Measurement engineer fitting a sampling probe in a sampling port on an insulated duct

Emission measurement · Metals

Metals in flue gas according to EN 14385

Measurement of metals in flue gas determines eleven metals that are regulated at waste incineration plants and elsewhere: antimony, arsenic, cadmium, chromium, cobalt, copper, lead, manganese, nickel, thallium and vanadium. The metals occur both in the dust and in the gas phase, so the sample is taken isokinetically on a filter and in absorption solution according to EN 14385 and analysed in a laboratory. The result is reported per metal and as sums, in mg/Nm3 at the plant's reference oxygen content. METLAB, accredited by Swedac (the Swedish accreditation body) according to ISO/IEC 17025, samples throughout Sweden; an accredited laboratory does the analysis, and we build the equipment. Mercury is sampled with a method of its own: see mercury measurement.

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When do you need to measure metals?

  • Permit conditions. The environmental permit sets emission limit values for metals, often for zinc too, and how often they are to be checked.
  • Waste incineration and co-incineration: the Swedish Ordinance on Waste Incineration (SFS 2013:253) has emission limit values for eleven metals and requires at least two measurements a year.
  • The BAT conclusions for waste incineration have lower BAT-associated emission levels (BAT-AELs) and specify measurement according to EN 14385 every six months.
  • Large combustion plants: the BAT conclusions specify measurement once a year for coal, solid biomass fuel, peat and fuel oil, more often when waste is co-incinerated.
  • Metal industry, cement and glass: BAT conclusions with measurement requirements or BAT-AELs exist for non-ferrous metals, foundries, cement kilns and glass furnaces.
  • Performance tests and guarantee checks after new or rebuilt flue gas cleaning.

How the sampling train is built

The measuring principle is isokinetic sampling with wet chemical absorption. The sample gas is drawn out through a nozzle facing the gas stream, at the same velocity as the flue gas, and led through a heated probe tube to a heated plane filter where the particles are caught. What passes the filter is captured in three absorption bottles in a cooling bath, filled with dilute nitric acid and hydrogen peroxide. An empty bottle catches splashes, a drying tower dries the gas, and after the control valve, pump and flow meter a dry gas meter measures the sample volume. A pitot tube, a thermocouple and pressure gauges provide the data for the isokinetic control.

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Isokinetic wet chemical sampling according to EN 14385, with three absorption bottles after the filter.
  1. 1. Nozzle, facing the gas stream
  2. 2. Probe tube, heated
  3. 3. Filter holder with plane filter, heated
  4. 4. Absorption bottles with absorption solution, in a cooling bath
  5. 5. Empty knock-out bottle that catches splashes
  6. 6. Drying tower with silica gel
  7. 7. Control valve
  8. 8. Gas-tight pump
  9. 9. Flow meter
  10. 10. Dry gas meter
  11. 11. Temperature sensor at the gas meter
  12. 12. Temperature sensor, flue gas temperature (type K thermocouple)
  13. 13. Pressure gauge, static pressure in the duct
  14. 14. Pressure gauge, dynamic pressure (micromanometer)
  15. 15. Pitot tube (L- or S-type) for gas velocity
  16. 16. Barometer

Everything the sample gas meets up to the last bottle must be made of borosilicate glass, quartz glass, PTFE or titanium. Titanium, however, can contain some of the metals to be determined. When several parameters are sampled at the same time, only part of the sample gas, a side stream, is led through the bottles.

How is a metals measurement done?

  1. Measurement plan and preliminary measurement

    The measurement site must meet EN 15259, as for dust measurement. Gas velocity, temperature, oxygen and moisture are measured at the measurement points, and the nozzle is chosen for isokinetic sampling.

  2. Clean equipment and field blank

    Everything that meets the sample gas is cleaned beforehand, and the absorption solution is mixed fresh. At the measurement site a field blank is taken: the whole sampling train is assembled and rinsed as after a sample, without drawing flue gas through it.

  3. Isokinetic sampling

    After the leak test (at most 2 % of the sample gas flow), the probe is moved between the measurement points. The flow is adjusted at least every five minutes so that the deviation from isokinetic sampling stays within −5 to +15 %. The probe and filter are kept at least 20 °C above the temperature and the dew point of the flue gas.

  4. Rinsing

    The nozzle, probe and filter holder are rinsed with dilute nitric acid, and the tube to the first bottle is rinsed into it. The filter, the rinse solution and the absorption solution are handled separately.

  5. Analysis

    An accredited laboratory digests the filter in acid under pressure and analyses all the solutions by ICP-MS, ICP-OES or atomic absorption.

  6. Calculation and report

    For each metal, the amounts on the filter, in the rinse solution and in the bottles are added up and divided by the volume of dry sample gas, which gives mg/Nm3 (dry gas at 0 °C and 101.3 kPa). The concentrations are converted to the reference oxygen content and reported per metal and as sums, with their measurement uncertainty.

The requirements in EN 14385

These requirements decide whether a metals sampling is valid. They are essentially the same in the 2004 and 2024 editions of the standard.

RequirementValue
Deviation from isokinetic sampling −5 to +15 %, according to EN 13284-1
Materials in contact with the sample gas Borosilicate glass, quartz glass, PTFE or titanium, from the nozzle to the last bottle
Probe and filter At least 20 °C above the temperature and the dew point of the flue gas
Filter Plane filters from the same batch, with a low and even metal content
Absorption bottles At least three in series, with less than 1 m of line from the probe
Absorption efficiency At most 10 % of a metal's total amount in the last bottle
Leak rate At most 2 % of the sample gas flow, before each sample
Field blank At most 10 % of the emission limit value. Not subtracted from the measured value; lower measured values are reported as ≤ the field blank

Which metals are included?

EN 14385 is validated for eleven metals, which the regulations split into two sums. Mercury has a standard of its own. Other metals are sampled in the same way, but the standard is not validated for them and we report them without accreditation.

MetalsIn EN 14385In the regulations
Cadmium (Cd) and thallium (Tl) YesThe sum Cd + Tl
Antimony (Sb), arsenic (As), lead (Pb), chromium (Cr), cobalt (Co), copper (Cu), manganese (Mn), nickel (Ni) and vanadium (V) YesThe sum of the nine
Selenium (Se), zinc (Zn) and tin (Sn) NoSelenium and zinc are in the measurement requirements for large combustion plants, selenium and tin in the glass industry's sums
Mercury (Hg) No, EN 13211Emission limit value of its own

Particle-bound and gaseous

Metals occur in the flue gas in and on particles, dissolved in droplets and as gas. The filter catches the particles and the absorption solution what passes it: gas, but also very fine dust. The standard's field trials showed that most metals cannot be determined quantitatively in the gas phase on its own, so the result is always the total concentration.

Because the particles carry metals, the sample is taken isokinetically and at several measurement points, as in dust measurement; otherwise the share of heavy particles is wrong.

At low concentrations, cleanliness decides the result. The BAT conclusions' upper value for cadmium and thallium at waste incineration plants is 0.02 mg/Nm3, and the field blank may be at most a tenth of that: 2 millionths of a gram per cubic metre, for the filter, rinse solution and bottles together. Measured values below the field blank are reported as at most equal to it, so in practice the field blank sets the detection limit. Bottles and tubing from mercury sampling must therefore not be used for metals: the permanganate solution leaves manganese behind.

Which emission limit values apply to metals?

The emission limit value is set in the permit, in the Swedish Ordinance on Waste Incineration (SFS 2013:253) or in the sector's BAT conclusions, whose upper value applies as a limit value four years after publication. The values refer to sums of metals, in solid form and in the gas phase.

PlantEmission limit value or BAT-AELRule
Waste incineration (11 % O2) Cd + Tl: 0.05 mg/Nm3. Sb + As + Pb + Cr + Co + Cu + Mn + Ni + V: 0.5 mg/Nm3SFS 2013:253, section 64
Co-incineration: combustion plant (6 % O2, solid fuel) and cement kiln (10 % O2) 0.05 and 0.5 mg/Nm3SFS 2013:253, sections 69 and 95
Waste incineration, BAT-AEL Cd + Tl: 0.005–0.02 mg/Nm3. The nine metals: 0.01–0.3 mg/Nm3BAT 25, (EU) 2019/2010
Large combustion plant co-incinerating waste with coal The nine: 0.005–0.5 mg/Nm3 below 300 MW, 0.005–0.2 from 300 MW (average of the year's samples). Cd + Tl: 5–12 and 5–6 µg/Nm3 respectivelyBAT 68, (EU) 2021/2326
Large combustion plant co-incinerating waste with biomass or peat The nine: 0.075–0.3 mg/Nm3. Cd + Tl: < 5 µg/Nm3 (average of the year's samples)BAT 69, (EU) 2021/2326
Cement kiln Cd + Tl: < 0.05 mg/Nm3. The nine: < 0.5 mg/Nm3BAT 28, 2013/163/EU
Container glass melting furnace As + Co + Ni + Cd + Se + Cr(VI): < 0.2–1 mg/Nm3. Together with Sb, Pb, Cr(III), Cu, Mn, V and Sn: < 1–5 mg/Nm3BAT 21, 2012/134/EU

What does a metals measurement cost?

The price depends on the number of stacks or ducts and operating conditions and on the number of samples. The laboratory analysis is a large part of it: each sample gives the laboratory several portions to analyse separately (the filter, the rinse solution, the first two bottles and the third on its own), and the field blank is analysed in the same way. More metals than the standard's eleven increase the analysis cost. When mercury, dust or dioxins are measured during the same visit, travel and set-up are shared. Request a quote and we will reply within two working days. Approximate prices for the most common measurements are in the price guide.

How often must metals be measured?

As often as the permit says. For waste incineration and co-incineration, the Swedish Ordinance on Waste Incineration (SFS 2013:253) requires at least two measurements a year, and one every three months during the first twelve months of operation. The BAT conclusions specify every six months for waste incineration and once a year for large combustion plants, but every six months when waste is co-incinerated and every three months from 300 MW. The non-ferrous metals industry and foundries measure once a year.

Measure metals yourself

Frequently asked questions about metals measurement

Is the metals measurement accredited?

Yes, the sampling. METLAB's Swedac accreditation covers the sampling of metals according to EN 14385, and the analysis is done by an accredited laboratory. Metals beyond the standard's eleven are reported without accreditation.

How long does a metals measurement take?

A sample lasts between 30 minutes and 8 hours. Energiforsk's Emissionsmäthandbok (the Swedish emission measurement handbook) recommends at least one hour, and the BAT conclusions' values refer to the average of three consecutive samples. Add to that the set-up, the preliminary measurement, the field blank and the rinsing.

Can metals be measured at the same time as mercury and HCl?

Yes. From the same probe and filter, the sample gas is split into side streams, each with its own absorption solution: one for metals, one for mercury and more where needed, for example for HCl. The filter and the side streams for metals and mercury must have the same sampling time.

What is required of the measurement site?

The same as for dust measurement: sampling ports on a straight run of duct, normally 3-inch threaded sockets, and a safe working platform with room for the probe, bottle rack and cooling bath. Also electricity for the probe heating and the pump.

How are values below the detection limit counted in the sum?

According to the 2024 edition of EN 14385, a portion of the sample below the laboratory's limit of quantification counts as half the limit when the metals are added up. With many small portions the sum can therefore be higher than the real emission, one reason to take a large enough sample volume.

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