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Environmental Analysis · Sample Types

Ambient Immission

TS EN 12341 (PM10 and PM2.5 — gravimetric reference method)TS EN 14211 (NO2 and NO — chemiluminescence)TS EN 14212 (SO2 — ultraviolet fluorescence)TS EN 14625 (ozone — ultraviolet photometry)TS EN 14626 (CO — non-dispersive infrared spectroscopy)TS EN 14662 series (benzene)
Environmental Analysis laboratory work

What Is Ambient Immission?

Ambient air measurement determines pollutant concentrations in the air around a facility or in a residential area. It differs from emission: emission measures what leaves the source, while ambient measurement measures the level in the air people breathe. It is carried out with a fixed station, mobile laboratory or passive samplers.

Purpose of Ambient Immission

The purpose is to assess air quality's compliance with health-based limit values and determine a facility's environmental impact.

Which Products Is Ambient Immission Applied To?

  • Residential-area air quality monitoring
  • Industrial facility vicinity measurements
  • Measurements under EIA studies
  • Traffic-related pollution monitoring
  • Vicinity of a construction site or mine

In Which Sectors Is Ambient Immission Used?

EnvironmentPublic SectorChemistryPublic SectorConstructionMining

Standards Related to Ambient Immission

  • TS EN 12341 (PM10 and PM2.5 — gravimetric reference method)
  • TS EN 14211 (NO2 and NO — chemiluminescence)
  • TS EN 14212 (SO2 — ultraviolet fluorescence)
  • TS EN 14625 (ozone — ultraviolet photometry)
  • TS EN 14626 (CO — non-dispersive infrared spectroscopy)
  • TS EN 14662 series (benzene)

Ambient Immission Conditions

Measurement duration
Suited to the limit value's averaging period; daily, hourly or annual
Station siting
Macro- and micro-siting criteria defined in the annex to 2008/50/EC
Data capture
Legislation requires a minimum data capture rate
Meteorology
Wind direction and speed are recorded simultaneously; required for interpretation

Equipment for Ambient Immission

  • Fixed and mobile air quality monitoring stations
  • Gravimetric PM samplers and precision balance
  • Gas analysers (NOx, SO2, O3, CO)
  • Passive samplers
  • Meteorological station

Sample Requirements for Ambient Immission

  • Measurement is performed on site; PM filters are weighed in the laboratory
  • Station location and environmental conditions must be recorded
  • Meteorological data must be collected simultaneously
  • The measurement period must ensure seasonal representativeness

Duration of Ambient Immission

Short-term campaign measurements take days or weeks. If comparing against annual limit values, measurement must run long enough to meet the data capture rate legislation requires.

Ambient Immission Procedure

  1. 1The measurement purpose and pollutant list are determined.
  2. 2The station location is chosen per the legislative criteria.
  3. 3Instruments are installed and their calibration verified.
  4. 4Data is collected continuously through the measurement period.
  5. 5PM filters are conditioned and weighed.
  6. 6Data is validated and compared against the limit values.

Ambient Immission Acceptance Criteria

2008/50/EC defines limit values for PM10, PM2.5, NO2, SO2, benzene, lead and CO, and target values for ozone; each has a different averaging period and permitted number of exceedances. Applicable values are confirmed from current legislation.

Evaluation of Results

Limit values are meaningful together with their averaging periods: a measurement exceeding the hourly limit does not create a non-conformity if it stays within the permitted number of exceedances. An ambient air result also cannot be attributed to a single source; source contribution can only be assessed with wind direction data and modelling.

Ambient Immission Report

  • Station location, coordinates and surroundings description
  • Measurement period and data capture rate
  • Average, maximum and percentile values for each pollutant
  • Meteorological data
  • Limit and target values compared against

Accreditation

EUROLAB holds internationally recognised accreditation obtained from accreditation bodies party to the IAF and ILAC multilateral recognition arrangements, under ISO/IEC 17025 for laboratory testing, ISO/IEC 17020 for inspection and surveillance, and ISO/IEC 17021-1 and ISO/IEC 17065 for system and product certification. This chain ensures the reports and certificates issued are accepted worldwide.

Whether this test can be offered within accredited scope depends on your product and the standard applied; since accreditation is method-based, the scope is confirmed in writing at the quotation stage.

Scope and authorisations

Related Regulations

  • 2008/50/EC Ambient Air Quality Directive
  • 2004/107/EC (arsenic, cadmium, mercury, nickel and PAHs)
  • (EU) 2010/75 Industrial Emissions Directive

Environmental Analysis — What Does This Testing Field Cover?

The section below describes the field that the Ambient Immission test belongs to; the conditions and acceptance criteria of this particular test are given in the sections above. The scope specific to your product is confirmed in writing at the quotation stage.

Environmental analysis determines the presence and concentration of pollutants in water, soil, waste, air and flue gas samples. The output of this family is usually part of a permit, a declaration or an inspection file; the result has direct legal consequences.

In this family SAMPLING is half the result, and this is the feature that most sets the field apart. A sample taken at the wrong time, in the wrong container, under the wrong preservation or from the wrong point gives an invalid result no matter how well it is analysed in the laboratory. In waste water a grab sample and a composite sample give different information; in soil, surface and depth produce different results. Sampling therefore has its own standards and its own accreditation scope.

On the water side, physico-chemical parameters (pH, conductivity, turbidity, COD, BOD, suspended solids), ions, heavy metals, organic pollutants and microbiological parameters are measured. Drinking water and waste water carry different parameter sets and different limits; the same laboratory method leads to a different decision under the two regimes.

In soil and waste, heavy metals, hydrocarbons, PAH and PCB compounds and LEACHING BEHAVIOUR are determined. The leaching test carries a logic peculiar to this field: it is not the total amount of a pollutant in soil but the fraction that can pass into water that determines the environmental risk. Waste classification and the disposal decision rest largely on this test.

On the emissions side, dust, sulphur dioxide, nitrogen oxides, carbon monoxide, oxygen, moisture and total organic carbon are monitored in flue gas. Measurement is made on site under operating conditions and must represent the plant's actual operating regime; a measurement taken at low load does not show the emissions at full capacity.

Continuous measurement systems are a separate body of work. In large plants emissions are monitored continuously and the accuracy of these systems is verified periodically by comparison with independent measurements; the quality assurance framework governs this.

Noise and vibration measurements complete the environmental impact side of the field: environmental noise mapping, workplace noise exposure and vibration exposure measurements produce evidence for both environmental and occupational health legislation.

Method groups in this field

  • Sampling

    Separate sampling standards for water, waste water, soil, waste, flue gas and ambient air; grab, composite and continuous sampling techniques.

  • Water physico-chemical

    pH, conductivity, turbidity, colour, suspended solids, COD, BOD, TOC, alkalinity, nitrogen and phosphorus species.

  • Elemental analysis

    Determination of heavy metals and trace elements in water, soil and waste by ICP-OES and ICP-MS.

  • Organic pollutants

    Volatile organic compounds, PAH, PCB and organochlorine pesticides by GC-MS; hydrocarbon oil index.

  • Flue gas

    Measurement of dust, SO2, NOx, CO, O2, moisture and total gaseous organic carbon; quality assurance of automated measuring systems.

  • Leaching and waste characterisation

    Leaching tests and waste classification parameters; the basis for the disposal decision.

Commonly confused in this field

  • An analytical result cannot be used on its own without the sampling record; the time, point, conditions and chain of custody are part of the report.
  • Total content and leachable amount give different information; in waste classification, leaching behaviour is what counts.
  • Emission measurement must be made under representative operating conditions of the plant; a result taken at partial load is misleading.
  • Drinking water and waste water limits are defined in different legislation; the same parameter carries a different threshold under the two regimes.
  • A sample from a single point does not represent the whole area; assessment of a contaminated site requires a grid-based sampling plan.

Which decisions these results support

  • Compliance with environmental permits and discharge limits
  • Quality assurance of continuous emission measurement systems
  • Contaminated site assessment and the remediation decision
  • Waste classification and selection of the disposal method
  • Workplace exposure measurements and occupational health obligations

Related Tests

Frequently Asked Questions About Ambient Immission

Our measurement result is high — is our facility responsible?

The measurement alone does not say this. Ambient concentration is the combined effect of all sources. Wind-direction analysis, comparison against a background station, and dispersion modelling are needed to separate source contribution.

Can a short-term measurement be compared against an annual limit value?

Not directly. Annual limit values require long-term data covering seasonal variation. Short campaign measurements can only be compared against limit values with a matching averaging period.

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