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Technical specification of performance testing for faclities of hazardous waste (including medical waste) incineration
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HJ 561-2010
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| Standard ID | HJ 561-2010 (HJ561-2010) | | Description (Translated English) | Technical specification of performance testing for faclities of hazardous waste (including medical waste) incineration | | Sector / Industry | Environmental Protection Industry Standard | | Classification of Chinese Standard | Z70 | | Classification of International Standard | 13.030.40 | | Word Count Estimation | 14,169 | | Date of Issue | 2010-02-22 | | Date of Implementation | 2010-06-01 | | Quoted Standard | GB 5085.3; GB 18484; GB/T 212; GB/T 213; GB/T 384; GB/T 11133; GB/T 16157; GB/T 17040; HJ/T 298; HJ/T 365 | | Summary | This standard specifies the requirements silica microspheres, test methods, inspection rules and signs, labeling, packaging, transportation and storage. This standard applies to sulfuric acid and sodium sulfate as raw materials obtained silica microspheres. Silica microspheres mainly used as catalyst carrier and catalyst. |
HJ 561-2010
Technical specification of performance testing for faclities of hazardous waste (including medical waste) incineration
People's Republic of China National Environmental Protection Standards
Issued on.2010-02-22
2010-06-01 implementation
Issued by the Ministry of Environmental Protection
People's Republic of China Ministry of Environmental Protection
announcement
2010, No. 24
For the implementation of the "People's Republic of China Environmental Protection Law", "People's Republic of China Solid Waste Pollution Prevention Law" to regulate dangerous
Risk waste (including medical waste) incineration facilities conduct performance testing, now approved a "hazardous waste (including medical waste) incineration facilities
Performance Test Specification "for the national environmental protection standards and to publish.
Standard name, numbered as follows.
The standard since June 1, 2010 implementation, published by the China Environmental Science Press, standard content in website of the Ministry of Environmental Protection
Special announcement.
February 22, 2010
Table of Contents
Preface ..iv
1. Scope ..1
2 Normative references ..1
3 Terms and Definitions .1
4 Performance Test content ..2
5 performance testing program .. 3
6 performance test technical requirements 3
Preparation 7 8 performance test report
Performance testing to ensure quality 8 9
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 ℃ (± 25 ℃) 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)
ρ ρ = ×
Where. CE-- combustion efficiency,%;
ρ (CO2) and ρ (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
WW
- = ×
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
Content 4 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, 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.
5.1
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
ρ G = × × -
Where. G - POHCs minimum amount, g;
Mass concentration (standard state), g/m3; ρ-- 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 Gρ η '= × × × × -
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 η-- design flue gas purification facilities
Q-- flue gas purification facility in the maximum amount of flue gas outlet measurements (superscript
ρ-- 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 Gρ η '= × × - -
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.
6.1.
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
ρ-- design of heavy metals in flue gas emissions
Heavy metal removal η-- 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 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
MQ
η × -
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
ρ = × ×
Hydrogen chloride gas cleaning facility design η-- removal
Q-- flue gas purification facility in the maximum amount of flue gas outlet measurements (superscript
ρ-- 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.
(1 )
MQ
η = × -
Where. M-- waste mercury levels, g/kg;
Heavy metal removal η-- design flue gas purification facility,%;
The maximum amount of flue gas (standard state), m3/h;
m3;
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 ℃) 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
Ρ-- 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 ℃) 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, 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 ℃ 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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