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HJ 561-2010Technical specification of performance testing for faclities of hazardous waste (including medical waste) incineration (English PDF)

危险废物(含医疗废物)焚烧处置设施性能测试技术规范

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Issued by

Ministry of Ecology and Environment

Level / Type

National · Mandatory

Issue date

February 22, 2010

Implementation date

June 1, 2010

Scope

HJ 561-2010 is the English-translated version of 危险废物(含医疗废物)焚烧处置设施性能测试技术规范.

HJ 561-2010 — This standard specifies the test content of hazardous waste (including medical waste) incineration facilities involved in the performance tests, procedures and technical requirements.

This standard applies to hazardous waste (including medical waste) performance test incineration facilities. This standard does not apply to cement kilns co-disposal of hazardous waste performance testing facilities.

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Document preview — HJ 561-2010

National Standard of the People's Republic of China

ICS
13.030.40
Classification
Z 70

Issued by: Ministry of Ecology and Environment

Contents

  • Preface
  • 1. Scope
  • 2 Normative references
  • 3 Terms and Definitions .1
  • 4 Performance Test content
  • 5 Performance testing program
  • 6 Performance test technical requirements

Foreword

For the implementation of the "People's Republic of China Environmental Protection Law", "People's Republic of China Solid Waste Pollution Prevention Law" and other laws Regulation, with the implementation of GB 18484, regulate conduct performance tests incineration facilities, the development of this standard.

This standard specifies the test content of hazardous waste (including medical waste) incineration facilities involved in the performance tests, procedures and technology to begging.

This standard is developed by the Ministry of Environmental Protection Science, Technology organization.

Drafting of this standard. Shenyang Academy of Environmental Sciences, Institute of High Energy Physics, the Department of Environmental Protection for Cooperation Outside the center, the State Environmental Protection Engineering Technology Center hazardous waste disposal.

This standard MEP February 22, 2010 for approval.

This standard since June 1, 2010 came into effect.

The standard explanation by the Ministry of Environmental Protection.

Hazardous waste incineration facilities Performance Test Specification (including medical waste)

1 Scope

This standard specifies the test content of hazardous waste (including medical waste) incineration facilities involved in the performance tests, procedures and technical requirements.

This standard applies to hazardous waste (including medical waste) performance test incineration facilities.

This standard does not apply to cement kilns co-disposal of hazardous waste performance testing facilities.

2 Normative references

The standard content of the following documents cited in the articles. For undated references, the effective version applies to this standard.

GB 5085.3 identification of hazardous waste leaching toxic identification standard GB 18484 Hazardous Waste Incineration Pollution Control Standard Analysis Method GB/T 212 coal Heat GB/T 213 Determination of coal GB/T 384 Petroleum products - Determination of calorific value GB/T 11133 Liquid petroleum products - Determination of water (Karl Fischer method) GB/T 16157 Stationary source emission-Determination of particulates and gaseous pollutants sampling methods GB/T 17040 Petroleum and petroleum products Determination of sulfur content - Energy Dispersive X-ray Fluorescence Spectrometry HJ/T 298 Identification of Hazardous Waste Technical Specifications HJ/T 365 hazardous waste (including medical waste) incineration facilities dioxin emissions monitoring technical specifications evil

3 Terms and Definitions

The following terms and definitions apply to this standard.

3.1 Hazardous Waste

Means included in the national list of hazardous waste or hazardous waste determination based on identification of standards and methods prescribed by the State having hazardous characteristics Waste.

3.2 Medical Waste

It refers to the medical and health institutions in the medical, prevention, health care and other related activities have generated directly or indirectly infectivity, toxicity to and other hazardous wastes.

3.3 Incineration Disposal Facilities

Means dedicated to the incineration of hazardous waste (including medical waste) of complete sets of equipment (including exhaust purification facilities).

3.4 Performance Test

It refers to the testing and evaluation of hazardous waste incineration facility performance behavior.

3.5 Hot burning rate reduction

It means the incineration residues by burning the reduced quality of the original mass percentage of incineration residues. It is calculated as follows.

100% A BP

Where. P-- rate of heat loss on ignition,%;

After drying A-- original mass incineration residues at room temperature, g;

After cooling B-- incineration residues by 600 °C (± 25 °C) 3 h burning quality to room temperature, g.

3.6 Gas residence time

It refers to the smoke generated by the combustion or secondary combustion chamber between the outlet from the last high-temperature combustion zone of the combustion air injection port or outlet to the burner the residence time.

3.7 Temperature incineration

It refers to a temperature incinerator chamber outlet center.

3.8 Combustion efficiency

It refers to the concentration of carbon dioxide and carbon monoxide and carbon dioxide concentrations and mass percentage in the flue gas. Table using the following formula it shows.

(CO) CE 100%

(CO) (CO)

rho rho = ×

Where. CE-- combustion efficiency,%;

rho (CO2) and rho (CO) - were burned exhaust gas mass concentration of CO2 and CO, mg/m3.

3.9 DRE

Refers to an organic substance by incineration percentage reduction. By the following formula.

0DRE 100% i

Where. DRE-- DRE,%;

Weight, g;

Weight, g.

3.10

Incineration facility performance test content, in accordance with the requirements and performance test burning test configuration (including medical waste) Yakimono

4 Content, performance test

Hazardous waste (including waste) incineration facilities should use standard test waste incinerator design temperature and design feed rate conditions DRE disposal facility may carry out performance tests.

Indicators, performance indicators, flue gas emissions targets, Including standard calorific value, mainly organic hazardous constituent (Principal Organic and Hazardous Components, Acronym Room rate reduction burning thermal incineration residues, heavy metals 18484 the flue gas pollutant emission targets stipulated.

Parameter; II group parameters Feed rate PO Incineration system comprising at least two combustion chamber exit temperature of the flue gas prior to quench oxygen content flue gas before the flue gas stream quench the amount, Inlet gas temperature, caustic feed rate, the activated carbon Injected Wi-- be incinerated in an organic substance W0-- flue gas emissions with Wi corresponding organic substances Standard Test waste Defined as the completion of hazardous waste material.

4.1 Medical

Under performance testing.

4.2 Medical waste incinerated

Performance Test 4.3 The incineration facility includes four main indicators. waste characteristics Equipment operating parameters.

4.3.1 Refers to waste characteristics

POHCs) content, organic chlorine content, heavy metal content, sulfur content, moisture content and ash.

4.3.2 System performance indicators include POHCs DRE, combustion efficiency, gas residence time

Removal, hydrogen chloride removal and dust removal.

4.3.3 Test smoke emission targets include GB

4.3.4 Test equipment operating parameters including I, II and III three sets of parameters. I set of parameters for the particular waste feed to describe the process parameters burning conditions and the need to continuously monitor; III set of parameters to describe the process parameters flue gas cleaning equipment operation.

(1) continuous operation-type incineration facilities I set of parameters including at least the waste feed rate, feed rate of heavy metals, organic chlorine into HCs feed rate. Intermittent incineration facilities in group I parameters include at least waste dosage, plus heavy metals, organic chlorine dosage, POHCs dosage.

(2) II group parameters Flue gas purification facilities and incinerators outlet gas flow inlet at minimum negative.

(3) III set of parameters comprises at least quench tower outlet temperature, flue gas purification facilities into Speed, bag filter differential pressure.

5 Performance test procedures

Performance testing program includes preparation, planning, performance testing, reporting four stages.

And the division of responsibilities, to carry out the appropriate technical training.

To achieve the desired operational requirements.

Road.

Technical parameters or stage Plan should include performance testing purposes, the content of the performance test, performance test conditions, test methods and performance of Institutions and monitoring bodies. Performance test facility should have the appropriate technical conditions and technological capacity, monitoring bodies should when requested to waste characteristic index, system performance, flue gas emission targets, operating parameters, respectively Performance testing agencies 4.3.2 gas residence time and test 4.3.4 I, II, III three sets of performance parameters, there are bars Slag hot burning rate reduction, removal of heavy metals, hydrogen chloride and test data.

Technical requirements Standard Test test waste disposal facility Design requirements.

The substrate can be used as liquid waste Waste mineral Other One kind the preparatory stage

5.1.1 Implementation of staff positions

5.1.2 the development of safety systems, job procedures, emergency plans.

5.1.3 A cold hot commissioning and trial run without load to ensure that each device can 5.1.4 to determine the type of material and the source of the required performance tests required for waste and waste standard test configuration.

5.1.5 clear performance test required auxiliary fuel, raw materials (such as activated carbon, calcium) and the type of procurement canal 5.1.6 incineration facility design, installation units and equipment suppliers work begins before the performance test shall provide the necessary Technical description.

5.2 Planning

5.2.1 Performance Test preparation

You can test schedule.

5.2.2 The implementation of the performance test with the national metrology certification or laboratory accreditation.

5.3 Performance testing phase

5.3.1 In the case of incineration and other tests.

5.3.2 Delegate

Incineration facility operating unit member may also be self-testing under the guidance of performance testing agencies.

5.3.3 Commissioned monitoring agencies 4.3.2 DRE, combustion efficiency, incineration residues

Removal, dust removal and flue gas emission monitoring indicators specified in 4.3.3.

5.4 Report preparation phase

5.4.1 Summary operating data

5.4.2 write performance test report.

6 Performance Test

Configuration 6.1 Standard testing of waste 6.1.1 for hazardous waste incinerated (1) After the standard test configuration should meet the calorific value of waste incineration facilities (2) should be selected ingredients stable, readily available, low environmental risks of waste as a standard test waste Oil, solid waste can be used for municipal wastewater treatment plant sludge, sawdust, contaminated food, plastics and other expired. You can also choose not to have Corrosive hazardous waste, acute toxicity, flammability, reactivity as a substrate, it should be reported to the competent administrative department of environmental protection.

(3) adding at least two kinds of good thermal stability, low toxicity and analytical test methods mature POHCs, wherein at least one of naphthalene, You can use carbon tetrachloride, polyvinyl chloride, perchlorethylene, etc., for the determination of DRE. If the hazardous waste incineration facility for POHCs selection have special requirements, you can select specific ingredients, but should be reported to the competent administrative department of environmental protection. POHCs most A small amount can be calculated with reference to the following formula.

QG t

rho G = × × -

Where. G - POHCs minimum amount, g;

Mass concentration (standard state), g/m3; rho-- meet the required minimum flue gas monitoring POHCs Q-- flue gas purification facility in the maximum amount of flue gas outlet measurements (standard state), m3/h;

D-- DRE (hazardous waste and medical waste 99.99% 99.999 PCB waste 9%);

POHCs content, g.

(4 to accommodate the waste content of organic chlorine, hydrogen chloride is removed for measuring rate.

t-- waste incineration time, h;

G0-- corresponding original waste ) By the addition of carbon tetrachloride, perchlorethylene, or polyvinyl chloride, etc.

Amount of organic chlorine can refer to the following formula.

35.5 36.5

GQ t Grho eta '= × × × × -where. G-- amount of organic chlorine, g;

Hydrogen removal rate,%;

State), m3/h;

Content, g.

Finally, calculate the amount of carbon tetrachloride, perchlorethylene, or polyvinyl chloride and other organic matter by adding the amount of organic chlorine.

(Genus content (play Onset Chlorinated eta-- design flue gas purification facilities Q-- flue gas purification facility in the maximum amount of flue gas outlet measurements (superscript rho-- design flue gas emission concentration of hydrogen chloride (standard state), g/m3;

t-- waste incineration time, h;

G '- Central Plains and some organochlorine waste

5) should be added at least volatile and semi-volatile, non-volatile compounds of three different types of heavy metal waste lots of money to deploy Alternatively heavy metal mercury or cadmium oxide, semi-volatile heavy metals selectively lead or zinc oxide, optional non-volatile heavy metals copper Oxide), for the determination of heavy metals removal. The amount of heavy metals can be added with reference to the following formula.

QG t Grho eta '= × × - -where. G-- added in an amount of heavy metals, g;

Concentration (standard state), g/m3;

State), m3/h;

Content, g.

Finally, calculate the amount of mercury, lead and copper oxides by adding the amount of heavy metals.

Treatment of waste mixed configuration. You can also follow local medical waste Plastic the need, if the content is not enough, by the addition of polyvinyl chloride to adjust rho-- design of heavy metals in flue gas emissions Heavy metal removal eta-- design flue gas purification facility,%;

Q-- flue gas purification facility in the maximum amount of flue gas outlet measurements (superscript t-- waste incineration time, h;

G '- heavy metal waste any original 2 standard test for medical waste incineration waste disposal facility testing (1) can collect various doctors medical waste temporary storage facility by uniformly Component content material, glass, metal, cloth, paper, wood, etc., calorific value, moisture content, ash content, chlorine content, heavy metal content, Sulfur content and other physical and chemical properties of indicators, configured through similar substances.

(2) waste organic chlorine content should be suitable for the determination of hydrogen chloride removal Hotels. Waste organic chlorine content can refer to the following formula.

135.

(1) 36.5

eta × -

Where. M-- waste organic chlorine content, g/kg;

rate,%;

State), m3/h;

(3 Determination of heavy metal removal needs, if the content is not enough, by the addition of mercury Compound rho = × × Hydrogen chloride gas cleaning facility design eta-- removal Q-- flue gas purification facility in the maximum amount of flue gas outlet measurements (superscript rho-- design flue gas emission concentration of hydrogen chloride (standard state), g/m3;

A-- waste incineration capacity, kg/h.

) Content of the heavy metals mercury wastes should meet to deploy. Waste mercury content can refer to the following formula.

eta = × -

Where. M-- waste mercury levels, g/kg;

Heavy metal removal eta-- design flue gas purification facility,%;

The maximum amount of flue gas (standard state), m3/h;

6.1.3 Hazardous waste incineration plant subsidiary of disposal facilities), and whose scale

Benchmarking of waste to be collected by uniformly mixing the proposed disposal of waste to configure, but should also be in accordance with 6.1.1 (3), (4), (5) requirements Claim Maintained within the design temperature (± 50 °C) range, the temperature should be designed according to the design value incineration facilities Before the test uptime of not less than 4 h, completed three conventional sampling test running time should not less than Q-- in the flue gas purification facilities measuring outlet rho-- design concentration of mercury in flue gas emissions (standard state), g /A-- waste incineration capacity, kg/h.

Relatively simple processed hazardous waste incineration facilities (such as a specific work Join POHCs, organochlorines and heavy metals.

6.2 Test operating conditions Technical Requirements

6.2.1 Technical hazardous waste incineration disposal facilities

(1) Reformer, Sec Furnace and non-heat-load test is determined.

(2) continuous operation-type incineration facility in accordance with the design of the feed rate, configured into standard waste incineration test run. stable Given running time of not less than 13 h, which 3 h, completed three dioxins sampling test running time should be not less than 6 h.

(3) intermittent incineration facility in accordance with the design of the feeding amount invested configured standard waste incineration test run. Trial burn period not less than two cycles, each cycle uptime of not less than 7 h, of which the first test uptime of not less than 1 h, the completion of the second regular Running time sampling test gauge shall be not less than 2 h, complete 2 dioxins sampling test running time should be not less than 4 h.

Technical Requirements 6.2.2 Incineration of medical waste disposal facilities (1) Reformer, Sec Furnace maintained within the design temperature (± 50 °C) range, design temperature incineration facility should be based on the design value 6.3 and points in Table 1.

Content and performance test points list no. Category Code test monitoring project unit test/sampling point and non-heat-load test is determined.

(2) continuous operation-type incineration facility in accordance with the design feed rate into medical waste incineration operation. According to 6.2.1 (2) the requirements for running the test.

(3) intermittent incineration facility in accordance with the design of the feeding amount invested medical waste incineration operation. According to 6.2.1 (2) to Demand test run.

Technical requirements for testing and monitoring

6.3.1 Performance test content

Table 1

Waste Characteristics (A) Aa waste storage container calorific value J/kg Ab POHCs content g/kg waste storage container inlet Ac organic chlorine content g/kg waste storage container inlet Ad heavy metal content g/kg waste storage container inlet Ae sulfur content in g/kg of waste storage containers Af% moisture content of the waste storage container Ag ash g/kg of waste storage containers Performance Gas residence time s (B) Before Ba flue gas quenching Before Bb heavy metal removal% flue gas quench, flue gas purification facilities export Before Bc HCl removal% flue gas quench, flue gas purification facilities export Bd PO HCs DRE% export flue gas purification facilities be the flue gas before combustion efficiency quenched% Before Bf dust removal% flue gas quench, flue gas purification facilities export Bg incineration residues burning heat reduction rate% incineration ash system at CONTINUED no. Category Item Unit test code to test monitoring/sampling point Flue gas discharge means Standard (C) Ringelman blackness, level smoke Ca outlet gas purification facilities Cb dust mg/m3 flue gas purification facilities export Cc a flue gas purification facilities export the carbon dioxide (CO) mg/m3 Cd dioxide 2) sulfur (SO mg/m3 flue gas purification facilities export Ce fluoride F) hydrogen (H mg/m3 flue gas purification facilities export Cf hydrogen chloride (HCl) mg/m3 flue gas purification facilities export Cg nitrogen oxides (as NO2) mg/m3 flue gas purification facilities export Ch mercury and its meter) compound (in Hg mg/m3 flue gas purification facilities export Ci and Cd meter) compound (in Cd mg/m3 flue gas purification facilities export Cj arsenic, nickel meter) and its compounds (in As Ni mg/m3 flue gas purification facilities export Ck Lead and its compounds (Pb) mg/m3 flue gas purification facilities export Cl Chromium, tin, antimony, copper, manganese and its compounds (In Cr Sn Sb Cu Mn meter) mg/m 3 exit flue gas purification facilities Cm dioxins class (in TEQ meter) ng/m3 flue gas purification facilities export Da incineration system secondary combustion chamber at the outlet temperature °C secondary combustion chamber outlet Db kg/h (kg/time) inlet waste feed rate (dosage) Dc heavy metal feed rate (dosage) kg/h) (kg/second inlet Dd organic chlorine feed rate (dosage) kg/h (times) kg/inlet De P OHCs feed rate (dosage) kg/h (kg/time) inlet Df flue gas oxygen content before quenching% Equipment operating parameters Number of (D) Before the flue gas quenching Before the flue gas before Dg quenching gas flow m3/h flue gas quenching Dh flue gas purification facilit...

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