38, Objective type MO, Metric NA, Target NA
Pollutant 5012, Objective type LV, Metric aMean, Target H
Pollutant 20, Objective type LV, Metric aMean, Target H
Pollutant 5014, Objective type TV, Metric aMean, Target H
Pollutant 1, Objective type LV, Metric daysAbove, Target H
Pollutant 5018, Objective type TV, Metric aMean, Target H
Pollutant 5015, Objective type TV, Metric aMean, Target H
Pollutant 5029, Objective type TV, Metric aMean, Target H
Pollutant 1045, Objective type MO, Metric aMean, Target NA
Pollutant 1046, Objective type MO, Metric aMean, Target NA
Pollutant 1047, Objective type MO, Metric aMean, Target NA
Pollutant 1771, Objective type MO, Metric aMean, Target NA
Pollutant 1772, Objective type MO, Metric aMean, Target NA
Pollutant 1629, Objective type MO, Metric aMean, Target NA
Pollutant 1659, Objective type MO, Metric aMean, Target NA
Pollutant 1, Objective type CL, Metric aMean, Target V
Pollutant 1657, Objective type MO, Metric aMean, Target NA
Pollutant 1668, Objective type MO, Metric aMean, Target NA
Pollutant 1631, Objective type MO, Metric aMean, Target NA
Pollutant 2012, Objective type MO, Metric aMean, Target NA
Pollutant 2014, Objective type MO, Metric aMean, Target NA
Pollutant 2015, Objective type MO, Metric aMean, Target NA
Pollutant 2018, Objective type MO, Metric aMean, Target NA
Pollutant 7013, Objective type MO, Metric aMean, Target NA
Pollutant 4013, Objective type MO, Metric aMean, Target NA
Pollutant 4813, Objective type MO, Metric aMean, Target NA
Pollutant 1, Objective type CL, Metric wMean, Target V
Pollutant 653, Objective type MO, Metric aMean, Target NA
Pollutant 5013, Objective type MO, Metric aMean, Target NA
Pollutant 5610, Objective type MO, Metric aMean, Target NA
Pollutant 5617, Objective type MO, Metric aMean, Target NA
Pollutant 5759, Objective type MO, Metric aMean, Target NA
Pollutant 5626, Objective type MO, Metric aMean, Target NA
Pollutant 5655, Objective type MO, Metric aMean, Target NA
Pollutant 5763, Objective type MO, Metric aMean, Target NA
Pollutant 7029, Objective type MO, Metric aMean, Target NA
Pollutant 611, Objective type MO, Metric aMean, Target NA
Pollutant 7, Objective type TV, Metric daysAbove-3yr, Target H
Pollutant 618, Objective type MO, Metric aMean, Target NA
Pollutant 760, Objective type MO, Metric aMean, Target NA
Pollutant 627, Objective type MO, Metric aMean, Target NA
Pollutant 656, Objective type MO, Metric aMean, Target NA
Pollutant 7419, Objective type MO, Metric aMean, Target NA
Pollutant 20, Objective type MO, Metric aMean, Target NA
Pollutant 428, Objective type MO, Metric aMean, Target NA
Pollutant 430, Objective type MO, Metric aMean, Target NA
Pollutant 432, Objective type MO, Metric aMean, Target NA
Pollutant 503, Objective type MO, Metric aMean, Target NA
Pollutant 7, Objective type LTO, Metric daysAbove, Target H
Pollutant 505, Objective type MO, Metric aMean, Target NA
Pollutant 394, Objective type MO, Metric aMean, Target NA
Pollutant 447, Objective type MO, Metric aMean, Target NA
Pollutant 6005, Objective type MO, Metric aMean, Target NA
Pollutant 6006, Objective type MO, Metric aMean, Target NA
Pollutant 6007, Objective type MO, Metric aMean, Target NA
Pollutant 24, Objective type MO, Metric aMean, Target NA
Pollutant 486, Objective type MO, Metric aMean, Target NA
Pollutant 316, Objective type MO, Metric aMean, Target NA
Pollutant 6008, Objective type MO, Metric aMean, Target NA
Pollutant 7, Objective type TV, Metric AOT40c-5yr, Target V
Pollutant 6009, Objective type MO, Metric aMean, Target NA
Pollutant 451, Objective type MO, Metric aMean, Target NA
Pollutant 443, Objective type MO, Metric aMean, Target NA
Pollutant 441, Objective type MO, Metric aMean, Target NA
Pollutant 475, Objective type MO, Metric aMean, Target NA
Pollutant 449, Objective type MO, Metric aMean, Target NA
Pollutant 21, Objective type MO, Metric aMean, Target NA
Pollutant 431, Objective type MO, Metric aMean, Target NA
Pollutant 464, Objective type MO, Metric aMean, Target NA
Pollutant 7, Objective type LTO, Metric AOT40c, Target V
Pollutant 482, Objective type MO, Metric aMean, Target NA
Pollutant 6011, Objective type MO, Metric aMean, Target NA
Pollutant 6012, Objective type MO, Metric aMean, Target NA
Pollutant 32, Objective type MO, Metric aMean, Target NA
Pollutant 25, Objective type MO, Metric aMean, Target NA
Pollutant 6001, Objective type LVMOT, Metric aMean, Target H
Pollutant 6001, Objective type TV, Metric aMean, Target H
Pollutant 6001, Objective type ERT, Metric AEI, Target H
Pollutant 8, Objective type LVmaxMOT, Metric aMean, Target H
applicable if time extension given (No time extension after 2015 inclusive).
Pollutant 8, Objective type LV, Metric hrsAbove, Target H
Pollutant 8, Objective type LVmaxMOT, Metric hrsAbove, Target H
Pollutant 8, Objective type MO, Metric aMean, Target NA
Pollutant 5, Objective type MO, Metric aMean, Target NA
Pollutant 1, Objective type ALT, Metric 3hAbove, Target H
Pollutant 8, Objective type ALT, Metric 3hAbove, Target H
Pollutant 7, Objective type INT, Metric hrsAbove, Target H
Pollutant 7, Objective type ALT, Metric hrsAbove, Target H
Pollutant 1045, Objective type MO, Metric NA, Target NA
Pollutant 1046, Objective type MO, Metric NA, Target NA
Pollutant 1047, Objective type MO, Metric NA, Target NA
Pollutant 450, Objective type MO, Metric NA, Target NA
Pollutant 6013, Objective type MO, Metric NA, Target NA
Non-reference measurement method(s) used for which equivalence testing is in progress (as set out in the Directives 2008/50/EC and 2004/107/EC)
Non-reference measurement method(s) used which equivalence has NOT been demonstrated as set out in the Directives 2008/50/EC and 2004/107/EC
Demonstration not possible, no reference method defined by Directive
There is no reference method defined by Directive 2008/50/EC or 2004/107/EC. Hence, demonstration is not possible.
Reference method used, demonstration not necessary.
Measurement method used is a reference methods as defined by Directive 2008/50/EC or 2004/107/EC.
Non-reference measurement method(s) used for which equivalence has been demonstrated as set out in the Directives 2008/50/EC and 2004/107/EC
Number of short term exceedances - for number of daily or hourly exceedances
The number of short term exceedances element allows for the description of the highest number of exceedances of short term reporting metrics observed or predicted in the zone for the pollutant and environmental objective specified. Irrespective of whether levels are above the environmental objective, insert the value of the number of exceedance in the units appropriate to the environmental objective and reporting metric.The number of exceedances element is applicable to environmental objectives based on the number of daily or hourly exceedances.
numericalExceedance - for average, percentile or AOT reporting metrics
AQD numerical exceedance allows for the description of the highest concentration value observed or predicted in the zone for the pollutant and environmental objective specified. Irrespective of whether levels are above the environmental objective, insert the numerical concentration value in units as appropriate to the environmental objective and reporting metric. The AQD numerical exceedance class is applicable to environmental objectives using average, percentileor AOT reporting metrics. For other short term reporting metrics use <aqd:numberExceedance>.The rounding rules stipulated by the Commissions guidance apply.
percentileExceedance - FOR reporting exceedance when using RANDOM only!
Transport of air pollution originating from sources outside the Member State
Favourable meteorological conditions for ozone formation
Emissions due to public works and construction in the vicinity
Local industry including power production
Accidental emission from industrial source
Accidental emission from non-industrial source
Use of studded tyres during winter months. The road dust that studded tyres creates through wear of road surfaces collects on roads and can be resuspended in ambient air during dry conditions leading to elevated concentrations of coarse particulate matter.
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for AT
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for FR
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for DE
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for GR
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for HU
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for IE
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for IT
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for LV
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for LT
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for LU
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for MT
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for BE
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for NL
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for PL
Reduction Target above 22 - Achieve 18 ugm-3
Reduction % calculated as a reduction of 9.8 ugm-3 (calculated as 27.8-18).
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for PT
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for RO
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for SK
Reduction % calculated as a reduction of 6.4 ugm-3 (calculated as 24.4-18).
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for SI
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for ES
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for SE
Information compiled to check exposure reduction for PM2.5 NERT in force in 2020 for NO
Added by consulting https://cdr.eionet.europa.eu/no/eu/colp0r8w/colquwo3a/envuydlpq
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for IS
Information provided by IS reporters after consultation
Information compiled to check exposure reduction for PM2.5 NERT in force in 2020 for BG
Reduction % calculated as a reduction of 18 ugm-3 (calculated as 36-18).
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for HR
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for CY
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for CZ
Information double checked with reported 2011: https://cdr.eionet.europa.eu/cz/eu/annualair/envuyaeyq/11CZ-Questionnaire2011v2.zip/manage_document
Reduction Target (percentage) updated to 32.3 following feedback from Alberto González Ortiz
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for DK
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for EE
Infomation compiled to check exposure reduction for PM2.5 NERT in force in 2020 for FI
Low emission fuels for small, medium and large scale stationary sources and in mobile sources
Shift to installations using low emission fuels
Emission control equipment for small and medium sized stationary combustion sources / replacement of combustion sources
Measures to reduce pollution through permit systems and economic instruments
- LCP permits and national plans going beyond BAT
Introduction/increase of environment charges
Introduction/increase of environmental funding
Other measures not specified in codelist
Introduction/increase of environment taxes
Low emission stationary combustion sources
Low emission fuels for stationary and mobile sources
New vehicles, including low emission vehicles
Public information/Education via leaflets
Public information/Education via other mechanisms
Television (Public information/Education)
Public information/Education via television
Retrofitting emission control equipment to vehicles
Low emission zones (Traffic planning and management)
Congestion pricing zones (Traffic planning and management)
Differentiation of parking fees (Traffic planning and management)
Land use planning to ensure sustainable transport facilities
Management of parking places (Traffic planning and management)
Effective improvement of public transport
Encouragement of shift of transport modes
Slow modes (e.g. expansion of bicycle and pedestrian infrastructure)
Effective reduction of speed limits and control
AQD - AQ Plans - Measure implementation status
Using gas chromatography: the model airTOXIC BTX PID measures the amount of Benzene Toluene Ethylbenzene and Xylenes in the air from sub-ppb levels up to 1.000 ppb.
Teledyne API 100 UV Fluorescent SO2 Analyser
Teledyne API 100A UV Fluorescent SO2 Analyser
Teledyne API 100E UV Fluorescent SO2 Analyser
Teledyne API 101 UV Fluorescent SO2 Analyser
Teledyne API 101A UV Fluorescent SO2/H2S Analyser
Teledyne API 200 chemiluminescent NOx analyser
Teledyne API 200A chemiluminescent NOx analyser
Teledyne API 200AU chemiluminescent NOx analyser
Teledyne API 200E chemiluminescent NOx analyser
Teledyne API 200EU chemiluminescent NOx analyser
Teledyne API 200EU chemiluminescent NOx analyser - blue light
Teledyne API 200UP chemiluminescent NOx analyser
Teledyne API 300 gas filter correlation CO analyser
Teledyne API 300A gas filter correlation CO analyser
Teledyne API 300E gas filter correlation CO analyser
Teledyne API 400 UV photometric O3 analyser
Teledyne API 400A UV photometric O3 analyser
Teledyne API 400E UV photometric O3 analyser
Teledyne API M100E UV Fluorescent SO2 Analyser
Teledyne API M200E chemiluminescent NOx analyser
Teledyne API M300E gas filter correlation CO analyser
Teledyne API M400E UV photometric O3 analyser
Teledyne API T100 UV Fluorescent SO2 Analyser
Teledyne API T100U UV Fluorescent SO2 Analyser
Teledyne API T200 chemiluminescent NOx analyser
Teledyne API T200U chemiluminescent NOx analyser
he Model T200U Trace-level NO/NO2/NOx analyzer has been developed specifically to address the challenges of low-level monitoring as required in the US NCore network. It uses the proven chemiluminescence principle and is designed to allow ultra-sensitive measurements with a lower detectable limit of 50 ppt while still meeting the requirements for use as a US EPA compliance analyzer.The Model T200U combines a gold plated reaction cell with an enhanced performance pump special low noise photomultiplier tube and unique signal conditioning to provide exceptional sensitivity. In addition a pre-reactor separates the NO-O3 reaction from background chemiluminescence to allow accurate auto-zero of the analyzer.All T Series instruments offer an advanced color display capacitive touch screen intuitive user interface flexible I/O and built-in data acquisition capability. All instrument set up control and access to stored data and diagnostic information is available through the front panel or via RS232 Ethernet or USB com ports either locally or by remote connection.The Model T200U comes with NumaView™ Software. NumaView™ Remote PC Software allows for a remote connection with virtual interface and data downloading capability to analyzers operating NumaView™ Software.e allows for a remote connection with virtual interface and data downloading capability to analyzers operating NumaView™ Software.
Teledyne API T300 gas filter correlation CO analyser
Teledyne API T400 UV photometric O3 analyser
The airmoVOC BTX is a gas chromatograph for the analysis and monitoring of trace amounts of benzene, toluene, ethylbenzene (m/p/o) xylene by FID detection.
The method applied by the APM-2 uses the light scattered by tiny particles (nephelometry) to determine the PM10 or PM2.5 concentration in the ambient air directly and continuously.
DIGITEL High Volume Samplers DHA-80 are fully automatic systems to sample dust and aerosol particles for later assessment and analysis (gravimetric and analytical determination). The sampler operation range in standard execution is 100 to 1’500 litres per minute (6 to 90 m³/h).
This instrument provides continuous and reliable measurement of Ozone in ambient air. Measurement is based on the UV photometric method as specified in ISO-13964
DIGITEL Low Volume Samplers DPA-14 are fully automatic systems to sample dust and aerosol particles for later assessment and analysis (gravimetric and analytical determination) in accordance with EN12341:2023
Dasibi 1003-AH Air Water Ozone Concentration PPM Measurement Analyzer Monitor
The EC9852 Sulfur Compounds Analyzer combines microprocessor control with fluorescence detection and an external converter to measure H2S and SO2 or TS TRS and SO2 or H2S SO2 and H2S + SO2 in the range of 0-2 ppm with a detection limit of 0.5 ppb for SO2.
Envea AC32e - NO/NO2/NOx Analyzer (replaces enviroAC32E)
MP101M particulate analyzer (replaces enviroMP101M)
Envea O342e - UV Photometric Ozone Analyzer (replaces enviroO342E)
Environnement S.A. Model 1003-RS under DASIBI license
Environnement SF8 for black smoke and acidity
SINTECH SPECTRAS BTX GC 855 series undetermined
Analysis of VOC/BTEX in ambient air at very low concentration levels (ppb/ppt) thanks to precontration using a trap
SYNTECH SPECTRAS GC 955 series undetermined
Gas chromatograph (GC) specifically built for the measurement of BTEX in ambient air. It can be utilised to simultaneously detect and measure up to 40 different components
SYNSPEC GC955 615/815 Ozone Precursor Analyzer
GRIMM CPC model 5412 Standard Condensation Particle Counter
Compact CPC for nanoparticle counting with optimized detection efficiency and response time with integrated sample flow pump. Different calibrations possible
GRIMM-CPC5420 Scanning Mobility Particle Counter and Sizer
GRIMM model EDM 107 for PM10 PM2.5 PM1 and TC
The GRIMM model 107 monitor is designed to measure particle size distribution and particulate mass based on a light scattering measurement of individual particles in the sampled air
GRIMM model EDM 180-C for PM10 and PM2.5
GRIMM model EDM 180-D for PM10 PM2.5 PM1 and TC
GRIMM model EDM 180-MC for PM10 PM2.5 PM1 TC and 31 size channels
GRIMM model EDM 280 for TSP PM10 PM4 PM2.5 PM1 PMcoarse
GRIMM model EDM 365 for PM10 PM2.5 PM1 and TC
Model 5420 SMPS+C Scanning Mobility Particle Counter and Sizer
IL-Punkkinen for NO2/NO hourly measurements
Device based on the modified automated Saltzman method by Finnish Meteorological Institute.
RA-915AM monitors are designed for continuous mercury measurements in ambient air indoor air and in natural gas. Ideal for permanent unattended installation at air monitoring stations RA-915AM monitor for ambient air allows ultra-sensitive measurements of background Hg concentrations and is compliant with the European standard EN 15852 for ambient air monitoring.The monitors feature fully-automated unattended operation without the need for the monthly technician maintenance and frequent recalibration. The use of the instrument allows cutting down operation costs as the analyzer requires no argon cylinders for operation and no consumables.The remote data transfer makes it possible to connect the monitor to data collection systems via RS232 Modbus and analogue output.
Mercury Analyzer is a portable multifunctional atomic absorption spectrometer with Zeeman background correction which eliminates the effect of interfering impurities. It is the only high sensitivity and selectivity instrument that does not require gold amalgam pre-concentration and subsequent regeneration steps. This enables the user to conduct real time air monitoring and detection of mercury vapor. Being combined with pyrolysis or cold vapour attachments for liquid and solid sample testing the instrument can determine mercury content in water soil food products natural and stack gases may be used for dental and toxicological applications etc.
The MRI Integrating nephelometer is used to measure the scattering coefficient of the air, caused by aerosol particulates.
The PNS DM consists of a low/medium volume sampler (LVS or MVS) and a filter changer with intake tube and sampling inlet. It collects fine particulate matter on sampling filters according to EN 12341:2014 (PM10 and PM2.5).
The PNS T-DM combines a low / medium volume sampler (LVS or MVS) and a filter changer in a stainless steel cabinet. It collects fine particulate matter on sampling filters according to EN 12341:2014 (PM10 and PM2.5).
Passive Palmes Tube. Generally for NO2. However available for other substances like NOX-NO SO2 O3 C6H6...
Picarro G2301 Gas Concentration Analyzer
The Picarro G2301 gas concentration analyzer provides simultaneous, precise measurement of carbon dioxide (CO2) - methane (CH4) at parts-per-billion (ppb) and water (H2O) vapor at parts-per-million (ppm) sensitivity with negligible drift for atmospheric science air quality and emissions quantification. It meets the World Meteorological Organization (WMO) and Integrated Carbon Observation System (ICOS) performance requirements for CO2 and CH4 atmospheric monitoring.
RUPPRECHT & PATASHNICK, SERIES 5400 CARBON MONITOR
The Series 5400 is an automatic speciation analyzer of suspended particulate matter. It measures the elemental and organic carbon contained in suspended particulate matter at averaging times as short as one hour.
The SIR Model S-5001 is a Non-Pulsed U.V. Fluorescence Sulfur Dioxide Analyzer. In the nalyzer optically filtered pure monochromatic U.V. light from a Zinc lamp is focused onto the SO2 reaction chamber.
The SIR Model S-5006 is a Non-Dispersive Infrared (NDIR) Analyzer for the measurement of Carbon Monoxide concentrations in ambient air
The SIR Model S-5012 Nitrogen Oxides Analyzer is designed to measure the amount of nitric oxide (NO) nitrogen dioxide (NO2) and total oxides of nitrogen (NOx) in a continuous ambient air sample
SIR Model S-5014 ozone analyser is a self-contained instrument which measures the concentration of ozone in a sample of ambient background) gas such as air oxygen nitrogen etc
TEOM 1405DF with FDMS Dichotomous monitor for PM2.5 & PM10
The 450iQ analyzer operates on the principle that H2S can be converted to SO2. As the SO2 molecules absorb ultraviolet (UV) light and become excited at one wavelength, the molecules then decay to a lower energy state emitting UV light at a different wavelength.
The Model 3022A Condensation Particle Counter detects particles down to 7 nm in diameter. Using both single-count and photometric detection modes it provides highly accurate measurements for concentrations as high as 107particles/cm3.
The Ultrafine Particle Monitor Model 3031 is specifically designed to measure ultrafine particles long-term. It reports the particle number concentration in six size classes between 20 and 500 nm and requires only minimal maintenance.
TSI's Electrostatic Classifiers 3080 Series produce highly monodisperse, submicrometer aerosol. They have been used in a variety of aerosol-generation or particle-sizing applications with highly accurate and repeatable results.
TSI Nanoparticle Surface Area Monitor 3550
The Nanoparticle Surface Area Monitor 3550 (NSAM) measures the human lung-deposited surface area of particles (reported as µm 2 /cm 3 ) corresponding to tracheobronchial (TB) and alveolar (A) regions of the lung. The NSAM 3550 provides a simple and fast solution for measuring the surface area equivalent dose in the lung. It is an important instrument for research in the fields of inhalation toxicology health effects and epidemiology and for measuring and monitoring workplace exposure.
Enables ambient air monitoring stations to measure size distributions of ultrafine particles in compliance with CEN/TS 17434:2020.
TSI model 3752 High Concentration Condensation Particle Counter
TSI Condensation Particle Counters (CPCs)
Condensation Particle Counter Model 3772 is a compact rugged and full-featured instrument that detects airborne particles down to 10 nm at an aerosol flow rate of 1.0 L/min over a concentration range from 0 to 10000 particles/cm 3. It is ideally suited for applications that do not require measurement of high concentrations.
TSI model 3775 Condensation Particle Counter
TSI model 3775 Condensation Particle Counter (Discontinued)
TSI Ultrafine Condensation Particle Counter (UCPC) Model 3776
The Ultrafine Condensation Particle Counter 3776 (UCPC) a types of condensation particle counter (CPC) is designed primarily for researchers interested in airborne particles smaller than 20 nm. It is a continuous-flow instrument that detects particles down to 2.5 nm. It uses a special sheath-air flow design that improves response to changes in particle concentration and increases counting efficiency for ultrafine particles.
TSI’s EPC™Monitor Model 3783 provides continuous, high precision airborne particle number concentration measurements
General Scanning Mobility Particle Sizer
The Thermo Scientific Model 17i Ammonia Analyzer uses the light producing reaction of nitric oxide (NO) with ozone (O3) as its basic principle. The instrument has three modes of operation NO NOx and Nt.
With ultraviolet photometry technology. High stability and low detection limit (0.5 ppm)
The aeris® AE2010U Trace Level Ozone (03) Analyser employs a non-dispersive ultraviolet (UV) absorption
The aeris® AE2030U Trace Level Carbon monoxide (CO) analyser employs a n on-dispersive infrared (NDIR) photometer to measure very low concentrations of CO
The aeris® AE2041U Trace Level NO/NO2/NOx chemiluminescence analyser incorporates a single-channel design measuring NO and NOx
The aeris® AE2050U Trace Level Sulphur Dioxide (S02) Analyser employs pulsed UV fluorescent radiation technology
The Aerosol Chemical Speciation Monitor (ACSM) measures mass loading and chemical composition of non-refractory aerosol particles in real-time. Smaller lower cost more robust and simpler to operate than our AMS instruments the ACSM is designed for long-term unattended deployment and routine monitoring applications.
Agilent HP 6890 (used for benzene and toluene measurement)
System for analysis of the Ozone precursor VOC
The airmoVOC BTX is an automatic gas chromatograph dedicated to the analysis and monitoring of trace amounts of BTEX compounds(Benzene Toluene Ethylbenzene m- p- and o-Xylenes)
The airpointer‘s modular design comprising a base unit analyzing modules and sensor modules allows for a configurationaccording to different application requirements.
Andersen/GMW Model FH621-N Beta Monitor
Andersen Instruments Model FH62I-N PM10 Beta Attenuation Monitor consisting of the following components: FH101 Vacuum Pump Assembly - FH102 Accessory Kit - FH107 Roof Flange Kit - FH125 Zero and Span PM 10 Mass Foil Calibration Kit - FH62I Beta Attenuation 19-inch Control Module - SA246b PM10Inlet (16.7 liter/min) or the louvered inlet specified in 40 CFR 50 Appendix L Figs. L-2 thru L-19 operated for 24-hour average measurements with an observing time of 60 minutes the calibration factor set to 2400 a glass fiber filter tape an automatic filter advance after each 24-hour sample period and with or without either of the following options: FH0P1 Indoor Cabinet FH0P2 Outdoor Shelter Assembly
Thermo Andersen Series FH 62 C14 Continuous PM10 Ambient Particulate Monitor
Thermo Andersen Series FH 62 C14 Continuous PM10 Ambient Particulate Monitor and Thermo Scientific Model 5014i Beta (5014i Beta) Continuous Ambient Particulate Monitor ” operated for 24-hour average measurements with the specified 10-micron EPA PM10inlet (or alternative louvered PM10inlet meeting 40 CFR 50 Appendix L specifications) inlet connector sample tube with heater roof flange kit mass foil kit pump kit sample filter tape with operational settings of 1000 L/h (16.67 L/min) sample flowrate daily filter change auto filter change at volumetric flow <950 L/h auto filter change at mass >1500 micrograms and factory default calculation mode settings operated with software version 1.07. Operated calibrated and serviced according to the appropriate Operator Manual
Andersen Instruments Model FH62I-N PM10 Beta Attenuation Monitor consisting of the following components: FH101 Vacuum Pump Assembly - FH102 Accessory Kit - FH107 Roof Flange Kit - FH125 Zero and Span PM 10 Mass Foil Calibration Kit - FH62I Beta Attenuation 19-inch Control Module - SA246b PM10Inlet (16.7 liter/min) or the louvered inlet specified in 40 CFR 50 Appendix L Figs. L-2 thru L-19 - operated for 24-hour average measurements with an observing time of 60 minutes the calibration factor set to 2400 a glass fiber filter tape an automatic filter advance after each 24-hour sample period and with or without either of the following options: FH0P1 Indoor Cabinet - FH0P2 Outdoor Shelter Assembly
Andersen/GMW generic High-Volume Air Sampler
3 WAVELENGTH INTEGRATING NEPHELOMETERAerosol particles in the atmosphere directly influence the earth‚Äôs radiative balance by absorbing and scattering the solar radiation and indirectly by changing the clouds microphysical properties."
Bendix/Combustion Engineering Model 8101-C Oxides of Nitrogen Analyze
Bendix or Combustion Engineering Model 8101-C Oxides of Nitrogen Analyzer operated on a 0-0.5 ppm range with a Teflon sample filter (Bendix P/N 007163) installed on the sample inlet line.
Columbia Scientific Industries Models 1600
CSI Model 1600 Oxides of Nitrogen Analyzer operated on a 0-0.5 ppm range with a Teflon sample filter (CSI P/N M951-8023)installed on the sample inlet line
Columbia Scientific Industries Models 5600
CSI Model 5600 Oxides of Nitrogen Analyzer operated on a 0-0.5 ppm range with any signal integration time in the range of 20 to 99 seconds with a Teflon sample filter (CSI P/N M951-8023) installed on the sample inlet line
Environnement S.A. Model AC21M NO2 Analyzer
Environnement S.A. Model AC30M NO2 Analyzer
Environnement S.A. Model AC31M NO2 Analyzer
Environnement S. A. Model AC31M Chemiluminescent Nitrogen Oxide Analyzer operated with a full scale range of 0 -500ppb at any temperature in the range of 15°C to 35°C with a 5-micron PTFE sample particulate filter with the following software settings: Environnement S. A. Model AC31M Chemiluminescent Nitrogen Oxide Analyzer operated with a full scale range of 0 -500ppb at any temperature in the range of 15°C to 35°C with a 5-micron PTFE sample particulate filter with the following software settings: Automatic response time ON Minimum response time set to 60 seconds (RT 2) and with or without any of the following options: Internal Permeation Oven- Connection for Silica Gel Dryer- RS232-422 interface- EV3 valve- Internal Printer
Environnement S.A. Model AC32M NO2 Analyzer
Environnement S. A. Model AC32M Chemiluminescent Nitrogen Oxides Analyzer operated with a full scale range of 0 -500 ppb at any temperature in the range of 10°C to 35°C with a 5-micron PTFE sample particulate filter with response time setting 11 (automatic response time) and with or without the following option:Internal permeation oven.
UV Fluorescence gas monitor offering excellent performances for the monitoring of SO2 in the range 0-10 ppm or 0-1 ppmEco-designed reference air quality monitor QAL1 certified by the TÜV US-EPA approved. Utilizes the standard method for the measurement of sulfur dioxides(EN 14212). With its ultra low power consumption & 24 V supply (option) the AF22e is the sole SO2 monitor on the market able to measure without being connected to the power grid.https://www.envea.global/s/emissions-en/gas-monitors-emissions-en/af22e-dilution/
Total Gaseous Mercury (TGM) Ultratracer. Measuring of Total Gaseous Mercury (TGM) in air and other gases
Environnement S.A. Model AC32E NO2 Analyzer (superseded by EnveaAC32e)
Environnement S.A. Model AF20M SO2 Analyzer
Environnement S.A. Model AF21M SO2 Analyzer
Environnement S.A Model AF21M Sulfur Dioxide Analyzer operated on a range of 0-0.5 ppm with a response time coefficient setting of 01 a Teflon ilter installed in the rear - panel filter assembly and with or without any of the following options: Rack Mount/Slides RS-232-C Interface
Environnement S.A. Model AF22E SO2 Analyzer
Environnement S.A. Model AF22M SO2 Analyzer
Environnement S.A Model AF22M UV Fluorescence Sulfur Dioxide Analyzer operated with a full scale range of 0 - 500 ppb at any temperature in the range of 10°C to 35°C with a 5-micron PTFE sample particulate filter with a response time setting of 11 (Automatic response time) with the automatic “ZERO-REF” cycle ON and set for activation every 24 hours and with or without either of the follow ing options: Permeation oven Rack mount slides
Environnement S.A. Model AS32M Nitrogen Dioxide Analyzer
Environnement S.A. Model CO10M CO Analyzer
Environnement S.A. Model CO11M CO Analyzer
Environnement S.A. Model CO11M Ambient Carbon Monoxide Analyzer operated on a full scale range of 0 - 50 ppm at any temperature in the range of 15 °C to 35°C with a 5-micron PTFE sample particulate filter with the following software settings:Automatic nvironnement S.A. Model CO11M Ambient Carbon Monoxide Analyzer operated on a full scale range of 0 - 50 ppm at any temperature in the range of 15 °C to 35°C with a 5-micron PTFE sample particulate filter with the following software settings:Automatic response time ON - Minimum response time set to 40 seconds (RT 13). Automatic ZERO-REF cycle programmed every 24 hours and with or without any of the following options: RS232-422 Serial Interface - Internal Printer
Environnement S.A. Model CO12E CO Analyzer
Environnement S.A. Model CO12M CO Analyzer
Environnement S.A Model CO12M Gas Filter Correlation Carbon Monoxide Analyzer operated with a full scale range of 0 - 50 ppm at any temperature in the range of 10°C to 35°C with a 5-micron PTFE sample particulate filter with response time ON and with the automatic “ZERO-REF” cycle either ON or OFF
Using a proven flame ionisation detector (FID) the analyzer HC51M measures ambient air hydrocarbons (THC CH4 nmHC) in the range 0-1000 ppm.
Environnement S.A. Model MP101M (may be used for PM10 and PM2.5) (superseded by EnveaMP101M)
Environnement S. A. Model MP101M with PM10 or PM2.5 Beta Gauge Monitor ” configured with the louvered PM 10 or PM2.5 inlet specified in 40 CFR 50 Appendix L or its flat-topped predecessor version and one of the three optional temperature-regulated sampling tubes (RST) and operated with a full scale measurement range of 0 - 0.500 mg/m3 (0 - 500 g/m3) with the sample flow rate set to 1.00 m3/h and flow regulation set to yes the “norms selection” set to m3(actual volume) the “cycle” set to 24 hours the “period” set to none and the “counting time” set to 200 seconds
Environnement S.A. Model MP2.5M undefined
Environnement S.A. Model O341M UV Ozone Analyzer
Environnement S.A. Model O341M UV Photometric Ozone Analyzer operated on a full scale range of 0 - 500 ppb at any temperature in the range of 15°C to 35°C with the response time set to 50 seconds and with or without any of the following options: Internal Ozone Generator - Span External Control - RS232 - 422 Serial Interface - Internal Printer.
Environnement S.A. Model O342E UV Ozone Analyzer (superseded by EnveaO342e)
Environnement S.A. Model O342M UV Ozone Analyze
Environnement S.A Model O342M UV Photometric Ozone Analyzer ” operated with a full scale range of 0 - 500 ppb at any temperature in the range of 10°C to 35°C with a 5-micron PTFE sample particulate filter with response time setting of 11 (Automatic response time) and with or without any of the following options: c) Internal ozone generator d) Span external control (zero/span solenoid valve).
Environnement S.A. SANOA Multigas Longpath Monitoring System
Environnement S.A. Model SANOA Multigas Longpath Air Quality Monitoring System consisting of a receiver one or more projectors interface unit a user-provided control unit computer running the SANOA VisionAIR software and associated incidental equipment configured for measuring SO2 with the temperature control and internal calibration cell options installed operated with a measurement range of 0 to 0.5 ppm over an installed monitoring path length of between 27 and 500 meters within an ambient air temperature range of -30 to +45°C with a measurement (integrating) time of 180 seconds and with or without external temperature and barometric pressure sensors or any of the following options: external (meteo) input connection series 1M bus connection OGR type projector analog outputs.
Horiba model APHA 360E hydrocarbons analyser
Horiba model APHA 360 hydrocarbons analyser
Horiba model APHA 370 hydrocarbons analyser
MCV CAV-A/MSb Captador d'Alt Volum Seqüencial
Meloy Model SA 700 Fluorescence Sulfur Dioxide Analyze
Meloy Model SA 700 Fluorescence Sulfur Dioxide Analyzeroperated on the 0-250 ppb1 the 0-500 ppb or the 0-1000 ppb range with a time constant switch position of either 2 or 3.The analyzer may be operated at temperatures between 20°C and 30°C and at line voltages between 105 and 130 volts with or without any of the following options: FS-1 Current Output - FS-2 Rack Mount Conversion - FS-2A Rack Mount Conversion - FS-2B Rack Mount Conversion - FS-3 Front Panel Mounted Digital Meter - FS-5 Auto/Manual Zero/Span With Status - FS-6Remote/Manual Zero/Span With Status - FS-7 Auto Zero Adjust. voltages between 105 and 130 volts with or without any of the following options: FS-1 Current Output
Multi-gas Micro Monitoring station (MMS) Portable version
Opsis AR500 Open path monitor with ER 110
Opsis AR500 Open path monitor with ER 120
Opsis AR500 Open path monitor with ER 150
Opsis SM200 Particulate Analyser with PM2.5 & PM10 Heads
Osiris air monitoring device measures airborne particles (TSP PM10 PM2.5 and PM1). MCERTS certified for PM10
PHILIPS K50109/00 Gas Filter Correlation CO analyser
PHILIPS K50110/00 UV Photometric O3 analyser
PHILIPS K50206/00 Pulsed Fluorescence SO2 analyser
Picarro G2103 (used for NH3 measurement)
Ecotech serinus 40 used for NOx-NO2-NO modified to measure NOH3 (including a converter)
The Serinus 51 H2S/SO2 instruments can integrate seamlessly into continuous monitoring networks and can sequentially measure H2S and then SO2
EC/OC measurements Sunset Laboratory Inc Thermal / Optical Carbon Analyser (near-real time)
EC/OC measurements Sunset Laboratory Inc Thermal / Optical Carbon Analyser - operated near real time
Tekran mercury analyser 2537A. Elemental mercury is sampled by placing the 1130 before the main 2537A instrument. The respective constituents are sampled from the air using either the 1130 add-on for reactive gaseous mercury or the 1135 add-on for particulate bound mercury.
Thermo model 14B chemiluminescence NO-NO2-Nox
Thermo model 14B/E chemiluminescence NO-NO2-Nox
Gas Filter Correlation CO2 Analyzer 115V-AC
Thermo model 42i NO/NOx analyser - blue light
Thermo model 43h pulsed fluorescence SO2 analyser
Thermo model 43i-TLE (Enhanced Trace Level)
Thermo model 48 CO analyser (gas filter correlation)
Thermo model 48i-TLE (Enhanced Trace Level)
This is a reference photomer not an analyser
The Model 5012 MAAP measures the aerosol-related absorption of light and the corresponding atmospheric black carbon mass concentration. Continuous data is provided by a multiple detector setup to simultaneously measure the transmitted and the scattered light from a particle-loaded filter. Typical applications include determining ambient elemental carbon for health-related effects and aerosol light absorption for visibility monitoring (regional haze) and climate research.
Thermo 5014i Beta Continuous Ambient Particulate Monitor
Measure PM-10 PM-2.5 or PM-1 mass concentrations with the Thermo Scientific™ 5014i Beta Continuous Ambient Particulate Monitor. The 5014i distinguishes itself from other beta measurement methods by utilizing a continuous (non-step wise) mass measurement with a proven industry standard which provides for long-term unattended operation. To accurately address potential water bias and volatile loss the Dynamic Heating System allows the user to hold the sample temperature at a fixed value or below a relative humidity threshold.
Thermo model 5030 SHARP Particular Monitor with PM10 & PM2.5 heads
The Thermo Scientific™ 5030 SHARP continuously measures the mass concentration of particulate utilizing a combination of beta attenuation and light scattering technology.The only continuous (non-step wise) hybrid ambient monitor that provides high resolution measurement of airborne particulates with excellent short and long term precision.
Aerosol Mass Spectrometer/Aerosol Chemical Mass Spectrometer
The instrument's primary operating mechanism is the radiometric microbalance system, which relies on changes in the strength of a beta ray beam passing through the filter paper to determine changes in particulate mass collected. A Beta Attenuation Monitor is comprised of three main components: the PM air inlet, the central instrument, and the vacuum pump.
Measurement of Particulate Matter (PM10, PM2.5 & PM1)
Capacitive sensors function by using the principle of an ideal plate capacitor. One plate is the sensor itself. The other is the measurement object, which lies across from it. An electrical field is generated between the two plates. A protection ring around the device structure ensures that the electrical field is as homogenous as possible. If an object enters the field, the distance between the two plates changes. This can be measured
Cavity ring down spectroscopy for measuring CO2, CH4 & CO
Differential Optical Absorption Spectroscopy (DOAS)
In atmospheric chemistry, differential optical absorption spectroscopy (DOAS) is used to measure concentrations of trace gases. When combined with basic optical spectrometers such as prisms or diffraction gratings and automated, ground-based observation platforms, what we have is a cheap and powerful means for the measurement of such trace gas species as ozone and nitrogen dioxide.
Flame Atomic Emission Spectroscopy (FAES)
Flame atomic emission spectroscopy (FAES) is a classical method which has been largely displaced by plasma spectroscopies. Plasmas produce higher atomization ratios, but the theory is similar in both flame and the plasmas. FAES is the classical method used as plasmas have taken over as the preferred method due to the higher atomization ratios that occur.
Gas chromatography followed by flame ionization detection (GC-FID)
Gas chromatography followed by mass spectrometry (GC-MS)
Gas chromatography–mass spectrometry (GC-MS) is a method that combines the features of gas-liquid chromatography and mass spectrometry to identify different substances within a test sample.
Multi-angle Absorption Photometry (MAAP)
The measurement is performed at three detection angles to resolve the influence of light-scattering aerosol components on the angular distribution of the back scattered radiation. The fraction of light absorbed by the deposited aerosol (absorbance ABS) is obtained from a radiative transfer scheme.
Non-dispersive infrared spectroscopy (NDIR)
A nondispersive infrared sensor (or NDIR) sensor is a simple spectroscopic device often used as gas detector. The main components are an infrared source (lamp), a sample chamber or light tube, a wavelength sample chamber, and gas concentration is measured electro-optically by its absorption of a specific wavelength in the infrared (IR). The IR light is directed through the sample chamber towards the detector. In parallel there is another chamber with an enclosed reference gas, typically nitrogen. The detector has an optical filter in front of it that eliminates all light except the wavelength that the selected gas molecules can absorb.
The reference method for the measurement of carbon monoxide is that described in EN 14626:2005 ‘Ambient air quality — Standard method for the measurement of the concentration of carbon monoxide by non-dispersive infrared spectroscopy’
Optical particle counter + conversion to mass concentration
Optical particle counter + conversion to mass concentration for Particular Matter Example: http://dd.eionet.europa.eu/vocabulary/aq/measurementequipment/GRIMM-EDM180
A PID uses an ultraviolet (UV) light source to break down VOCs in the air into positive and negative ions. The PID then detects or measures the charge of the ionized gas, with the charge being a function of the concentration of VOCs in the air.
Tapered Element Oscillating Microbalance (TEOM)
A continuous direct mass measurement of particulate matter utilizing a tapered element oscillating microbalance (TEOM).
Tapered Element Oscillating Microbalance (TEOM) with Filter Dynamics Measurement System (FDMS)
A continuous direct mass measurement particulate matter utilizing a tapered element oscillating microbalance (TEOM) and Filter Dynamics Measurement System (FDMS).
Tapered Element Oscillating Microbalance (TEOM) + correction with estimated volatile fraction
A continuous direct mass measurement particulate matter utilizing a tapered element oscillating microbalance (TEOM) and correction with estimated volatile fraction (A correction to take into account the missing volatile fraction. This fraction is estimated from another station where a TEOM 1400 and a TEOM FDMS are used in parallel.)
The reference method for the measurement of sulphur dioxide is that described in EN 14212:2005 ‘Ambient air quality — Standard method for the measurement of the concentration of sulphur dioxide by ultraviolet fluorescence’.
The reference method for the measurement of ozone is that described in EN 14625:2005 ‘Ambient air quality — Standard method for the measurement of the concentration of ozone by ultraviolet photometry’.
Chemiluminescence (sometimes "chemoluminescence") is the emission of light (luminescence), as the result of a chemical reaction. One known gas phase reaction is the basis of nitric oxide detection in commercial analytic instruments applied to environmental air-quality testing. Ozone is combined with nitric oxide to form nitrogen dioxide in an activated state. The activated NO2 luminesces broadband visible to infrared light as it reverts to a lower energy state. A photomultiplier and associated electronics counts the photons that are proportional to the amount of NO present. To determine the amount of nitrogen dioxide, NO2, in a sample (containing no NO) it must first be converted to nitric oxide, NO, by passing the sample through a converter before the above ozone activation reaction is applied. The ozone reaction produces a photon count proportional to NO that is proportional to NO2 before it was converted to NO. In the case of a mixed sample that contains both NO and NO2, the above reaction yields the amount of NO and NO2 combined in the air sample, assuming that the sample is passed through the converter.
The reference method for the measurement of nitrogen dioxide and oxides of nitrogen is that described in EN 14211:2005 ‘Ambient air quality — Standard method for the measurement of the concentration of nitrogen dioxide and nitrogen monoxide by chemiluminescence’.
See description for Nephelometry See description for BETA Example: http://dd.eionet.europa.eu/vocabulary/aq/measurementequipment/thermo5030SHARP
Saltzman - colorimetric microdetermination of NO2
Saltzman method for the determination of NO2 in the atmosphere by colorimetric reaction.
Measure outside of Air quality or Short term Action Plan
Measure geared at the protection of sensitive groups
AQD - Model or objective estimation input parameters
Description of the scheme used to characterise the horizontal transport of the atmosphere
Chemistry or chemical schemes applicable
A description of the chemical schemes or algorithms describing chemistry used in the model.
Description of the scheme used to describe the vertical transport of the atmosphere
Description of the deposition schemes used to describe dry and wet deposition
Descriptive text to enable the identification tracing of the emissions inventory used as input to the model, including version / year publication & projection information as applicable.
Descriptive text on the type of meteorology used to parameterise the model.
Parameter used in D1b to declare that modelapplication is to be provided in E1b. In E1b, further description of encoding is to be provided via http://dd.eionet.europa.eu/vocabulary/aq/modelapplication/
A list of the sampling point used to inform an objective estimation assessment technique
Description of empirical scaling factors applied as part of the model e.g. scaling factors to derive short-term exceedance statistics from long-term means.
Description scheme for the terrain height and/or surface roughness
Turbulence profiles based on surface similarity and boundary layer scaling used to describe atmospheric turbulence
Parameter used in D1b to declare that the model type is to be provided in E1b. In E1b, specific description of the type is to be provided via http://dd.eionet.europa.eu/vocabulary/aq/modeltype
Xlink to the projection of the results provided in E1b. (example: http://spatialreference.org/ref/epsg/4326/)
Atmospheric numerical model. Eulerian models define specific reference points in a gridded system that monitors atmospheric properties, including temperature, pressure, chemical concentration of tracers, over time. Being the representative of the Eulerian model, the Unified Model divides the world up into fixed grid cells which allows for modelling the interactive chemistry within the atmosphere, regarded as a three - dimensional single fluid, and applying well - developed convection parameterisation scheme to represent convective motions.
Atmospheric numerical model. Lagrangian models take the perspective of a finite element or so - called ‘air parcel’. Over time both the position and properties of this air parcel are calculated according to the mean wind field data. The path along which air parcel travels is called its trajectory. It can be expressed as a differential equation. Advanced equation for the trajectory contains two components: mean winds and random turbulence.
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Network designed for the observation of single emission sources
Networks comprising monitoring sites in more than one country; networks targeted at special ecosystem monitoring.
Network designed at the spatial level of an administrative unit of some 1000s to some 10.000s km²
Network designed at the spatial level of an agglomeration or conurbation.
‘Alert threshold’ shall mean a level beyond which there is a risk to human health from brief exposure for the population as a whole and at which immediate steps are to be taken by the Member States
'Critical Level’ shall mean a level fixed on the basis of scientific knowledge, above which direct adverse effects may occur on some receptors, such as trees, other plants or natural ecosystems but not on humans.
‘Exposure Concentration Obligation’ shall mean a level fixed on the basis of the average exposure indicator with the aim of reducing harmful effects on human health, to be attained over a given period.
‘Information threshold’ shall mean a level beyond which there is a risk to human health from brief exposure for particularly sensitive sections of the population and for which immediate and appropriate information is necessary.
‘Long-Term Objective’ shall mean a level to be attained in the long term, save where not achievable through proportionate measures, with the aim of providing effective protection of human health and the environment.
‘Limit Value’ shall mean a level fixed on the basis of scientific knowledge, with the aim of avoiding, preventing or reducing harmful effects on human health and/or the environment as a whole, to be attained within a given period and not to be exceeded once attained.
Limit value plus applicable margin of tolerance (LVMOT)
Limit value plus maximum margin of tolerance
LVmaxMOT to be used if a time extension is in place. MS need to declare compliance with the LV + max MOT.
'Target value’ shall mean a level fixed with the aim of avoiding, preventing or reducing harmful effects on human health and/or the environment as a whole, to be attained where possible over a given period.
Limit Value (Stage II) for reporting PM2.5 only
Objective type for the reporting of the PM2.5 Stage 2 Limit Value (20 ugm-3) — indicative limit value to be reviewed by the Commission in 2013 in the light of further information on health and environmental effects, technical feasibility and experience of the target value in Member States.
For primary data, data is considered to be invalid due to other circumstances or data is simply missing. For aggregated data, data is not valid because of insufficient data capture following rules set out in Directive and Guidance.
Not valid due to station maintenance or calibration
Data is considered to be invalid due to the regular calibration or the normal maintenance of the instrumentation (only used for primary data).
Primary data considered valid by the data provider for its related reporting purposes. Aggregated data is valid following rules set out in Directive and Guidance.
Valid, but below detection limit measurement value given
Data considered valid by the data provider for its related reporting purposes. However, the value has been measured below the detection limit and the value reported is the detection limit (only used for primary data).
Valid, but below detection limit and number replaced by 0.5*detection limit
Data considered valid by the data provider for its related reporting purposes. However, the value has been measured below the detection limit and the value reported is half of this detection limit (only used for primary data).
Valid ozone (pollutant code 7) data using new cross section CCQM.O3.2019 (Any ozone previously reported using validation flag 1 is assumed Hearn.1961) Invalid data regardless of cross section to be reported as validation flag -1
Data has gone through full quality assurance and quality control by data provider/owner. Data is considered verified and can be formally used for its reporting purposes.
Final data having gone through full qa/qc.
Data has gone through initial checks by data provider/owner. Extra quality assurance and quality control verifications have been carried out compared to "Not verified" data. Data Verification might be carried out on an ongoing basis and is nominally a process to "clean-up" the initial "Not verified" data. Any corrections to the data made during the verification process are changes the status flag to "Preliminary verified". The data with this data flag is considered provisional and can be used as provisional. This flag is independant to the validity status.
Mainly used when Up To Date data is reported. Data subject to changes as further qa/qc is carried out.
Data has not gone through (or has gone through minimal) checks by data provider/owner. Some basic screening criteria in order to exclude clearly faulty data as far as possible maybe used. The data with this data flag is considered provisional and can be used as provisional. This flag is independant to the validity status.
SO2
As in PM2.5
SO42- in PM2.5 - recommended unit: µg/m3
Chrysene in PM2.5 - recommended unit: ng/m3
Dibenzo(ah)anthracene in PM2.5 (aerosol)
Dibenzo(ah)anthracene in PM2.5 - recommended unit: ng/m3
Anthracene in PM2.5 (aerosol) - recommended unit: ng/m3
Benzo(a)anthracene in PM2.5 - recommended unit: ng/m3
Benzo(b)fluoranthene in PM2.5 - recommended unit: ng/m3
Benzo(b)fluoranthene in PM2.5 (air+aerosol)
Benzo(ghi)perylene in PM2.5 - recommended unit: ng/m3
Benzo(k)fluoranthene in PM2.5 - recommended unit: ng/m3
Fluoranthene in PM2.5 (aerosol) - recommended unit: ng/m3
Indeno-(1,2,3-cd)pyrene in PM2.5 - recommended unit: ng/m3
Indeno-(1,2,3-cd)pyrene in PM2.5
Phenanthrene in PM2.5 (aerosol) - recommended unit: ng/m3
Pyrene in PM2.5 (aerosol) - recommended unit: ng/m3
Benzo(j)fluoranthene in PM2.5 - recommended unit: ng/m3
C6H6
Total nitrogen in precipitation - recommended unit: mg N/l
Benzo(b,j,k)fluoranthene - recommended unit: ng/l
1-methylnaphtalene - recommended unit: ng/m3
1-methylphenanthrene - recommended unit: ng/m3
Methyletylketone (MEK) - recommended unit: µg/m3
Crotonaldehyde - recommended unit: µg/m3
2-methylanthracene - recommended unit: ng/m3
2-methylbenzaldehyde - recommended unit: µg/m3
2-methylnaphtalene - recommended unit: ng/m3
(CH3)2-CH-CH2-CH2-CH3 - recommended unit: µg/m3
2-methylphenanthrene - recommended unit: ng/m3
Methylvinylketone (MVK) - recommended unit: µg/m3
3-methylbenzaldehyde - recommended unit: µg/m3
3-methylpentane - recommended unit: pptv
4-methylbenzaldehyde - recommended unit: µg/m3
Benzo(a)fluoranthene - recommended unit: ng/m3
Benzo(b+j+k)fluoranthenes - recommended unit: ng/m3
Benzo(e)pyrene - recommended unit: ng/m3
Benzo(k+j)fluoranthene (air+aerosol) - recommended unit: ng/m3
H3C-CH2-CH2-CH3 - recommended unit: µg/m3
Methacroleine + Butanal - recommended unit: µg/m3
Carbon-tetrachloride - recommended unit: pptv
Cyklopenta(cd)pyrene - recommended unit: ng/m3
Dibenzo(ac+ah)anthracenes - recommended unit: ng/m3
Dibenzo(ac+ah)anthracenes
Dibenzo(ah)anthracene - recommended unit: ng/l
Dibenzothiophene - recommended unit: ng/m3
Chrysene + Triphenylene - recommended unit: ng/m3
(CH3)3-C-CH2-CH-(CH3)2 - recommended unit: µg/m3
H3C-CH2-CH(CH3)2 - recommended unit: µg/m3
CH2=CH-C(CH3)=CH2 - recommended unit: µg/m3
Nonane
n-Nonano
Tetrachloromethane (air) - recommended unit: µg/m3
Chlorobenzene (air) - recommended unit: µg/m3
1,1,2-trichloroethane (air) - recommended unit: µg/m3
1,1-dichloroethane (air) - recommended unit: µg/m3
1,2-dichloroethylene (air) - recommended unit: µg/m3
1,2-dichloroethane (air) - recommended unit: µg/m3
1,1,1-trichloroethane (air) - recommended unit: µg/m3
Methyl-chloroform - recommended unit: pptv
m,p-C6H4(CH3)2 - recommended unit: µg/m3
SO4 (H2SO4 aerosols) (SO4--) - recommended unit: µg/m3
Hg0 + Hg-reactive - recommended unit: ng/m3
H3C-(CH2)3-CH3 - recommended unit: µg/m3
Syn-DP
PM10
2-methylpropanal isobutanal isobutylaldehyde
Pb in PM10
Cd in PM10
Ni in PM10
As in PM10
BaP in PM10
CH2=CH-CH3 + H3C-CH2-CH2-CH3 - recommended unit: µg/m3
Sn in PM10
H3C-(CH2)3-CH3 + H3C-CH2-CH(CH3)2 - recommended unit: µg/m3
Pentane + Isopentane
Acetone + Acrolein- recommended unit: µg/m3
Acetone + Acrolein (air)
HC C2-C6(excl. AROM. & CHLH) (air+aerosol)
HC C2-C6(excl. AROM. & CHLH) - recommended unit: µg/m3
HC > C6 (excl. AROM. & CHLH) (air+aerosol)
HC > C6 (excl. AROM. & CHLH) - recommended unit: µg/m3
Aromatics (except C6H6) - recommended unit: µg/m3
1-Methyl anthracene in PM10 (air+aerosol)
1-Methyl anthracene in PM10 - recommended unit: ng/m3
Anthanthrene in PM10 - recommended unit: ng/m3
Benzo(b,j,k)fluoranthene in PM10 (aerosol)
Benzo(b,j,k)fluorantheneInPM1 - recommended unit: ng/m3
Benzo(e)pyrene in PM10 - recommended unit: ng/m3
Benzo(k+j)fluoranthene in PM10 (aerosol)
Benzo(k+j)fluoranthene in PM10 (aerosol) - recommended unit: ng/m3
Chlorinated hydrocarbons - recommended unit: µg/m3
Chrysene in PM10 - recommended unit: ng/m3
Coronene in PM10 - recommended unit: ng/m3
Cyclopenta(c,d)pyrene in PM10 - recommended unit: ng/m3
Dibenzo(ac+ah)anthracene in PM10 (aerosol)
Dibenzo(ac+ah)anthracene in PM10 - recommended unit: ng/m3
Dibenzo(ah)anthracene in PM10 - recommended unit: ng/m3
Benzo(b,j)fluoranthene in PM10 (aerosol)
Benzo(b,j)fluorantheneInPM10 - recommended unit: ng/m3
Perylene in PM10 - recommended unit: ng/m3
4.5-Methylene phenanthrene in PM10 (air+aerosol)
4.5-Methylene phenanthrene in PM10 - recommended unit: ng/m3
5-Methyl Chrysene in PM10 - recommended unit: ng/m3
9-Methyl anthracene in PM10 (air+aerosol)
9-Methyl anthracene in PM10 - recommended unit: ng/m3
Benzo(b)naphtho(2,1-d)thiophene in PM10 (aerosol)
Benzo(b)naphtho(2,1-d)thiophene in PM10 - recommended unit: ng/m3
Benzo(c)phenanthrene in PM10 - recommended unit: ng/m3
Cholanthrene in PM10 - recommended unit: ng/m3
Dibenzo(ac)anthracene in PM10 - recommended unit: ng/m3
Dibenzo(al)pyrene in PM10 - recommended unit: ng/m3
Benzo(b+j)fluoranthene in PM10 (air+aerosol)
Benzo(b+j)fluoranthene in PM10 - recommended unit: ng/m3
Anthracene in PM10 (aerosol) - recommended unit: ng/m3
Benzo(a)anthracene in PM10 (air+aerosol)
Benzo(a)anthracene in PM10 - recommended unit: ng/m3
Benzo(b)fluoranthene in PM10 (air+aerosol)
Benzo(b)fluoranthene in PM10 - recommended unit: ng/m3
Benzo(ghi)perylene in PM10 - recommended unit: ng/m3
Benzo(b)naphtho(2,1-d)thiophene in PM10 (air+aerosol)
Benzo(k)fluoranthene in PM10 (air+aerosol)
Benzo(k)fluoranthene in PM10 - recommended unit: ng/m3
Dibenzo(ac)anthracene in PM10 (air+aerosol)
Dibenzo(ah+ac)anthracene in PM10 (aerosol)
Dibenzo(ah+ac)anthracene in PM10 - recommended unit: ng/m3
Dibenzo(ae)pyrene in PM10 - recommended unit: ng/m3
Dibenzo(ah)pyrene in PM10 - recommended unit: ng/m3
Dibenzo(ai)pyrene in PM10 - recommended unit: ng/m3
indeno_123cd_pyrene in PM10 (air+aerosol)
Indeno-(1,2,3-cd)pyrene in PM - recommended unit: ng/m3
Phenanthrene in PM10 (aerosol) - recommended unit: ng/m3
Pyrene in PM10 (aerosol) - recommended unit: ng/m3
Benzo(c)phenanthrene in PM10 (air+aerosol)
Dibenzo(ah+ac)anthracene in PM10 (air+aerosol)
Benzo(j)fluoranthene in PM10 - recommended unit: ng/m3
Benzo(j)fluoranthene in PM10 (air+aerosol)
Dibenzo(ah)anthracene in PM10 (air+aerosol)
PM2.5
Ultra Fine Particles (UFPs) - recommended unit: particles.cm-3
Ultra Fine Particles (UFPs) means particles with a diameter less than or equal to 100 nanometers (10^-9 m), where UFP are measured as the particle number concentrations per cubic centimetre for a size range with a lower limit of 10 nm and for a size range with no restriction on the upper limit
PNSD - Particle Number Size Distribution
particle number size distribution (PNSD) is the frequency distribution of the particle number concentration represented as a function of the logarithm of particle size, such that the area under the distribution between two sizes is the number concentration of that size range.
H2C=CH-CH2-CH3 - recommended unit: µg/m3
trans-H3C-CH=CH-CH3 - recommended unit: µg/m3
cis-H3C-CH=CH-CH3 - recommended unit: µg/m3
H2C=CH-CH2-CH2-CH3 - recommended unit: µg/m3
H3C-HC=CH-CH2-CH3 - recommended unit: µg/m3
H3C-HC=CH-CH2-CH3
3-methylphenantrene - recommended unit: ng/m3
1,2,4-C6H3(CH3)3 - recommended unit: µg/m3
1,2,3-C6H3(CH3)3 - recommended unit: µg/m3
1,3,5-C6H3(CH3)3 - recommended unit: µg/m3
Butyl acetate (air) - C6H12O2 - recommended unit: µg/m3
9-methylphenantrene - recommended unit: ng/m3
Ultra Fine Particles (UFPs) with a lower limit of 3 nanometers and no restriction on the upper limit - recommended unit: particles.cm-3
Ultra Fine Particles (UFPs) means particles with a diameter less than or equal to 100 nanometers (10^-9 m), where UFP are measured as the particle number concentrations per cubic centimetre for a size range with a lower limit of 3 nm and for a size range with no restriction on the upper limit - PLEASE USE /6003 FOR REPORTING UFP ACCORDING TO RECAST EU 2024/2881
Ultra Fine Particles (UFPs) with a lower limit of 4 nanometers and no restriction on the upper limit - recommended unit: particles.cm-3
Ultra Fine Particles (UFPs) means particles with a diameter less than or equal to 100 nanometers (10^-9 m), where UFP are measured as the particle number concentrations per cubic centimetre for a size range with a lower limit of 4 nm and for a size range with no restriction on the upper limit - PLEASE USE /6003 FOR REPORTING UFP ACCORDING TO RECAST EU 2024/2881
Ultra Fine Particles (UFPs) with a lower limit of 7 nanometers and no restriction on the upper limit - recommended unit: particles.cm-3
Ultra Fine Particles (UFPs) means particles with a diameter less than or equal to 100 nanometers (10^-9 m), where UFP are measured as the particle number concentrations per cubic centimetre for a size range with a lower limit of 7 nm and for a size range with no restriction on the upper limit - PLEASE USE /6003 FOR REPORTING UFP ACCORDING TO RECAST EU 2024/2881
Anthracene - recommended unit: µg/m2/day
Benzo(a)anthracene - recommended unit: ng/m3
Benzo(a)anthracene - recommended unit: ng/l
Benzo(a)anthracene - recommended unit: µg/m2/day
Benzo(a)fluorene - recommended unit: ng/m3
Benzo(b)fluoranthene - recommended unit: ng/m3
Benzo(b)fluoranthene - recommended unit: ng/l
Benzo(b)fluoranthene - recommended unit: µg/m2/day
Benzo(b)fluorene - recommended unit: ng/m3
Fluor (except HF) - recommended unit: µg/m3
Benzo(ghi)fluoranthene - recommended unit: ng/m3
Benzo(ghi)fluoranthene - recommended unit: ng/l
Benzo(ghi)perylene - recommended unit: ng/m3
Benzo(ghi)perylene - recommended unit: ng/l
Benzo(ghi)perylene - recommended unit: µg/m2/day
Benzo(k)fluoranthene - recommended unit: ng/m3
Benzo(k)fluoranthene - recommended unit: ng/l
Benzo(k)fluoranthene - recommended unit: µg/m2/day
Dibenz(ac+ah)anthracenes - recommended unit: ng/m3
Dibenz(ac+ah)anthracenes (precip) - PLEASE use .../418
Dibenz(ac+ah)anthracenes - recommended unit: ng/l
Dibenz(ac+ah)anthracenes
Dibenz(ah)anthracene (precip) - please use .../419
Dibenz(ah)anthracene - recommended unit: ng/l
Dibenz(ah)anthracene
Dibenzo(ae)pyrene - recommended unit: ng/m3
Dibenzo(ah)pyrene - recommended unit: ng/m3
Dibenzo(ai)pyrene - recommended unit: ng/m3
Benzo(b,j,k)fluoranthene in PM10 (air+aerosol)
Benzo(k+j)fluoranthene in PM10 (air+aerosol)
Benzo(k+j)fluoranthene in PM10 - recommended unit: ng/m3
Dibenzo(ai)pyrene - recommended unit: ng/l
The volatile fraction of PM10 - recommended units ug/m3
The non-volatile fraction of a PM10 measurement - recommended units ug/m3
The volatile fraction of a PM2.5 measurememt - recommended units ug/m3
The non-volatile fraction of a PM2.5 measurement - recommended units ug/m3
The volitile fraction of a PM1 measurement - recommended units ug/m3
The non-volatile fraction of a PM1 measurement - recommended units ug/m3
Fluoranthene - recommended unit: µg/m2/day
Heptachlor Epoxide - recommended unit: ng/l
Indeno-(1,2,3-cd)pyrene - recommended unit: ng/m3
Indeno-(1,2,3-cd)pyrene - recommended unit: ng/l
Indeno-(1,2,3-cd)pyrene - recommended unit: µg/m2/day
NH4+
NO3-
Kj-N in precipitation - recommended unit: mg N/l
Radioactivity
Phenanthrene - recommended unit: µg/m2/day
SO4--
1-Methyl anthracene - recommended unit: µg/m2/day
1-Methyl Naphthalene - recommended unit: µg/m2/day
alpha-HCH - recommended unit: ng.m-2.day-1
alpha-HCH
1-Methyl phenanthrene - recommended unit: µg/m2/day
2-Methyl anthracene - recommended unit: µg/m2/day
2-Methyl Naphthalene - recommended unit: µg/m2/day
2-Methyl phenanthrene - recommended unit: µg/m2/day
Acenaphthene - recommended unit: µg/m2/day
Acenaphthylene - recommended unit: µg/m2/day
Anthanthrene - recommended unit: µg/m2/day
gamma-HCH - recommended unit: ng.m-2.day-1
gamma-HCH
Benzo(b,j,k)fluoranthene (precip+dry_dep)
Benzo(b,j,k)fluoranthene - recommended unit: µg/m2/day
Benzo(e)pyrene - recommended unit: µg/m2/day
Benzo(k+j)fluoranthene - recommended unit: µg/m2/day
Chrysene + Triphenylene - recommended unit: µg/m2/day
Cyclopenta(c,d)pyrene - recommended unit: µg/m2/day
Dibenzo(ac+ah)anthracenes (precip+dry_dep)
Dibenzo(ac+ah)anthracenes - recommended unit: µg/m2/day
Dibenzo(ah)anthracene - recommended unit: µg/m2/day
Naphthalene - recommended unit: µg/m2/day
Benzo(b,j)fluoranthene - recommended unit: µg/m2/day
4.5-Methylene phenanthrene (precip+dry_dep)
4.5-Methylene phenanthrene - recommended unit: µg/m2/day
5-Methyl Chrysene - recommended unit: µg/m2/day
9-Methyl anthracene - recommended unit: µg/m2/day
Benzo(b)naphtho(2,1-d)thiophene (precip+dry_dep)
Benzo(b)naphtho(2,1-d)thiophene - recommended unit: µg/m2/day
Benzo(c)phenanthrene - recommended unit: µg/m2/day
Cholanthrene - recommended unit: µg/m2/day
Dibenzo(ac)anthracene - recommended unit: µg/m2/day
Dibenzo(al)pyrene - recommended unit: µg/m2/day
precip_amount_off - recommended unit: mm
Benzo(j)fluoranthene - recommended unit: ng/l
Benzo(j)fluoranthene - recommended unit: µg/m2/day
Benzo(j)fluorene - recommended unit: ng/m3
Benzo(j)fluoranthene - recommended unit: ng/m3
Dibenzo(ah)anthracene - recommended unit: ng/m3
Dibenzo(ae)pyrene - recommended unit: µg/m2/day
Dibenzo(ah)pyrene - recommended unit: µg/m2/day
Dibenzo(ai)pyrene - recommended unit: µg/m2/day
Dieldrin - recommended unit: ng.m-2.day-1
alpha-Endosulfan - recommended unit: pg.m-3
beta-Endosulfan - recommended unit: pg.m-3
Endosulfan sulfate - recommended unit: pg.m-3
p,p'-DDD - recommended unit: ng.m-2.day-1
p,p'-DDE - recommended unit: ng.m-2.day-1
p,p'-DDT - recommended unit: ng.m-2.day-1
trans-CD - recommended unit: ng.m-2.day-1
trans-NO - recommended unit: ng.m-2.day-1
alpha-Endosulfan - recommended unit: ng.m-2.day-1
beta-Endosulfan - recommended unit: ng.m-2.day-1
Endosulfan sulfate - recommended unit: ng.m-2.day-1
Atrazine - recommended unit: ng.m-2.day-1
Isoproturon - recommended unit: ng.m-2.day-1
Heptachlor - recommended unit: ng.m-2.day-1
NO2
trans-H3C-HC=CH-CH2-CH3 - recommended unit: µg/m3
cis-H3C-HC=CH-CH2-CH3 - recommended unit: µg/m3
NOX
The daily average or daily mean derived from a sample period of one day.
The data capture associated with a primary observation. This primary observation parameter is the percentage of the time envelope defined by its start and end time for which a sample or observation has been made or taken. It is essential for sampler based measurements where (i) random measurements operate over the time envelope defined, (ii) where samples are frequently not taken for the complete sampling envelope and (ii) for samples bulked for analysis. In these cases time weight concentrations estimates are calculated using the value domain of the "dc" field. For automatic measurements the value will frequently not be stored in local systems as hourly means derived from <75% dc are discarded. At best the dc rate will be known to >=75% (as a valid hourly mean for example). For automatic measurements return -99 or -999 for the value domain of the "dc" field.
The average or mean derived from a sample over the period of 2-weeks. The duration will be defined by the startTime & endTime components of the data array.
The hourly average or hour mean is the average of all valid minute values for an hour. An hourly average is calculated if at least 45 valid minutes values are available.
The monthly average or mean derived from a sample period of one month.
The n-hourly average or n-hour mean is the average of all valid minute values for n-hour. An n-hourly average is calculated if at least 75% are available. Note: n must be equal to 2, 3, 4, 6 in order to be able to correctly aggregate the data.
The average or mean derived from a sample(s) taken over a 3-month period. The duration will be defined by the startTime & endTime components of the data array.
The average or mean derived from a sample of variable temporal duration. The duration will be defined by the startTime & endTime components of the data array.
The weekly average or mean derived from a sample period of one week.
The yearly average or mean derived from a sample period of one year - PRIMARY DATA
Range for pollutant 5 for hour in ug.m-3
Range for pollutant 38 for hour in ug.m-3
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Range for pollutant 63 for day in ng.m-3
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Range for pollutant 67 for day in ugN.m-3
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Range for pollutant 5 for week in ug.m-3
Range for pollutant 68 for week in ugN.m-3
Range for pollutant 73 for day in ng.m-3
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Range for pollutant 83 for hour in ug.m-3
Range for pollutant 316 for day in ug.m-3
Range for pollutant 316 for hour in ug.m-3
Range for pollutant 316 for month in ug.m-3
Range for pollutant 316 for year in ug.m-3
Range for pollutant 323 for month in pptv
Range for pollutant 351 for day in ng.m-3
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Range for pollutant 352 for day in ng.m-3
Range for pollutant 380 for var in ng.m-3
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Range for pollutant 391 for day in ug.m-3
Range for pollutant 394 for day in ug.m-3
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Range for pollutant 6 for hour in ug.m-3
Range for pollutant 394 for month in ug.m-3
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Range for pollutant 412 for day in uS.cm-1
Range for pollutant 416 for hour in pptv
Range for pollutant 419 for var in ng.l-1
Range for pollutant 425 for hour in ppbv
Range for pollutant 428 for day in ug.m-3
Range for pollutant 428 for hour in ug.m-3
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Range for pollutant 430 for day in ug.m-3
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Range for pollutant 432 for day in ug.m-3
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Range for pollutant 7 for hour in ug.m-3
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Range for pollutant 435 for day in ng.m-3
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Range for pollutant 447 for day in ug.m-3
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Range for pollutant 8 for hour in ug.m-3
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Range for pollutant 451 for day in ug.m-3
Range for pollutant 8 for month in ug.m-3
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Range for pollutant 464 for day in ug.m-3
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Range for pollutant 1 for hour in ug.m-3
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Range for pollutant 475 for day in ug.m-3
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Range for pollutant 482 for day in ug.m-3
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Range for pollutant 8 for week in ug.m-3
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Range for pollutant 486 for day in ug.m-3
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Range for pollutant 503 for day in ug.m-3
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Range for pollutant 520 for day in ugS.m-3
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Range for pollutant 604 for day in ng.m-3
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Range for pollutant 611 for day in ug.m-2.day-1
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Range for pollutant 9 for hour in ug.m-3
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Range for pollutant 616 for month in ng.m-3
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Range for pollutant 618 for day in ug.m-2.day-1
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Range for pollutant 622 for day in ng.m-3
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Range for pollutant 10 for day in mg.m-3
Range for pollutant 624 for month in ug.m-2.day-1
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Range for pollutant 627 for day in ug.m-2.day-1
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Range for pollutant 630 for day in mg.l-1
Range for pollutant 10 for hour in mg.m-3
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Range for pollutant 632 for day in mg.l-1
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Range for pollutant 643 for day in ng.m-3
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Range for pollutant 645 for month in ug.m-2.day-1
Range for pollutant 648 for day in ueH.l-1
Range for pollutant 653 for day in ng.m-3
Range for pollutant 11 for day in ug.m-3
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Range for pollutant 656 for day in ug.m-2.day-1
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Range for pollutant 658 for day in mg.l-1
Range for pollutant 11 for hour in ug.m-3
Range for pollutant 659 for day in ug.m-3
Range for pollutant 660 for day in mg.l-1
Range for pollutant 664 for day in mgH.l-1
Range for pollutant 666 for day in mgH.l-1
Range for pollutant 668 for day in ug.m-3
Range for pollutant 669 for day in mg.l-1
Range for pollutant 673 for var in pg.m-3
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Range for pollutant 12 for day in ug.m-3
Range for pollutant 683 for var in pg.m-3
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Range for pollutant 701 for var in pg.m-3
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Range for pollutant 1 for month in ug.m-3
Range for pollutant 12 for hour in ug.m-3
Range for pollutant 707 for var in pg.m-3
Range for pollutant 709 for var in pg.m-3
Range for pollutant 712 for day in ng.m-3
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Range for pollutant 714 for month in ug.m-2.day-1
Range for pollutant 715 for day in ng.m-3
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Range for pollutant 715 for year in ng.m-3
Range for pollutant 12 for month in ug.m-3
Range for pollutant 717 for month in ug.m-2.day-1
Range for pollutant 719 for day in mgS.m-1
Range for pollutant 728 for var in ug.l-1
Range for pollutant 728 for week in ug.l-1
Range for pollutant 759 for var in ng.l-1
Range for pollutant 760 for day in ug.m-2.day-1
Range for pollutant 760 for month in ug.m-2.day-1
Range for pollutant 12 for var in ug.m-3
Range for pollutant 760 for var in ug.m-2.day-1
Range for pollutant 762 for day in ng.m-3
Range for pollutant 762 for year in ng.m-3
Range for pollutant 763 for month in ng.m-3
Range for pollutant 1012 for day in ug.m-3
Range for pollutant 1014 for day in ng.m-3
Range for pollutant 1015 for day in ng.m-3
Range for pollutant 1018 for day in ug.m-3
Range for pollutant 1029 for day in ng.m-3
Range for pollutant 1045 for day in ug.m-3
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Range for pollutant 1045 for hour in ug.m-3
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Range for pollutant 1046 for day in ug.m-3
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Range for pollutant 12 for year in ug.m-3
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Range for pollutant 1063 for day in ng.m-3
Range for pollutant 1629 for day in ug.m-3
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Range for pollutant 13 for day in ng.m-3
Range for pollutant 1631 for day in ug.m-3
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Range for pollutant 1657 for day in ug.m-3
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Range for pollutant 13 for hour in ng.m-3
Range for pollutant 1659 for day in ug.m-3
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Range for pollutant 1668 for day in ug.m-3
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Range for pollutant 13 for month in ng.m-3
Range for pollutant 1771 for day in ug.m-3
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Range for pollutant 1772 for day in ug.m-3
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Range for pollutant 2012 for var in ug.l-1
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Range for pollutant 13 for var in ng.m-3
Range for pollutant 2013 for week in ng.l-1
Range for pollutant 2014 for month in ug.l-1
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Range for pollutant 2015 for month in ug.l-1
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Range for pollutant 13 for year in ng.m-3
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Range for pollutant 2063 for var in ug.l-1
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Range for pollutant 14 for day in ng.m-3
Range for pollutant 3012 for day in ug.m-3
Range for pollutant 3014 for day in ng.m-3
Range for pollutant 3015 for day in ng.m-3
Range for pollutant 3018 for day in ng.m-3
Range for pollutant 4013 for day in ng.m-3
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Range for pollutant 4330 for var in pg.m-3
Range for pollutant 14 for month in ng.m-3
Range for pollutant 4336 for var in pg.m-3
Range for pollutant 4339 for var in pg.m-3
Range for pollutant 4341 for var in pg.m-3
Range for pollutant 4406 for day in ng.m-3
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Range for pollutant 4406 for year in ng.m-3
Range for pollutant 4813 for day in ng.m-3
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Range for pollutant 14 for var in ng.m-3
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Range for pollutant 5012 for day in ug.m-3
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Range for pollutant 5014 for day in ng.m-3
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Range for pollutant 5029 for day in ng.m-3
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Range for pollutant 5029 for var in ng.m-3
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Range for pollutant 5045 for day in ug.m-3
Range for pollutant 15 for day in ng.m-3
Range for pollutant 5046 for day in ug.m-3
Range for pollutant 5047 for day in ug.m-3
Range for pollutant 5129 for day in ng.m-3
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Range for pollutant 5380 for day in ng.m-3
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Range for pollutant 5419 for day in ng.m-3
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Range for pollutant 5419 for var in ng.m-3
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Range for pollutant 5609 for day in ng.m-3
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Range for pollutant 5610 for day in ng.m-3
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Range for pollutant 5616 for day in ng.m-3
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Range for pollutant 5617 for day in ng.m-3
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Range for pollutant 5625 for day in ng.m-3
Range for pollutant 15 for week in ng.m-3
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Range for pollutant 5626 for day in ng.m-3
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Range for pollutant 5631 for day in ug.m-3
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Range for pollutant 5654 for day in ng.m-3
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Range for pollutant 1 for week in ug.m-3
Range for pollutant 16 for day in ng.m-3
Range for pollutant 5659 for day in ug.m-3
Range for pollutant 5668 for day in ug.m-3
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Range for pollutant 5762 for day in ng.m-3
Range for pollutant 5762 for month in ng.m-3
Range for pollutant 5762 for var in ng.m-3
Range for pollutant 17 for day in ng.m-3
Range for pollutant 5763 for day in ng.m-3
Range for pollutant 5763 for var in ng.m-3
Range for pollutant 5771 for day in ug.m-3
Range for pollutant 5772 for day in ug.m-3
Range for pollutant 6001 for day in ug.m-3
Range for pollutant 6001 for hour in ug.m-3
Range for pollutant 6001 for var in ug.m-3
Range for pollutant 6002 for day in ug.m-3
Range for pollutant 6002 for hour in ug.m-3
Range for pollutant 6005 for day in ug.m-3
Range for pollutant 18 for day in ng.m-3
Range for pollutant 6005 for hour in ug.m-3
Range for pollutant 6005 for month in ug.m-3
Range for pollutant 6006 for day in ug.m-3
Range for pollutant 6006 for hour in ug.m-3
Range for pollutant 6007 for day in ug.m-3
Range for pollutant 6007 for hour in ug.m-3
Range for pollutant 6008 for day in ug.m-3
Range for pollutant 6008 for hour in ug.m-3
Range for pollutant 6008 for var in ug.m-3
Range for pollutant 6008 for week in ug.m-3
Range for pollutant 18 for month in ng.m-3
Range for pollutant 6009 for day in ug.m-3
Range for pollutant 6009 for hour in ug.m-3
Range for pollutant 6009 for var in ug.m-3
Range for pollutant 6009 for week in ug.m-3
Range for pollutant 6011 for day in ug.m-3
Range for pollutant 6011 for hour in ug.m-3
Range for pollutant 6011 for var in ug.m-3
Range for pollutant 6011 for week in ug.m-3
Range for pollutant 6012 for day in ug.m-3
Range for pollutant 6012 for hour in ug.m-3
Range for pollutant 18 for var in ng.m-3
Range for pollutant 6012 for var in ug.m-3
Range for pollutant 6012 for week in ug.m-3
Range for pollutant 6013 for day in ug.m-3
Range for pollutant 6013 for hour in ug.m-3
Range for pollutant 6013 for var in ug.m-3
Range for pollutant 6013 for week in ug.m-3
Range for pollutant 6015 for day in ng.m-3
Range for pollutant 6015 for month in ng.m-3
Range for pollutant 6015 for var in ng.m-3
Range for pollutant 6015 for year in ng.m-3
Range for pollutant 18 for week in ng.m-3
Range for pollutant 6380 for day in ng.m-3
Range for pollutant 7012 for month in ug.m-2.day-1
Range for pollutant 7012 for week in ug.m-2.day-1
Range for pollutant 7012 for year in ug.m-2.day-1
Range for pollutant 7013 for month in ug.m-2.day-1
Range for pollutant 7013 for var in ug.m-2.day-1
Range for pollutant 7013 for year in ug.m-2.day-1
Range for pollutant 7014 for day in ug.m-2.day-1
Range for pollutant 7014 for month in ug.m-2.day-1
Range for pollutant 7014 for var in ug.m-2.day-1
Range for pollutant 18 for year in ng.m-3
Range for pollutant 7014 for week in ug.m-2.day-1
Range for pollutant 7014 for year in ug.m-2.day-1
Range for pollutant 7015 for day in ug.m-2.day-1
Range for pollutant 7015 for month in ug.m-2.day-1
Range for pollutant 7015 for var in ug.m-2.day-1
Range for pollutant 7015 for week in ug.m-2.day-1
Range for pollutant 7015 for year in ug.m-2.day-1
Range for pollutant 7018 for day in ug.m-2.day-1
Range for pollutant 7018 for month in ug.m-2.day-1
Range for pollutant 7018 for var in ug.m-2.day-1
Range for pollutant 19 for hour in ug.m-3
Range for pollutant 7018 for week in ug.m-2.day-1
Range for pollutant 7018 for year in ug.m-2.day-1
Range for pollutant 7029 for day in ug.m-2.day-1
Range for pollutant 7029 for month in ug.m-2.day-1
Range for pollutant 7029 for var in ug.m-2.day-1
Range for pollutant 7029 for week in ug.m-2.day-1
Range for pollutant 7029 for year in ug.m-2.day-1
Range for pollutant 7380 for month in ug.m-2.day-1
Range for pollutant 7380 for var in ug.m-2.day-1
Range for pollutant 7380 for week in ug.m-2.day-1
Range for pollutant 20 for day in ug.m-3
Range for pollutant 7407 for month in ug.m-2.day-1
Range for pollutant 7419 for day in ug.m-2.day-1
Range for pollutant 7419 for month in ug.m-2.day-1
Range for pollutant 7419 for var in ug.m-2.day-1
Range for pollutant 7419 for week in ug.m-2.day-1
Range for pollutant 1 for day in ug.m-3 for Austria
Range for pollutant 20 for hour in ug.m-3
Range for pollutant 3 for day in ugSO2.m-3
Range for pollutant 20 for month in ug.m-3
Range for pollutant 20 for var in ug.m-3
Range for pollutant 20 for week in ug.m-3
Range for pollutant 20 for year in ug.m-3
Range for pollutant 21 for day in ug.m-3
Range for pollutant 21 for hour in ug.m-3
Range for pollutant 21 for month in ug.m-3
Range for pollutant 21 for var in ug.m-3
Range for pollutant 21 for week in ug.m-3
Range for pollutant 21 for year in ug.m-3
Range for pollutant 22 for day in ug.m-3
Range for pollutant 22 for hour in ug.m-3
Range for pollutant 22 for week in ug.m-3
Range for pollutant 24 for day in ug.m-3
Range for pollutant 24 for hour in ug.m-3
Range for pollutant 25 for day in ug.m-3
Range for pollutant 25 for var in ug.m-3
Range for pollutant 25 for week in ug.m-3
Range for pollutant 26 for day in ug.m-3
Range for pollutant 26 for week in ug.m-3
Range for pollutant 4 for hour in ug.m-3
Range for pollutant 27 for day in ug.m-3
Range for pollutant 27 for week in ug.m-3
Range for pollutant 29 for day in ng.l-1
Range for pollutant 29 for hour in ng.l-1
Range for pollutant 29 for var in ng.l-1
Range for pollutant 29 for year in ng.l-1
Range for pollutant 30 for day in ng.m-3
Range for pollutant 32 for day in ugC.m-3
Range for pollutant 32 for hour in ugC.m-3
Range for pollutant 33 for day in ug.m-3
Range for pollutant 33 for hour in ug.m-3
Range for pollutant 34 for hour in ug.m-3
Range for pollutant 35 for day in ug.m-3
Range for pollutant 35 for hour in ug.m-3
Range for pollutant 35 for var in ug.m-3
Range for pollutant 35 for week in ug.m-3
Range for pollutant 36 for var in mgN.m-2.m-1
Range for pollutant 37 for day in mgS.m-2.m-1
Range for pollutant 37 for var in mgS.m-2.m-1
Range for pollutant 38 for day in ug.m-3
AQD - primary Observation Range - Country specific (temporary)
Range for pollutant 1 for day in ug.m-3 specific to MK
Range for pollutant 1 for hour in ug.m-3 specific to MK
Range for pollutant 5 for hour in ug.m-3 specific to MK
Range for pollutant 20 for hour in ug.m-3 specific to MT
Range for pollutant 21 for hour in ug.m-3 specific to MT
Range for pollutant 431 for hour in ug.m-3 specific to MT
Range for pollutant 482 for hour in ug.m-3 specific to MT
Range for pollutant 1 for day in ug.m-3 specific to NL
Range for pollutant 1 for hour in ug.m-3 specific to NL
Range for pollutant 5 for day in ug.m-3 specific to NL
Range for pollutant 5 for hour in ug.m-3 specific to NL
Range for pollutant 6 for day in ug.m-3 specific to NL
Range for pollutant 7 for day in ug.m-3 specific to NL
Range for pollutant 7 for hour in ug.m-3 specific to NL
Range for pollutant 8 for day in ug.m-3 specific to NL
Range for pollutant 8 for hour in ug.m-3 specific to NL
Range for pollutant 9 for day in ug.m-3 specific to NL
Range for pollutant 9 for hour in ug.m-3 specific to NL
Range for pollutant 10 for day in mg.m-3 specific to NL
Range for pollutant 10 for hour in mg.m-3 specific to NL
Range for pollutant 12 for day in ug.m-3 specific to NL
Range for pollutant 14 for day in ng.m-3 specific to NL
Range for pollutant 15 for day in ng.m-3 specific to NL
Range for pollutant 18 for day in ng.m-3 specific to NL
Range for pollutant 20 for day in ug.m-3 specific to NL
Range for pollutant 20 for hour in ug.m-3 specific to NL
Range for pollutant 20 for week in ug.m-3 specific to NL
Range for pollutant 21 for day in ug.m-3 specific to NL
Range for pollutant 21 for hour in ug.m-3 specific to NL
Range for pollutant 21 for week in ug.m-3 specific to NL
Range for pollutant 22 for day in ug.m-3 specific to NL
Range for pollutant 22 for week in ug.m-3 specific to NL
Range for pollutant 26 for day in ug.m-3 specific to NL
Range for pollutant 26 for week in ug.m-3 specific to NL
Range for pollutant 27 for day in ug.m-3 specific to NL
Range for pollutant 27 for week in ug.m-3 specific to NL
Range for pollutant 35 for day in ug.m-3 specific to NL
Range for pollutant 35 for hour in ug.m-3 specific to NL
Range for pollutant 36 for 4week in mgN.m-2.m-1 specific to NL
Range for pollutant 37 for 4week in mgS.m-2.m-1 specific to NL
Range for pollutant 38 for day in ug.m-3 specific to NL
Range for pollutant 38 for hour in ug.m-3 specific to NL
Range for pollutant 41 for hour in ug.m-3 specific to NL
Range for pollutant 45 for day in ug.m-3 specific to NL
Range for pollutant 46 for day in ug.m-3 specific to NL
Range for pollutant 47 for day in ug.m-3 specific to NL
Range for pollutant 63 for day in ng.m-3 specific to NL
Range for pollutant 394 for hour in ug.m-3 specific to NL
Range for pollutant 412 for day in uS.cm-1 specific to NL
Range for pollutant 416 for hour in pptv specific to NL
Range for pollutant 428 for hour in ug.m-3 specific to NL
Range for pollutant 430 for hour in ug.m-3 specific to NL
Range for pollutant 431 for day in ug.m-3 specific to NL
Range for pollutant 431 for hour in ug.m-3 specific to NL
Range for pollutant 431 for week in ug.m-3 specific to NL
Range for pollutant 432 for hour in ug.m-3 specific to NL
Range for pollutant 441 for day in ug.m-3 specific to NL
Range for pollutant 441 for hour in ug.m-3 specific to NL
Range for pollutant 441 for week in ug.m-3 specific to NL
Range for pollutant 443 for day in ug.m-3 specific to NL
Range for pollutant 443 for hour in ug.m-3 specific to NL
Range for pollutant 443 for week in ug.m-3 specific to NL
Range for pollutant 464 for day in ug.m-3 specific to NL
Range for pollutant 464 for hour in ug.m-3 specific to NL
Range for pollutant 464 for week in ug.m-3 specific to NL
Range for pollutant 475 for day in ug.m-3 specific to NL
Range for pollutant 475 for hour in ug.m-3 specific to NL
Range for pollutant 475 for week in ug.m-3 specific to NL
Range for pollutant 482 for day in ug.m-3 specific to NL
Range for pollutant 482 for hour in ug.m-3 specific to NL
Range for pollutant 482 for week in ug.m-3 specific to NL
Range for pollutant 486 for hour in ug.m-3 specific to NL
Range for pollutant 503 for hour in ug.m-3 specific to NL
Range for pollutant 505 for hour in ug.m-3 specific to NL
Range for pollutant 629 for day in ug.m-3 specific to NL
Range for pollutant 630 for day in mg.l-1 specific to NL
Range for pollutant 631 for day in ug.m-3 specific to NL
Range for pollutant 632 for day in mg.l-1 specific to NL
Range for pollutant 648 for day in ueH.l-1 specific to NL
Range for pollutant 658 for day in mg.l-1 specific to NL
Range for pollutant 660 for day in mg.l-1 specific to NL
Range for pollutant 664 for day in mgH.l-1 specific to NL
Range for pollutant 666 for day in mgH.l-1 specific to NL
Range for pollutant 669 for day in mg.l-1 specific to NL
Range for pollutant 719 for day in mgS.m-1 specific to NL
Range for pollutant 2012 for 4week in ug.l-1 specific to NL
Range for pollutant 2012 for var in ug.l-1 specific to NL
Range for pollutant 2013 for week in ng.l-1 specific to NL
Range for pollutant 2014 for 4week in ug.l-1 specific to NL
Range for pollutant 2063 for 4week in ug.l-1 specific to NL
Range for pollutant 2063 for week in ug.l-1 specific to NL
Range for pollutant 2065 for 4week in ug.l-1 specific to NL
Range for pollutant 2065 for var in ug.l-1 specific to NL
Range for pollutant 2073 for 4week in ug.l-1 specific to NL
Range for pollutant 2073 for var in ug.l-1 specific to NL
Range for pollutant 2073 for week in ug.l-1 specific to NL
Range for pollutant 6005 for hour in ug.m-3 specific to NL
Range for pollutant 6006 for hour in ug.m-3 specific to NL
Range for pollutant 6007 for hour in ug.m-3 specific to NL
Range for pollutant 6011 for day in ug.m-3 specific to NL
Range for pollutant 6011 for week in ug.m-3 specific to NL
Range for pollutant 6012 for day in ug.m-3 specific to NL
Range for pollutant 6012 for week in ug.m-3 specific to NL
Range for pollutant 6013 for day in ug.m-3 specific to NL
Range for pollutant 6013 for week in ug.m-3 specific to NL
Range for pollutant 1 for hour in ug.m-3 specific to NO
Range for pollutant 9 for hour in ug.m-3 specific to NO
Range for pollutant 38 for hour in ug.m-3 specific to NO
Range for pollutant 6001 for week in ug.m-3 specific to NO
Range for pollutant 431 for hour in ug.m-3 specific to PT
Range for pollutant 482 for hour in ug.m-3 specific to PT
Range for pollutant 1 for hour in ug.m-3 specific to RO
Range for pollutant 5 for day in ug.m-3 specific to RO
Range for pollutant 7 for hour in ug.m-3 specific to RO
Range for pollutant 8 for hour in ug.m-3 specific to RO
Range for pollutant 9 for hour in ug.m-3 specific to RO
Range for pollutant 10 for hour in mg.m-3 specific to RO
Range for pollutant 12 for day in ug.m-3 specific to RO
Range for pollutant 14 for day in ng.m-3 specific to RO
Range for pollutant 15 for day in ng.m-3 specific to RO
Range for pollutant 18 for day in ng.m-3 specific to RO
Range for pollutant 20 for hour in ug.m-3 specific to RO
Range for pollutant 6001 for day in ug.m-3 specific to RO
Range for pollutant 1 for day in ug.m-3 specific to RS
Range for pollutant 1 for hour in ug.m-3 specific to RS
Range for pollutant 5 for day in ug.m-3 specific to RS
Range for pollutant 5 for hour in ug.m-3 specific to RS
Range for pollutant 6 for day in ug.m-3 specific to RS
Range for pollutant 7 for day in ug.m-3 specific to RS
Range for pollutant 7 for hour in ug.m-3 specific to RS
Range for pollutant 8 for day in ug.m-3 specific to RS
Range for pollutant 8 for hour in ug.m-3 specific to RS
Range for pollutant 9 for day in ug.m-3 specific to RS
Range for pollutant 9 for hour in ug.m-3 specific to RS
Range for pollutant 10 for day in mg.m-3 specific to RS
Range for pollutant 10 for hour in mg.m-3 specific to RS
Range for pollutant 20 for day in ug.m-3 specific to RS
Range for pollutant 38 for day in ug.m-3 specific to RS
Range for pollutant 38 for hour in ug.m-3 specific to RS
Range for pollutant 5 for hour in ug.m-3 specific to SE
Range for pollutant 9 for hour in ug.m-3 specific to SE
Range for pollutant 83 for hour in ug.m-3 specific to SE
Range for pollutant 432 for hour in ug.m-3 specific to SE
Range for pollutant 441 for hour in ug.m-3 specific to SE
Range for pollutant 443 for hour in ug.m-3 specific to SE
Range for pollutant 475 for hour in ug.m-3 specific to SE
Range for pollutant 482 for hour in ug.m-3 specific to SE
Range for pollutant 486 for hour in ug.m-3 specific to SE
Range for pollutant 503 for hour in ug.m-3 specific to SE
Range for pollutant 505 for hour in ug.m-3 specific to SE
Range for pollutant 6012 for hour in ug.m-3 specific to SE
Range for pollutant 6013 for hour in ug.m-3 specific to SE
Range for pollutant 1 for day in ug.m-3 specific to SI
Range for pollutant 1 for hour in ug.m-3 specific to SI
Range for pollutant 5 for day in ug.m-3 specific to SI
Range for pollutant 5 for hour in ug.m-3 specific to SI
Range for pollutant 8 for day in ug.m-3 specific to SI
Range for pollutant 9 for hour in ug.m-3 specific to SI
Range for pollutant 10 for hour in mg.m-3 specific to SI
Range for pollutant 12 for day in ug.m-3 specific to SI
Range for pollutant 14 for day in ng.m-3 specific to SI
Range for pollutant 15 for day in ng.m-3 specific to SI
Range for pollutant 18 for day in ng.m-3 specific to SI
Range for pollutant 20 for hour in ug.m-3 specific to SI
Range for pollutant 21 for hour in ug.m-3 specific to SI
Range for pollutant 431 for hour in ug.m-3 specific to SI
Range for pollutant 464 for hour in ug.m-3 specific to SI
Range for pollutant 482 for hour in ug.m-3 specific to SI
Range for pollutant 611 for week in ug.m-2.day-1 specific to SI
Range for pollutant 656 for week in ug.m-2.day-1 specific to SI
Range for pollutant 2013 for 2week in ng.l-1 specific to SI
Range for pollutant 4813 for day in ng.m-3 specific to SI
Range for pollutant 5380 for day in ng.m-3 specific to SI
Range for pollutant 5419 for day in ng.m-3 specific to SI
Range for pollutant 5610 for day in ng.m-3 specific to SI
Range for pollutant 5655 for day in ng.m-3 specific to SI
Range for pollutant 6001 for day in ug.m-3 specific to SI
Range for pollutant 7014 for week in ug.m-2.day-1 specific to SI
Range for pollutant 7015 for week in ug.m-2.day-1 specific to SI
Range for pollutant 7018 for week in ug.m-2.day-1 specific to SI
Range for pollutant 7029 for week in ug.m-2.day-1 specific to SI
Range for pollutant 7380 for week in ug.m-2.day-1 specific to SI
Range for pollutant 7419 for week in ug.m-2.day-1 specific to SI
Range for pollutant 1 for hour in ug.m-3 specific to SK
Range for pollutant 5 for hour in ug.m-3 specific to SK
Range for pollutant 18 for day in ng.m-3 specific to SK
Range for pollutant 1 for hour in ug.m-3 specific to TR
Range for pollutant 5 for hour in ug.m-3 specific to TR
Range for pollutant 1 for var in ug.m-3 specific to FR
Range for pollutant 1 for hour in ug.m-3 specific to AT
Range for pollutant 5 for day in ug.m-3 specific to AT
Range for pollutant 5 for hour in ug.m-3 specific to AT
Range for pollutant 7 for hour in ug.m-3 specific to AT
Range for pollutant 8 for hour in ug.m-3 specific to AT
Range for pollutant 10 for hour in mg.m-3 specific to AT
Range for pollutant 12 for day in ug.m-3 specific to AT
Range for pollutant 12 for year in ug.m-3 specific to AT
Range for pollutant 14 for day in ng.m-3 specific to AT
Range for pollutant 14 for year in ng.m-3 specific to AT
Range for pollutant 15 for day in ng.m-3 specific to AT
Range for pollutant 15 for year in ng.m-3 specific to AT
Range for pollutant 18 for day in ng.m-3 specific to AT
Range for pollutant 18 for year in ng.m-3 specific to AT
Range for pollutant 20 for day in ug.m-3 specific to AT
Range for pollutant 20 for hour in ug.m-3 specific to AT
Range for pollutant 20 for year in ug.m-3 specific to AT
Range for pollutant 21 for day in ug.m-3 specific to AT
Range for pollutant 38 for hour in ug.m-3 specific to AT
Range for pollutant 316 for day in ug.m-3 specific to AT
Range for pollutant 431 for day in ug.m-3 specific to AT
Range for pollutant 441 for day in ug.m-3 specific to AT
Range for pollutant 443 for day in ug.m-3 specific to AT
Range for pollutant 449 for day in ug.m-3 specific to AT
Range for pollutant 450 for day in ug.m-3 specific to AT
Range for pollutant 464 for day in ug.m-3 specific to AT
Range for pollutant 475 for day in ug.m-3 specific to AT
Range for pollutant 482 for day in ug.m-3 specific to AT
Range for pollutant 486 for day in ug.m-3 specific to AT
Range for pollutant 616 for year in ng.m-3 specific to AT
Range for pollutant 633 for year in ng.m-3 specific to AT
Range for pollutant 762 for year in ng.m-3 specific to AT
Range for pollutant 6001 for day in ug.m-3 specific to AT
Range for pollutant 6002 for day in ug.m-3 specific to AT
Range for pollutant 6008 for day in ug.m-3 specific to AT
Range for pollutant 6009 for day in ug.m-3 specific to AT
Range for pollutant 6011 for day in ug.m-3 specific to AT
Range for pollutant 6012 for day in ug.m-3 specific to AT
Range for pollutant 6013 for day in ug.m-3 specific to AT
Range for pollutant 6015 for year in ng.m-3 specific to AT
Range for pollutant 1 for hour in ug.m-3 specific to BE
Range for pollutant 5 for hour in ug.m-3 specific to BE
Range for pollutant 6 for day in ug.m-3 specific to BE
Range for pollutant 7 for hour in ug.m-3 specific to BE
Range for pollutant 8 for hour in ug.m-3 specific to BE
Range for pollutant 10 for hour in mg.m-3 specific to BE
Range for pollutant 12 for day in ug.m-3 specific to BE
Range for pollutant 13 for hour in ng.m-3 specific to BE
Range for pollutant 14 for day in ng.m-3 specific to BE
Range for pollutant 15 for day in ng.m-3 specific to BE
Range for pollutant 18 for day in ng.m-3 specific to BE
Range for pollutant 20 for day in ug.m-3 specific to BE
Range for pollutant 20 for hour in ug.m-3 specific to BE
Range for pollutant 38 for hour in ug.m-3 specific to BE
Range for pollutant 2013 for week in ng.l-1 specific to BE
Range for pollutant 3012 for day in ug.m-3 specific to BE
Range for pollutant 3014 for day in ng.m-3 specific to BE
Range for pollutant 3015 for day in ng.m-3 specific to BE
Range for pollutant 3018 for day in ng.m-3 specific to BE
Range for pollutant 5012 for day in ug.m-3 specific to BE
Range for pollutant 5014 for day in ng.m-3 specific to BE
Range for pollutant 5015 for day in ng.m-3 specific to BE
Range for pollutant 5018 for day in ng.m-3 specific to BE
Range for pollutant 6001 for hour in ug.m-3 specific to BE
Range for pollutant 6015 for day in ng.m-3 specific to BE
Range for pollutant 1 for hour in ug.m-3 specific to BG
Range for pollutant 4 for day in ug.m-3 specific to BG
Range for pollutant 11 for hour in ug.m-3 specific to BG
Range for pollutant 35 for hour in ug.m-3 specific to BG
Range for pollutant 5 for day in ug.m-3 specific to CY
Range for pollutant 5 for hour in ug.m-3 specific to CY
Range for pollutant 15 for day in ng.m-3 specific to CY
Range for pollutant 16 for day in ng.m-3 specific to CY
Range for pollutant 17 for day in ng.m-3 specific to CY
Range for pollutant 49 for day in ng.m-3 specific to CY
Range for pollutant 63 for day in ng.m-3 specific to CY
Range for pollutant 65 for day in ng.m-3 specific to CY
Range for pollutant 73 for day in ng.m-3 specific to CY
Range for pollutant 604 for day in ng.m-3 specific to CY
Range for pollutant 1047 for day in ug.m-3 specific to CY
Range for pollutant 1629 for day in ug.m-3 specific to CY
Range for pollutant 5654 for day in ng.m-3 specific to CY
Range for pollutant 6001 for day in ug.m-3 specific to CY
Range for pollutant 1 for hour in ug.m-3 specific to CZ
Range for pollutant 5 for day in ug.m-3 specific to CZ
Range for pollutant 5 for hour in ug.m-3 specific to CZ
Range for pollutant 7 for hour in ug.m-3 specific to CZ
Range for pollutant 8 for hour in ug.m-3 specific to CZ
Range for pollutant 9 for hour in ug.m-3 specific to CZ
Range for pollutant 10 for hour in mg.m-3 specific to CZ
Range for pollutant 12 for day in ug.m-3 specific to CZ
Range for pollutant 14 for day in ng.m-3 specific to CZ
Range for pollutant 15 for day in ng.m-3 specific to CZ
Range for pollutant 18 for day in ng.m-3 specific to CZ
Range for pollutant 20 for day in ug.m-3 specific to CZ
Range for pollutant 20 for hour in ug.m-3 specific to CZ
Range for pollutant 38 for hour in ug.m-3 specific to CZ
Range for pollutant 3012 for day in ug.m-3 specific to CZ
Range for pollutant 3014 for day in ng.m-3 specific to CZ
Range for pollutant 3015 for day in ng.m-3 specific to CZ
Range for pollutant 3018 for day in ng.m-3 specific to CZ
Range for pollutant 6001 for day in ug.m-3 specific to CZ
Range for pollutant 6001 for hour in ug.m-3 specific to CZ
Range for pollutant 6015 for day in ng.m-3 specific to CZ
Range for pollutant 38 for hour in ug.m-3 specific to DK
Range for pollutant 48 for day in ng.m-3 specific to DK
Range for pollutant 1 for hour in ug.m-3 specific to EE
Range for pollutant 4 for day in ug.m-3 specific to EE
Range for pollutant 5 for day in ug.m-3 specific to EE
Range for pollutant 7 for hour in ug.m-3 specific to EE
Range for pollutant 8 for hour in ug.m-3 specific to EE
Range for pollutant 9 for hour in ug.m-3 specific to EE
Range for pollutant 10 for hour in mg.m-3 specific to EE
Range for pollutant 12 for day in ug.m-3 specific to EE
Range for pollutant 14 for day in ng.m-3 specific to EE
Range for pollutant 15 for day in ng.m-3 specific to EE
Range for pollutant 18 for day in ng.m-3 specific to EE
Range for pollutant 20 for day in ug.m-3 specific to EE
Range for pollutant 5029 for day in ng.m-3 specific to EE
Range for pollutant 6001 for day in ug.m-3 specific to EE
Range for pollutant 25 for var in ug.m-3 specific to ES
Range for pollutant 441 for var in ug.m-3 specific to ES
Range for pollutant 443 for var in ug.m-3 specific to ES
Range for pollutant 449 for var in ug.m-3 specific to ES
Range for pollutant 450 for var in ug.m-3 specific to ES
Range for pollutant 451 for var in ug.m-3 specific to ES
Range for pollutant 475 for var in ug.m-3 specific to ES
Range for pollutant 486 for var in ug.m-3 specific to ES
Range for pollutant 643 for month in ng.m-3 specific to ES
Range for pollutant 715 for month in ng.m-3 specific to ES
Range for pollutant 4406 for month in ng.m-3 specific to ES
Range for pollutant 5045 for day in ug.m-3 specific to ES
Range for pollutant 5046 for day in ug.m-3 specific to ES
Range for pollutant 5047 for day in ug.m-3 specific to ES
Range for pollutant 5629 for day in ug.m-3 specific to ES
Range for pollutant 5631 for day in ug.m-3 specific to ES
Range for pollutant 5657 for day in ug.m-3 specific to ES
Range for pollutant 5659 for day in ug.m-3 specific to ES
Range for pollutant 5668 for day in ug.m-3 specific to ES
Range for pollutant 5759 for month in ng.m-3 specific to ES
Range for pollutant 6008 for var in ug.m-3 specific to ES
Range for pollutant 6009 for var in ug.m-3 specific to ES
Range for pollutant 6011 for var in ug.m-3 specific to ES
Range for pollutant 6012 for var in ug.m-3 specific to ES
Range for pollutant 6013 for var in ug.m-3 specific to ES
Range for pollutant 1 for hour in ug.m-3 specific to FI
Range for pollutant 4 for day in ug.m-3 specific to FI
Range for pollutant 5 for day in ug.m-3 specific to FI
Range for pollutant 5 for hour in ug.m-3 specific to FI
Range for pollutant 7 for hour in ug.m-3 specific to FI
Range for pollutant 8 for hour in ug.m-3 specific to FI
Range for pollutant 9 for hour in ug.m-3 specific to FI
Range for pollutant 10 for hour in mg.m-3 specific to FI
Range for pollutant 5018 for month in ng.m-3 specific to FI
Range for pollutant 6001 for hour in ug.m-3 specific to FI
Range for pollutant 20 for hour in ug.m-3 specific to FR
Range for pollutant 5018 for year in ng.m-3 specific to FR
Range for pollutant 6 for day in ug.m-3 specific to GB
Range for pollutant 12 for month in ug.m-3 specific to GB
Range for pollutant 12 for var in ug.m-3 specific to GB
Range for pollutant 12 for year in ug.m-3 specific to GB
Range for pollutant 13 for month in ng.m-3 specific to GB
Range for pollutant 13 for year in ng.m-3 specific to GB
Range for pollutant 14 for month in ng.m-3 specific to GB
Range for pollutant 14 for var in ng.m-3 specific to GB
Range for pollutant 14 for year in ng.m-3 specific to GB
Range for pollutant 15 for month in ng.m-3 specific to GB
Range for pollutant 15 for var in ng.m-3 specific to GB
Range for pollutant 15 for year in ng.m-3 specific to GB
Range for pollutant 18 for month in ng.m-3 specific to GB
Range for pollutant 18 for var in ng.m-3 specific to GB
Range for pollutant 18 for year in ng.m-3 specific to GB
Range for pollutant 20 for hour in ug.m-3 specific to GB
Range for pollutant 20 for var in ug.m-3 specific to GB
Range for pollutant 21 for hour in ug.m-3 specific to GB
Range for pollutant 24 for hour in ug.m-3 specific to GB
Range for pollutant 316 for hour in ug.m-3 specific to GB
Range for pollutant 351 for var in ng.m-3 specific to GB
Range for pollutant 394 for hour in ug.m-3 specific to GB
Range for pollutant 428 for hour in ug.m-3 specific to GB
Range for pollutant 430 for hour in ug.m-3 specific to GB
Range for pollutant 431 for hour in ug.m-3 specific to GB
Range for pollutant 432 for hour in ug.m-3 specific to GB
Range for pollutant 435 for var in ng.m-3 specific to GB
Range for pollutant 441 for hour in ug.m-3 specific to GB
Range for pollutant 443 for hour in ug.m-3 specific to GB
Range for pollutant 447 for hour in ug.m-3 specific to GB
Range for pollutant 449 for hour in ug.m-3 specific to GB
Range for pollutant 450 for hour in ug.m-3 specific to GB
Range for pollutant 451 for hour in ug.m-3 specific to GB
Range for pollutant 464 for hour in ug.m-3 specific to GB
Range for pollutant 475 for hour in ug.m-3 specific to GB
Range for pollutant 482 for hour in ug.m-3 specific to GB
Range for pollutant 486 for hour in ug.m-3 specific to GB
Range for pollutant 503 for hour in ug.m-3 specific to GB
Range for pollutant 505 for hour in ug.m-3 specific to GB
Range for pollutant 606 for var in ng.m-3 specific to GB
Range for pollutant 609 for var in ng.m-3 specific to GB
Range for pollutant 622 for var in ng.m-3 specific to GB
Range for pollutant 625 for var in ng.m-3 specific to GB
Range for pollutant 627 for year in ug.m-2.day-1 specific to GB
Range for pollutant 643 for var in ng.m-3 specific to GB
Range for pollutant 653 for var in ng.m-3 specific to GB
Range for pollutant 654 for var in ng.m-3 specific to GB
Range for pollutant 673 for var in pg.m-3 specific to GB
Range for pollutant 674 for var in pg.m-3 specific to GB
Range for pollutant 677 for var in pg.m-3 specific to GB
Range for pollutant 679 for var in pg.m-3 specific to GB
Range for pollutant 683 for var in pg.m-3 specific to GB
Range for pollutant 684 for var in pg.m-3 specific to GB
Range for pollutant 685 for var in pg.m-3 specific to GB
Range for pollutant 686 for var in pg.m-3 specific to GB
Range for pollutant 689 for var in pg.m-3 specific to GB
Range for pollutant 690 for var in pg.m-3 specific to GB
Range for pollutant 691 for var in pg.m-3 specific to GB
Range for pollutant 692 for var in pg.m-3 specific to GB
Range for pollutant 701 for var in pg.m-3 specific to GB
Range for pollutant 706 for var in pg.m-3 specific to GB
Range for pollutant 707 for var in pg.m-3 specific to GB
Range for pollutant 709 for var in pg.m-3 specific to GB
Range for pollutant 712 for var in ng.m-3 specific to GB
Range for pollutant 715 for var in ng.m-3 specific to GB
Range for pollutant 1629 for hour in ug.m-3 specific to GB
Range for pollutant 1668 for hour in ug.m-3 specific to GB
Range for pollutant 1771 for week in ug.m-3 specific to GB
Range for pollutant 1772 for week in ug.m-3 specific to GB
Range for pollutant 4330 for var in pg.m-3 specific to GB
Range for pollutant 4336 for var in pg.m-3 specific to GB
Range for pollutant 4339 for var in pg.m-3 specific to GB
Range for pollutant 4341 for var in pg.m-3 specific to GB
Range for pollutant 4406 for var in ng.m-3 specific to GB
Range for pollutant 4813 for var in ng.m-3 specific to GB
Range for pollutant 4813 for year in ng.m-3 specific to GB
Range for pollutant 5029 for 3month in ng.m-3 specific to GB
Range for pollutant 5029 for var in ng.m-3 specific to GB
Range for pollutant 5419 for year in ng.m-3 specific to GB
Range for pollutant 5610 for 3month in ng.m-3 specific to GB
Range for pollutant 5610 for var in ng.m-3 specific to GB
Range for pollutant 5617 for year in ng.m-3 specific to GB
Range for pollutant 5626 for 3month in ng.m-3 specific to GB
Range for pollutant 5626 for var in ng.m-3 specific to GB
Range for pollutant 5655 for 3month in ng.m-3 specific to GB
Range for pollutant 5655 for month in ng.m-3 specific to GB
Range for pollutant 5655 for var in ng.m-3 specific to GB
Range for pollutant 5655 for year in ng.m-3 specific to GB
Range for pollutant 6005 for hour in ug.m-3 specific to GB
Range for pollutant 6006 for hour in ug.m-3 specific to GB
Range for pollutant 6007 for hour in ug.m-3 specific to GB
Range for pollutant 6008 for hour in ug.m-3 specific to GB
Range for pollutant 6009 for hour in ug.m-3 specific to GB
Range for pollutant 6011 for hour in ug.m-3 specific to GB
Range for pollutant 6012 for hour in ug.m-3 specific to GB
Range for pollutant 6013 for hour in ug.m-3 specific to GB
Range for pollutant 6015 for var in ng.m-3 specific to GB
Range for pollutant 7012 for year in ug.m-2.day-1 specific to GB
Range for pollutant 1 for hour in ug.m-3 specific to GR
Range for pollutant 5 for hour in ug.m-3 specific to GR
Range for pollutant 12 for day in ug.m-3 specific to GR
Range for pollutant 20 for hour in ug.m-3 specific to GR
Range for pollutant 21 for hour in ug.m-3 specific to GR
Range for pollutant 38 for hour in ug.m-3 specific to GR
Range for pollutant 431 for hour in ug.m-3 specific to GR
Range for pollutant 464 for hour in ug.m-3 specific to GR
Range for pollutant 482 for hour in ug.m-3 specific to GR
Range for pollutant 1 for day in ug.m-3 specific to HU
Range for pollutant 1 for hour in ug.m-3 specific to HU
Range for pollutant 5 for day in ug.m-3 specific to HU
Range for pollutant 7 for hour in ug.m-3 specific to HU
Range for pollutant 8 for day in ug.m-3 specific to HU
Range for pollutant 8 for hour in ug.m-3 specific to HU
Range for pollutant 9 for hour in ug.m-3 specific to HU
Range for pollutant 10 for hour in mg.m-3 specific to HU
Range for pollutant 14 for day in ng.m-3 specific to HU
Range for pollutant 15 for day in ng.m-3 specific to HU
Range for pollutant 18 for day in ng.m-3 specific to HU
Range for pollutant 20 for day in ug.m-3 specific to HU
Range for pollutant 21 for day in ug.m-3 specific to HU
Range for pollutant 394 for day in ug.m-3 specific to HU
Range for pollutant 428 for day in ug.m-3 specific to HU
Range for pollutant 430 for day in ug.m-3 specific to HU
Range for pollutant 431 for day in ug.m-3 specific to HU
Range for pollutant 447 for day in ug.m-3 specific to HU
Range for pollutant 450 for day in ug.m-3 specific to HU
Range for pollutant 464 for day in ug.m-3 specific to HU
Range for pollutant 482 for day in ug.m-3 specific to HU
Range for pollutant 486 for day in ug.m-3 specific to HU
Range for pollutant 503 for day in ug.m-3 specific to HU
Range for pollutant 505 for day in ug.m-3 specific to HU
Range for pollutant 611 for month in ug.m-2.day-1 specific to HU
Range for pollutant 656 for month in ug.m-2.day-1 specific to HU
Range for pollutant 5029 for day in ng.m-3 specific to HU
Range for pollutant 5380 for day in ng.m-3 specific to HU
Range for pollutant 5419 for day in ng.m-3 specific to HU
Range for pollutant 5610 for day in ng.m-3 specific to HU
Range for pollutant 5655 for day in ng.m-3 specific to HU
Range for pollutant 6001 for day in ug.m-3 specific to HU
Range for pollutant 6005 for day in ug.m-3 specific to HU
Range for pollutant 7013 for month in ug.m-2.day-1 specific to HU
Range for pollutant 7014 for month in ug.m-2.day-1 specific to HU
Range for pollutant 7015 for month in ug.m-2.day-1 specific to HU
Range for pollutant 7018 for month in ug.m-2.day-1 specific to HU
Range for pollutant 7029 for month in ug.m-2.day-1 specific to HU
Range for pollutant 7380 for month in ug.m-2.day-1 specific to HU
Range for pollutant 7419 for month in ug.m-2.day-1 specific to HU
Range for pollutant 352 for year in ng.m-3 specific to IE
Range for pollutant 5626 for year in ng.m-3 specific to IE
Range for pollutant 5 for hour in ug.m-3 specific to IS
Range for pollutant 11 for hour in ug.m-3 specific to IS
Range for pollutant 6001 for hour in ug.m-3 specific to IS
Range for pollutant 1 for hour in ug.m-3 specific to IT
Range for pollutant 4 for day in ug.m-3 specific to IT
Range for pollutant 5 for day in ug.m-3 specific to IT
Range for pollutant 5 for hour in ug.m-3 specific to IT
Range for pollutant 7 for hour in ug.m-3 specific to IT
Range for pollutant 8 for hour in ug.m-3 specific to IT
Range for pollutant 9 for hour in ug.m-3 specific to IT
Range for pollutant 10 for hour in mg.m-3 specific to IT
Range for pollutant 11 for day in ug.m-3 specific to IT
Range for pollutant 11 for hour in ug.m-3 specific to IT
Range for pollutant 12 for day in ug.m-3 specific to IT
Range for pollutant 14 for day in ng.m-3 specific to IT
Range for pollutant 15 for day in ng.m-3 specific to IT
Range for pollutant 16 for day in ng.m-3 specific to IT
Range for pollutant 17 for day in ng.m-3 specific to IT
Range for pollutant 18 for day in ng.m-3 specific to IT
Range for pollutant 20 for day in ug.m-3 specific to IT
Range for pollutant 21 for day in ug.m-3 specific to IT
Range for pollutant 29 for day in ng.l-1 specific to IT
Range for pollutant 30 for day in ng.m-3 specific to IT
Range for pollutant 32 for day in ugC.m-3 specific to IT
Range for pollutant 32 for hour in ugC.m-3 specific to IT
Range for pollutant 33 for day in ug.m-3 specific to IT
Range for pollutant 35 for day in ug.m-3 specific to IT
Range for pollutant 38 for hour in ug.m-3 specific to IT
Range for pollutant 41 for day in ug.m-3 specific to IT
Range for pollutant 63 for day in ng.m-3 specific to IT
Range for pollutant 65 for day in ng.m-3 specific to IT
Range for pollutant 73 for day in ng.m-3 specific to IT
Range for pollutant 431 for day in ug.m-3 specific to IT
Range for pollutant 482 for day in ug.m-3 specific to IT
Range for pollutant 5014 for day in ng.m-3 specific to IT
Range for pollutant 5015 for day in ng.m-3 specific to IT
Range for pollutant 5016 for day in ng.m-3 specific to IT
Range for pollutant 5029 for day in ng.m-3 specific to IT
Range for pollutant 5029 for hour in ng.m-3 specific to IT
Range for pollutant 6001 for day in ug.m-3 specific to IT
Range for pollutant 1 for day in ug.m-3 specific to LT
Range for pollutant 1 for hour in ug.m-3 specific to LT
Range for pollutant 1 for week in ug.m-3 specific to LT
Range for pollutant 5 for hour in ug.m-3 specific to LT
Range for pollutant 7 for hour in ug.m-3 specific to LT
Range for pollutant 8 for day in ug.m-3 specific to LT
Range for pollutant 8 for hour in ug.m-3 specific to LT
Range for pollutant 8 for week in ug.m-3 specific to LT
Range for pollutant 9 for hour in ug.m-3 specific to LT
Range for pollutant 10 for hour in mg.m-3 specific to LT
Range for pollutant 20 for hour in ug.m-3 specific to LT
Range for pollutant 21 for hour in ug.m-3 specific to LT
Range for pollutant 24 for hour in ug.m-3 specific to LT
Range for pollutant 67 for day in ugN.m-3 specific to LT
Range for pollutant 67 for week in ugN.m-3 specific to LT
Range for pollutant 68 for day in ugN.m-3 specific to LT
Range for pollutant 68 for week in ugN.m-3 specific to LT
Range for pollutant 394 for hour in ug.m-3 specific to LT
Range for pollutant 428 for hour in ug.m-3 specific to LT
Range for pollutant 430 for hour in ug.m-3 specific to LT
Range for pollutant 431 for hour in ug.m-3 specific to LT
Range for pollutant 441 for hour in ug.m-3 specific to LT
Range for pollutant 443 for hour in ug.m-3 specific to LT
Range for pollutant 447 for hour in ug.m-3 specific to LT
Range for pollutant 450 for hour in ug.m-3 specific to LT
Range for pollutant 464 for hour in ug.m-3 specific to LT
Range for pollutant 475 for hour in ug.m-3 specific to LT
Range for pollutant 482 for hour in ug.m-3 specific to LT
Range for pollutant 486 for hour in ug.m-3 specific to LT
Range for pollutant 503 for hour in ug.m-3 specific to LT
Range for pollutant 505 for hour in ug.m-3 specific to LT
Range for pollutant 520 for day in ugS.m-3 specific to LT
Range for pollutant 520 for week in ugS.m-3 specific to LT
Range for pollutant 1046 for week in ug.m-3 specific to LT
Range for pollutant 1657 for week in ug.m-3 specific to LT
Range for pollutant 1659 for week in ug.m-3 specific to LT
Range for pollutant 1771 for week in ug.m-3 specific to LT
Range for pollutant 1772 for week in ug.m-3 specific to LT
Range for pollutant 4813 for hour in ng.m-3 specific to LT
Range for pollutant 5012 for month in ug.m-3 specific to LT
Range for pollutant 5014 for month in ng.m-3 specific to LT
Range for pollutant 5015 for month in ng.m-3 specific to LT
Range for pollutant 5018 for month in ng.m-3 specific to LT
Range for pollutant 5419 for month in ng.m-3 specific to LT
Range for pollutant 5610 for month in ng.m-3 specific to LT
Range for pollutant 5617 for month in ng.m-3 specific to LT
Range for pollutant 5626 for month in ng.m-3 specific to LT
Range for pollutant 5655 for month in ng.m-3 specific to LT
Range for pollutant 6001 for hour in ug.m-3 specific to LT
Range for pollutant 6001 for week in ug.m-3 specific to LT
Range for pollutant 6005 for hour in ug.m-3 specific to LT
Range for pollutant 6006 for hour in ug.m-3 specific to LT
Range for pollutant 6007 for hour in ug.m-3 specific to LT
Range for pollutant 6011 for hour in ug.m-3 specific to LT
Range for pollutant 6012 for hour in ug.m-3 specific to LT
Range for pollutant 6013 for hour in ug.m-3 specific to LT
Range for pollutant 7013 for month in ug.m-2.day-1 specific to LT
Range for pollutant 7014 for month in ug.m-2.day-1 specific to LT
Range for pollutant 7015 for month in ug.m-2.day-1 specific to LT
Range for pollutant 7018 for month in ug.m-2.day-1 specific to LT
Range for pollutant 1629 for week in ug.m-3 specific to LV
Range for pollutant 2015 for week in ug.l-1 specific to LV
Range for pollutant 2018 for week in ug.l-1 specific to LV
Range for pollutant 5610 for week in ng.m-3 specific to LV
Range for pollutant 5617 for week in ng.m-3 specific to LV
Range for pollutant 5626 for week in ng.m-3 specific to LV
Range for pollutant 5655 for week in ng.m-3 specific to LV
Range for pollutant 7015 for month in ug.m-2.day-1 specific to LV
Range for pollutant 7018 for month in ug.m-2.day-1 specific to LV
Range for pollutant 5610 for var in ng.m-3 specific to FI
Range for pollutant 5626 for var in ng.m-3 specific to FI
Range for pollutant 5617 for var in ng.m-3 specific to FI
Range for pollutant 5655 for var in ng.m-3 specific to FI
Range for pollutant 717 for var in ug/m2/day specific to FI
A monitoring facility used to observe air pollution
Objective Estimation and/or Expert Judgement
Time/averaging period of primary observation - to be specified when aggregating statistics within om:parameter
Parameter used in D1b to declare that resultencoding is to be provided in E1b. In E1b, further description of encoding is to be provided via http://dd.eionet.europa.eu/vocabulary/aq/resultencoding
Parameter used in D1b to declare that result format is to be provided in E1b. In E1b, further description of the location is to be provided via http://dd.eionet.europa.eu/vocabulary/aq/resultformat
Differentiates between the annual mean Stage 1 & 2 health protection target for PM2.5 both of which use annual mean as the reporting metric.
Please note that countries should use either H or V separately
No available technology or solution exists to address the issue in the specific context.
The cost of the measure would entail disproportionate costs.
Measure not applicable to the pollutants exceeding limit values.
No available budget or staff to support the measure.
Not within the competence of the AQ plan authority
The competence authority lies outside the AQ plan authority’s control.
The measure is already in place; no further action needed.
Past evidence or modelling shows low impact on air quality (applicable for O3).
Implementation paused pending results from other measures.
Legislation does not permit or enable the implementation.
The measure contradicts or undermines other existing policies, plans and/or measures.
Implementation is delayed due to legal, procurement, or planning processes.
Measure under review or update before potential implementation.
Scientific or technical data is lacking to support implementation.
The measure is deprioritized in favor of more impactful or urgent actions.
Strong resistance from the public or key stakeholders prevents implementation.
GMES (Global Monitoring for Environment and Security)
GMES (Global Monitoring for Environment and Security) is the European Programme for the establishment of a European capacity for Earth Observation.
OECD (Organisation for Economic Co-operation and Development)
Organisation for Economic Co-operation and Development (OECD), an international organisation helping governments tackle the economic, social and governance challenges of a globalised economy.
The Global Atmosphere Watch (GAW) programme of WMO is a partnership involving 80 countries, which provides reliable scientific data and information on the chemical composition of the atmosphere, its natural and anthropogenic change, and helps to improve the understanding of interactions between the atmosphere, the oceans and the biosphere.
EMEP (European Monitoring and Evaluation Programme)
EMEP (European Monitoring and Evaluation Programme) is a scientifically based and policy driven programme under the Convention on Long-range Transboundary Air Pollution for international co-operation to solve transboundary air pollution problems.
Three consecutive hours in exceedance (at locations representative of air quality over at least 100 km 2 or an entire zone or agglomeration, which ever is smaller) ONLY NO2 & SO2 - ALT
The percentile 90,4 for PM 10 in the particular case when random measurements are applied instead of continuous measurements
The Average Exposure Indicator expressed in μg/m3 (AEI) shall be based upon measurements in urban background locations in zones and agglomerations throughout the territory of a Member State. It should be assessed as a three-calendar year running annual mean concentration averaged over all sampling points established pursuant to Section B of Annex V of Directive 2008/50/EC.
Accumulated Ozone Exposure 40 (expressed in (μg/m3) ∙ hours) means the sum of the difference between hourly concentrations greater than 80 μg/m3 and 80 μg/m3 between 1 May to 31 July using only the one-hour values measured between 8.00 and 20.00 Central European Time (CET) each day.
AOT40 vegetation protection (AOT40) averaged over 5 years. As per Directive 2008/50/EC, If the three or five year averages cannot be determined on the basis of a full and consecutive set of annual data, the minimum annual data required for checking compliance with the target values will be as follows for the target value for the protection of vegetation: valid data for three years.
Accumulated Ozone Exposure 40 (expressed in (μg/m3) ∙ hours) means the sum of the difference between hourly concentrations greater than 80 μg/m3 and 80 μg/m3 between 1 April to 31 September using only the one-hour values measured between 8.00 and 20.00 Central European Time (CET) each day.
NA is to be used when reporting an EnvironmentalObjective that does not have a reporting metric (e.g. When reporting Ozone precursos as Monitoring Objective)
Average between 1st January to 31st December (1/1/year X - 31/12/year X)
Calendar year
Days in exceedance in a calendar year (i.e. For PM10 and SO2 number of days when daily mean has exceeded the Limit Value in 1 calendar year. For O3 & CO, days when maximum daily 8-h mean exceed the LTO & LV, respectively in 1 calendar year)
Days in exceedance averaged over 3 calendar years
Days in exceedance averaged over 3 years. Applicable to Ozone Health Target Value as "Days when maximum daily eight- hour mean exceeded the target value averaged over 3 years"
Number of hours in exceedance in a calendar year
Average over winter. Average between 1st October year x-1 to 31st March year X.
Three consecutive days in exceedance (at locations representative of air quality over at least 100 km 2 or an entire zone, which ever is smaller) ONLY PM2.5 & PM10 - ALT
AQD - Specific encoding of results provided (inline/external)
External - results are provided outside the XML
Inline - results are provided within the XML
AQD - Specific format of results provided
The AGL is an instrument from the UK for measuring BlackSmoke and acidity. The AGL instrument is used in conjunction with the EEL (Diffusion Systems) Model 43 smoke stain reflectometer. The zero is set with the reflectometer switched off. The instrument is checked for correct functioning using a calibrating tile. The measuring head Is set on the white standard tile and the control adjusted to read 100. The head is then moved to the grey half of the tile which has a calibration marked on it. The instrument should agree with this calibration to ±1.5 divisions. The white tile is now covered by a clean Whatman No. 1 filter paper smooth side uppermost. The instrument Is re-set to 100. Stained papers are assessed on the white tile. The instrument does not use a coloured filter.
Instrument for pumping 2m3 air per day through absorbing solution ( in glass container).
Bergerhoff (bulk sampler for deposition of heavy metals and PAHs)
The Digitel High Volume Sampler DH-77 is a system to sample dust and aerosol particles for later assessment and analysis. The sampler operation range in standard execution is 100 to 1000 litres per minute (6 to 60 cubic metres per hour). The system's usual designation is 'High Volume Sampler'. Air-borne-dust parts in the sampled air are separated onto 150 mm diameter filters
INTERSCIENCE Finnigan trace GC ultre + trace DSQ
The IHE instrument is an instrument from Belgium to measure BlackSmoke and acidity. The IHE instrument is used with the Diffusion Systems Reflectometer Mark III Model 11. The instrument is zeroed using a standard black tile and the span (100) by setting the measuring head on the smooth side of a Whatman No. 1 filter paper set on a standard white tile - supplied with the black standard. The smoke stained filter is evaluated on the standard white tile. The reflectometer uses a green filter.
Medium volumen sampler for PM10 and PM2.5
Low volume sampler for gravimetric determination of the mass concentration PM10 or PM2.5 of particulate matter in suspension, with sample collection on filter and determination in laboratory. With a capacity of up to 30 filters
System for the collection of samples in absorption tubes for subsequent analysis in the laboratory. The instrument is intended for the collection of volatile organic compounds present in the atmosphere. The collection is carried out in tubes with chemical sorbents, with daily sampling, which allow its collection. The equipment has a sequential module to be able to carry out continuous campaigns of several days
High Volume Sampler HVS16. Microcomputer controlled gas collector for the automated dust sampling on membrane filters with a diameter of 140 mm or 150 mm in acc. with EN 12341. Automatic switching to sequentially admit up to 16 filters
Collection on 16 filters for the subsequent laboratory analysis in samples.
Control system for the automated collection of gases and particles on adsorption tubes, wash-bottles, or filters. The control program has a modular structure and, with an optional sampling switching, can log up to 8 sequential samples (optionally up to 16)
EIGENBRODT (NSA 181 KHT) - WET ONLY SAMPLER
ENVIRONNEMENT AUTOMATIC SEQUENTIAL PARTICULATE SAMPLER
PM162M is a sequential automatic sampling device for particulate matter in the ambient air. The particles are sampled at constant flow rate (1 m3/h or 2.3 m3/h) and collected on filters for gravimetric weighing and possible physicochemical laboratory analysis
Sequential Air Sampler, Type EK, Aerosol filter as for sulphate + oxalic acid im
Sequential Air Sampler, Type EK. KOH-impregnated Whatman 40 filter
Sequential Air Sampler, Type SS2000. NaI-impregnated glass sinters
Diffusion Systems Ltd: Smoke Stain Reflectometer mod. 43
This will be remove shortly from CODELIST
Digitel DPA96MV (active sampling for VOC)
The Environnement SF8 is an instrument from France to measure Black Smoke & Acidity The Environnement SF8 instrument is used with a Photovolt Model 670 reflectometer, to measure the degree of staining on Schneider CA 32 filter paper. The reflectometer is zeroed by setting the measuring head on a standard black tile and to 100 when set on a pile of clean Schneider filter papers. A standard white tile of similar reflectance to the filter papers is used to check the calibration which should not differ from clean filter paper by more than ±2 divisions. Each stain is measured with the stained paper set on a pile of clean filter papers. The reflectometer uses a green optical filter.
Modified diffusion tube by Gradko to measure NH3
The LIFETEK PMS model is certified for outdoor use in temperatures ranging from -20 C° to 50 °C. https://dilus.com/wp-content/uploads/2021/02/LIFETEK-PMS-SERIES-1.pdf
The Ogawa sampler is a badge-type sampler that can be equipped with a sampling filter on either side of the sampler body. Sampling filters consist of cellulose fibre.
To include both PM10, PM2.5 or other PM fraction...
Passive sampler (Carbopack E),Perkin-Elmer ATD 400,HP GC 5890,HP MS 5792
PERKIN ELMER Turbomatrix Desorber, PERKIN ELMER Clarus 500
Semi-automatic combined filter and impinger
Semi-automatic (combined filter and impinger) device for daily sampling of NO2, SO2, and soot in ambient air
Sunset Laboratory Inc Thermal / Optical Carbon Analyser
Thermo Scientific: Trace GC ultra + DSQII
Thermo Scientific: Trace GC ultra + Trace MS
Active sampler 0.004 m3/h - Gold trap - manual sample change
ACTIVE - Low Volume Sampling with manual change - Gold trap. Air sampling flow to be 0.004 m³/h
Active sampler 0.05 m³/h - Activated charcoal - automatic sample change
ACTIVE - Low Volume Sampling with automatic change of activated charcoal samplers. Air sampling flow to be 1 m³/h
Active sampler 0.05 m³/h - activated charcoal - manual sample change
ACTIVE - Low Volume Sampling with manual change of activated charcoal samplers. Air sampling flow to be 1 m³/h
Active sampler 0.06 m³/h - Gold trap - automatic sample change
ACTIVE - Low Volume Sampling with automatic change - Gold trap. Air sampling flow to be 0.06 m³/h
Active sampler 0.12 m³/h - denuders - automatic sample change
ACTIVE - Low Volume Sampling with automatic change of Denuders. Air sampling flow to be 0.12 m³/h
Active sampler 0.12 m³/h - denuders&filters - automatic sample change
ACTIVE - Low Volume Sampling with automatic change of Denuders&Filters. Air sampling flow to be 0.12 m³/h
Active sampler 0.12 m³/h - denuders - manual sample change
ACTIVE - Low Volume Sampling with manual change of Denuders. Air sampling flow to be 0.12 m³/h
Active sampler 0.12 m³/h - denuders&filters - manual sample change
ACTIVE - Low Volume Sampling with manual change of Denuders&Filters. Air sampling flow to be 0.12 m³/h
Active sampler 0.1 m³/h - filters - manual sample change
ACTIVE - Low Volume Sampling with manual change of filters. Air sampling flow to be 0.1 m³/h
Active sampler 0.6 m³/h - denuders - automatic sample change
ACTIVE - Low Volume Sampling with automatic change of Denuders. Air sampling flow to be 0.6 m³/h
Active sampler 0.6 m³/h – quartz filter – automatic sample change
ACTIVE - Low Volume Sampling with automatic change of quartz filers. Air sampling flow to be 0.6 m³/h
Active sampler 15 m³/h - filters - automatic sample change
ACTIVE - Medium Volume Sampling with automatic change of filters. Air sampling flow to be 15 m³/h
Active sampler 15 m³/h - filters - manual sample change
ACTIVE - Medium Volume Sampling with manual change of filters. Air sampling flow to be 15 m³/h
Active sampler 1 m³/h - canisters - automatic sample change
ACTIVE - Low Volume Sampling with automatic change of canisters. Air sampling flow to be 1 m³/h
Active sampler 1 m³/h - filters - automatic sample change
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 1 m³/h
Active sampler 1 m³/h - canisters - manual sample change
ACTIVE - Low Volume Sampling with manual change of canisters. Air sampling flow to be 1 m³/h
Active sampler 1 m³/h - filters - manual sample change
ACTIVE - Low Volume Sampling with manual change of filters. Air sampling flow to be 1 m³/h
Active sampler 2.3 m³/h - filters - automatic sample change
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 2.3 m³/h
Active sampler 2.3 m³/h - PU foam - automatic sample change
ACTIVE - Medium Volume Sampling with automatic change of PU foam. Air sampling flow to be 2.3 m³/h
Active sampler 2.3 m³/h - filters - manual sample change
ACTIVE - Low Volume Sampling with manual change of filters. Air sampling flow to be 2.3 m³/h
Active sampler 30 m³/h - filters - automatic sample change
ACTIVE - High Volume Sampling with automatic change of filters. Air sampling flow to be 30 m³/h
Active sampler 30 m³/h - PU foam - automatic sample change
ACTIVE - High Volume Sampling with automatic change of PU foam. Air sampling flow to be 30 m³/h
Active sampler 30 m³/h - PU foam&Filters - automatic sample change
ACTIVE - High Volume Sampling with automatic change of PU foam&Filters. Air sampling flow to be 30 m³/h
Active sampler 30 m³/h - filters - manual sample change
ACTIVE - High Volume Sampling with manual change of filters. Air sampling flow to be 30 m³/h
Active sampler 5 m³/h - PU foam - automatic sample change
ACTIVE - Medium Volume Sampling with automatic change of PU foam. Air sampling flow to be 5 m³/h
Active sampler 5 m³/h - PU foam&Filters - automatic sample change
ACTIVE - Medium Volume Sampling with automatic change of PU foam&Filters. Air sampling flow to be 5 m³/h
Active sampler 5 m³/h - PU foam - manual sample change
ACTIVE - Medium Volume Sampling with manual change of PU foam. Air sampling flow to be 5 m³/h
Active sampler 5 m³/h - PU foam&Filters - manual sample change
ACTIVE - Medium Volume Sampling with manual change of PU foam&Filters. Air sampling flow to be 5 m³/h
Active sampler 68 m³/h - filters - automatic sample change
ACTIVE - High Volume Sampling with automatic change of filters. Air sampling flow to be 68 m³/h
Active sampler 68 m³/h - filters - manual sample change
ACTIVE - High Volume Sampling with manual change of filters. Air sampling flow to be 68 m³/h
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 0.7 m³/d
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 0,8 m³/h
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 0,9 m³/h
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 1.5 m³/d
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 2.2 m³/d
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 2,3 m³/h
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 21 m³/d
ACTIVE - Low Volume Sampling with manual change of filters. Air sampling flow to be 0.24 m³/h
ACTIVE - Low Volume Sampling with automatic change of filters. Air sampling flow to be 0,03 m³/h
ACTIVE - Low Volume Sampling with manual change of filters. Air sampling flow to be 0,9 m³/h
ACTIVE - Low Volume Sampling with manual change of filters. Air sampling flow to be 0,8 m³/h
ACTIVE - Low Volume Sampling with manual change of filters. Air sampling flow to be 2,3 m³/h
MVS - manual puf cartridge change 5,0 m3/h
ACTIVE - Medium Volume Sampling with manual PUF cartridge. Air sampling flow to be 5,0 m3/h
Passive Sampler - Potassiumcarbonate&Glycerine
ACTIVE adsorbent - either solid or liquid
ACTIVE - Rainwater sampler only open when it rains
Deposition: wet and dry (also known as bulk)
PASSIVE adsorbent - either solid or liquid (Also know as Diffusive adsorbent)
Automatic Pumpling at about 2 m3 per day
Drawing air, at about 2 m3 per day, through a filter paper, by means of a pump. Sampling is for periods of 24 hours after which the filter is changed automatically. Sampling principle for instruments for Black Smoke sampling.
Used for National Assessment Exposure Indicator
Used to characterise a SamplingPoint to the Assessment Exposure for PM2.5
SamplingPoint used for the demonstration or substraction of exceedances attributable to natural sources
Sampling used for the demonstration or substraction of exceedances attributable to winter-sanding or -salting
Agricultural livestock and land activities; including fertilizer use; manure management; and crop residue burning.
Total aircraft operations at an airport; including landing; take-off (LTO); and taxiing.
Residential heating (wood; coal; gas); commercial and institutional buildings.
Industry production; combustion in manufacturing industry; solvent and other product use; and others.
Natural sources like biogenic emissions.
Emission source not listed; requires specification.
Passenger cars; trucks; buses; and motorcycles on roads.
Inland and sea-shipping vessels operating in ports or coastal areas.
Contribution from other countries across borders.
Waste treatment and disposal; including incineration.
AQD - IPR - EEA grid - Spatial Resolution
Spatial resolution of 10 meters following the EEA LAEA grid (EPSG:3035).
Spatial resolution of 100 meters following the EEA LAEA grid (EPSG:3035).
Spatial resolution of 1000 meters following the EEA LAEA grid (EPSG:3035).
Spatial resolution of 10000 meters following the EEA LAEA grid (EPSG:3035).
Spatial representativeness of sampling point
Located such that its pollution levels are representative of the average exposure of the general population within the type of area under assessment. The pollution level should not be dominated by a single source type (e.g. traffic), unless that source type is typical within the area under assessment. The station should usually be representative of a wider area of at least several square kilometers.
Located in close proximity to single industrial sources or industrial areas, in a location that should represent the highest concentrations to which the population within the zone are exposed to. A wide range of industrial sources can be considered here, including: a) thermal power generation, b) district heating plants, c) refineries, d) waste incineration/treatment plants, dump sites, e) mining, including gravel, oil, natural gas, f) airports or g) ports.
Located in close proximity to a road, in a location that should represent the highest concentrations to which the population are exposed to within the zone. Located such that the pollution level for the specific pollutant is determined predominantly by the emissions from road traffic (i.e. not ship, railway, airplane, off-road) on distinct major roads. As per ANNEX III of DIRECTIVE 2008/50/EC, for all pollutants, traffic-orientated sampling probes shall be at least 25 m from the edge of major junctions and no more than 10 m from the kerbside.
First year of implementation, adopted during reporting year
Minor modifications of the adopted plan may occur and do not need to be reported through the full information on AQ plan
Time extension for benzene annual mean Limit Value.
Time extension for NO2 hourly Limit Value
Time extension for NO2 annual mean Limit Value.
Time extension for PM10 daily Limit Value.
Time extension for PM10 annual mean Limit Value.
Timescale of the action is unknown or undetermined.
AQD Time Zone - used for aggregated data & statistics
Coordinated Universal Time (UTC) is the primary time standard by which the world regulates clocks and time. (Wikipedia) or defined as the time scale which forms the basis of a coordinated radio dissemination of standard frequencies and time signals (ISO_8601-2004)
UTC offset of +01 hours. For example, the local time in a time zone which observes UTC+01 is calculated by adding 1 hours to UTC.
UTC offset of -01 hours. For example, the local time in a time zone which observes UTC-01 is calculated by substracting 1 hours to UTC.
AQD - AQ Assessment & Management Zone Type
‘Agglomeration’ shall mean a zone that is a conurbation with a population in excess of 250 000 inhabitants or, where the population is 250 000 inhabitants or less, with a given population density per km2 to be established by the Member States.
A zone delimited by a Member State for the purposes of air quality assessment and management which does not fullfil the requirements of an agglomeration