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HJ 544-2009Stationary source emission - Determination of sulfuric acid mist - Ion chromatography (English PDF)

固定污染源废气 硫酸雾的测定 离子色谱法(暂行)

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Issued by

Ministry of Environmental Protection Announcement of Ministry of Environmental Protection of the People’s Repu

Level / Type

National · Mandatory

Issue date

December 30, 2009

Implementation date

April 1, 2010

Scope

HJ 544-2009 is the English-translated version of 固定污染源废气 硫酸雾的测定 离子色谱法(暂行).

HJ 544-2009 is the Chinese standard "Stationary source emission - Determination of sulfuric acid mist - Ion chromatography".

Its scope clause reads: This standard specifies the ion chromatography for determining the sulfuric acid mist in stationary source emission This standard applies to the determination of sulfuric acid mist in the stationary source emission.

For the organized emission, when the filter cartridge is used for preparing 250mL sample, the detection limit of this method is 0.12µg/mL; when sample volume is 400L, the detection limit is 0.08mg/m3, the lower limit of determination is 0.3mg/m3, and the upper limit of determination is 500mg/m3.

For the fugitive emission, when the filter membrane is used for preparing 250mL sample, the detection limit of this method is 0.12µg/mL; when sample volume is 3m3, the detection limit is 0.01mg/m3, and the lower limit of determination is 0.04mg/m3.

Its clauses include scope of application; method and principle; precautions. It was issued by the Ministry of Environmental Protection Announcement of Ministry of Environmental Protection of the People’s Repu on 2009-12-30 and took effect on 2010-04-01.

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Document preview — HJ 544-2009

National Standard of the People's Republic of China

Issued by: Ministry of Environmental Protection Announcement of Ministry of Environmental Protection of the People’s Repu

Contents

  • Foreword...5
  • 1 Scope of application...6
  • 2 Normative references...6
  • 3 Method and principle...6
  • 4 Interference and elimination...7
  • 5 Reagents and materials...7
  • 6 Instruments and equipment...7
  • 7 Samples...8
  • 8 Analytical steps...10
  • 9 Result calculations...11
  • 10 Quality assurance and quality control...11
  • 11 Precautions...12

Foreword

This standard is formulated to implement the "Environmental Protection Law of the

People's Republic of China" and "Law of the People's Republic of China on the Prevention

and Control of Atmospheric Pollution"; protect the environment; guarantee human health;

and stipulate the monitoring methods of sulfuric acid mist in exhaust gas of stationary

pollution source.

This standard specifies the ion chromatography for determining the sulfuric acid mist in

stationary source emission.

This standard is organized and formulated by Department of Science, Technology and

Standards of Ministry of Environmental Protection of the People's Republic of China.

Main drafting organization of this standard. Beijing Municipal Environmental Monitoring

Center.

This standard was approved by Ministry of Environmental Protection on December 30,

2009.

The standard shall be implemented on April 1, 2010.

The Ministry of Environmental Protection is responsible for the interpretation of this

standard.

Stationary source emission - Determination of sulfuric

acid mist - Ion chromatography (on trial)

1 Scope of application

This standard specifies the ion chromatography for determining the sulfuric acid mist in

stationary source emission

This standard applies to the determination of sulfuric acid mist in the stationary source

emission.

For the organized emission, when the filter cartridge is used for preparing 250mL sample,

the detection limit of this method is 0.12µg/mL; when sample volume is 400L, the

detection limit is 0.08mg/m3, the lower limit of determination is 0.3mg/m3, and the upper

limit of determination is 500mg/m3.

For the fugitive emission, when the filter membrane is used for preparing 250mL sample,

the detection limit of this method is 0.12µg/mL; when sample volume is 3m3, the detection

limit is 0.01mg/m3, and the lower limit of determination is 0.04mg/m3.

2 Normative references

The articles contained in the following documents have become part of this standard when

they are quoted herein. For the undated documents so quoted, the latest editions shall be

applicable to this standard.

GB/T 16157 The determination of particulates and sampling methods of gaseous

pollutants emitted from exhaust gas of stationary source

HJ/T 55 Technical guidelines for fugitive emission monitoring of air pollutants

HJ/T 373 Technical specifications of quality assurance and quality control for

monitoring of stationary pollution source (on trial)

3 Method and principle

In this method, glass fiber filter cartridge or quartz fiber filter cartridge is used for collecting

particulate matter sample in organized emission; superfine glass fiber filter membrane or

quartz fiber filter membrane is used for collecting particulate matter in fugitive emission.

Use water to extract. After removing the metal cation through pre-treatment column, inject

the sample into ion chromatograph. Determine the nature in accordance with the retention

sampling point inside the exhaust funnel for isokinetic sampling. Appropriately select

sampling time according to the concentration of sulfuric acid mist. Meanwhile, determine

the necessary temperature, pressure and other parameters. After sampling, carefully take

out filter cartridge. Place it into 250mL ground conical flask with stopper. Rinse the

sampling mouth and elbow with a little of distilled water. Collect and combine the cleaning

lotion into the conical flask. Cover up the flask with stopper. Bring it back to laboratory. Dry

the sampling mouth with cotton swab. Dry the elbow with suction bulb for standby. During

each sampling, at least three filter cartridges of samples shall be collected; take their

average value.

7.1.2 Fugitive emission

It shall be implemented in accordance with HJ/T 55 "Technical Guidelines for Fugitive

Emission Monitoring of Air Pollutants". Use the medium-volume particulate matter sampler

equipped with filter membrane to collect particulate matter sample at 100L/min for 30min.

If the concentration of sulfuric acid mist is too low, the sampling time can be extended

appropriately. In order to eliminate the interference of background sulfate from ambient air,

reference point shall be set up at upwind direction of fugitive emission; and ambient

background sample shall be collected at the same time under the same conditions.

Record the sampling conditions.

7.2 Sample preservation

The sample in the filter cartridge is put into the ground conical flask with stopper, after

collection. The filter membrane sample is folded to put into the clean paper bags for

preservation, after collection.

7.3 Sample preparation

Select any one of the following sample preparation methods.

7.3.1 Ultrasonic extraction method

Cut the samples collected in (7.1) (be sure not to shake off dust particles). Place them into

a 250mL ground conical flask with stopper. Add 150mL of deionized water for immersing.

Place the conical flask into ultrasonic cleaner. Take out after 30min. Cool down. Filter the

leaching solution into a 250mL volumetric flask with medium-speed quantitative filter

paper (5.6). Rinse the conical flask and sample residues for (3-4) times, with a little

amount of deionized water. Collect and combine the cleaning lotion into the volumetric

flask. Add 1.0mol/L or 0.10mol/L sodium hydroxide solution to neutralize the solution to pH

7-9.Dilute to marked line with water.

7.3.2 Heating and leaching method

Cut the samples collected in (7.1) (be sure not to shake off dust particles). Place them into

a 250mL ground conical flask with stopper. Add 150mL of water to immerse the samples.

Place a glass funnel on the flask mouth. Place it into electric furnace or on electric hot

11 Precautions

In-series connect 2 striking absorption flasks that contain absorption liquid, at the back of

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This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 12 pages — is available in the English PDF.

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