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Basic dataStandard ID: HJ 2037-2013 (HJ2037-2013)Description (Translated English): Technical specifications for centralized incineration disposal engineering on PCBs waste Sector / Industry: Environmental Protection Industry Standard Classification of Chinese Standard: Z70 Classification of International Standard: 13.030.40 Word Count Estimation: 19,115 Quoted Standard: GB 151; GB/T 7190.1; GB/T 7190.2; GB 8978; GB 12348; GB/T 12801; GB 13015; GB 15562.2; GB 18452; GB 18484; GB 18597; GB/T 28001; GB 50736; GB 50028; GB 50034; GB 50057; GB/T 50062; GB 50156; GB 50431; GB 50205; GB 50014; GB 50016; GBJ 22; GB 50140; GB/T 1 Regulation (derived from): Department of Environmental Protection Notice No. 60 of 2013 Issuing agency(ies): Ministry of Ecology and Environment Summary: This standard specifies the incineration project design, construction, commissioning and operation and management of the technical requirements of the process waste containing PCBs. This standard applies specifically for the disposal of PCB-containing was HJ 2037-2013: Technical specifications for centralized incineration disposal engineering on PCBs waste---This is a DRAFT version for illustration, not a final translation. Full copy of true-PDF in English version (including equations, symbols, images, flow-chart, tables, and figures etc.) will be manually/carefully translated upon your order. Technical specifications for centralized incineration disposal engineering on PCBs waste Technical specification for polychlorinated biphenyl waste incineration disposal engineering Technical specifications for centralized incineration disposal Engineering on PCBs waste Ministry of Environmental Protection National Environmental Protection Standard of the People's Republic Published on.2013-09-26 2013-12-1 Implementation release Content1 Scope..1 2 Normative references 1 3 Terms and definitions. 2 4 Contaminants and pollution loads.4 5 General requirements..4 6 PCBs waste incineration disposal engineering process design..5 7 Main process equipment and materials..9 8 Detection and Process Control..11 9 Auxiliary Engineering Design.12 10 Labor Safety and Occupational Health 13 11 Construction and acceptance..14 12 Operation and maintenance..15 To implement the Law of the People's Republic of China on the Prevention and Control of Environmental Pollution by Solid Wastes, to regulate the design of waste treatment facilities containing polychlorinated biphenyls. Construction and operation management to prevent environmental pollution caused by incineration of PCB-containing wastes, protect the environment, and protect human health. standard. This standard specifies the relevant technologies in the process of design, construction, acceptance and operation management of polychlorinated biphenyl waste incineration disposal projects. Claim. This standard is a guidance document. This standard is the first release. This standard was formulated by the Science and Technology Standards Department of the Ministry of Environmental Protection. This standard was drafted. Shenyang Environmental Science Research Institute (National Environmental Protection Hazardous Waste Disposal Engineering Technology (Shenyang) Center). This standard was approved by the Ministry of Environmental Protection on September 26,.2013. This standard has been implemented since December 1,.2013. This standard is explained by the Ministry of Environmental Protection.ForewordTechnical specification for polychlorinated biphenyl waste incineration disposal engineering1 Scope of applicationThis standard specifies the technical requirements for the design, construction, acceptance and operation management of polychlorinated biphenyl waste incineration disposal projects. begging. This standard applies to the construction and operation of waste incineration disposal projects containing polychlorinated biphenyls.2 Normative referencesThe contents of this standard refer to the terms in the following documents. For undated references, the valid version applies to This standard. GB 151 shell and tube heat exchanger GB 5085.1-7 Hazardous Waste Identification Standard GB 7190 glass fiber reinforced plastic cooling tower GB 8978 Integrated Wastewater Discharge Standard GB 12348 Environmental noise emission standards for industrial enterprises General rules for safety and health requirements of GB 12801 production process GB 13015 Contains PCB pollution control standards GB 15562.2 Environmental Protection Graphic Mark - Solid Waste Storage (Disposal) Site GB 18452 crushing equipment safety requirements GB 18484 Hazardous Waste Incineration Pollution Control Standard GB 18597 Hazardous Waste Storage Pollution Control Standard GB/T 28001 Occupational Health and Safety Management System Requirements GB 50019 Heating, Ventilation and Air Conditioning Design Code GB 50028 town gas design code GB 50034 Architectural Lighting Design Code GB 50057 building lightning protection specification GB 50062 Specification for relay protection and automatic devices for electrical installations GB 50156 Refueling and gas station design and construction specification GB 50431 belt conveyor engineering design specification GB 502221 Steel Structure Engineering Quality Assessment Standard GB J14 Outdoor Drainage Design Code GB J16 Building Design Fire Code GB J22 factory mine road design specification GB J87 industrial enterprise noise control design specification GB J140 building fire extinguisher configuration design specification GB/T.19923 Urban sewage recycling industrial water quality GBZ 1 industrial enterprise design hygiene standard GBZ 2.1 Workplace harmful factors Occupational exposure limits Chemical harmful factors GBZ 2.2 Workplace harmful factors occupational exposure limit physical factors HJ/T 20 Technical Specifications for Sampling and Sample Preparation of Industrial Solid Waste HJ/T 176 Technical Specifications for Construction of Hazardous Waste Centralized Incineration Disposal Project HJ/T 324 Environmental Protection Products Technical Requirements Bag Filters HJ/T 324 environmental protection product technical requirements bag filter bag HJ/T 365 Hazardous Waste (including Medical Waste) Incineration and Disposal Facilities Dioxin Emission Monitoring Technical Specifications HJ 561-2010 Technical Specifications for Performance Testing of Hazardous Waste (including Medical Waste) Incineration Disposal Facilities HJ 2020-2012 General technical specifications for bag dust removal engineering HG/T 20566 rotary kiln design regulations Technical requirements for JB/T 1388 compound pendulum jaw crusher JB/T 8690 industrial fan noise limit Measures for the Management of Pollution Sources Monitoring (Huanfa [1999] No. 246) Measures for the Administration of Hazardous Waste Transfer Joint Orders (Order No. 5 of the State Environmental Protection Administration) Guidelines for Preparing Emergency Plans for Hazardous Waste Business Units (State Environmental Protection Administration Announcement [2007] No. 48)3 Terms and definitionsThe following terms and definitions apply to this standard. 3.1 Polychlorinated biphenyls for waste Refers to polychlorinated biphenyls (PCBs) containing wastes listed in the National Hazardous Wastes List. 3.2 Incineration incineration Refers to the process of burning and burning PCBs waste at high temperature to decompose and harm. 3.3 Incinerator incinerator Refers to the main unit that incinerates waste containing PCBs, which is a pyrolysis gasification incinerator consisting of a rotary kiln and a secondary combustion chamber. 3.4 Incineration amount Refers to the weight of waste containing PCBs incinerators per unit time. 3.5 Incineration residues Refers to the combustion residue discharged after the burning of PCBs-containing waste, the fly ash generated by the exhaust gas purification device, and other solid and semi-solid State substance. 3.6 Deconstruction removal rate (DRE) Refers to the difference between the quality of the PCBs in the incinerated waste and the quality of the PCBs remaining in the emitted flue gas, accounting for the incineration The percentage of PCBs quality. The expression for DRE is as follows. DRE=(Wi-Wo)/Wi ×100% (1) In the formula. Wi- is the mass of PCBs burned in unit time, kg/h; Wo- is the mass of PCBs in the flue gas discharged per unit time, kg/h. 3.7 thermal burn rate loss of ignition Refers to the percentage of the mass of the incineration residue that has been reduced by the burning of the incineration residue. Its calculation formula is as follows. P= (AB)/A ×100% (2) In the formula. P-thermal burning rate, %; A-quality of the original incineration residue after drying at room temperature, g; B-Incineration residue is heated to 600 ° C (± 25 ° C) for 3 h, then cooled to room temperature, g. 3.8 smoke retention time Refers to the residence time between the flue gas generated by combustion from the last burner exit to the flue cooling spray port. [GB 18484] 3.9 Incinerator temperature incinerator temperature Refers to the temperature at the exit center of the incinerator combustion chamber. [GB 18484] 3.10 Combustion efficiency (CE) Refers to the percentage of the concentration of carbon dioxide in the exhaust gas of the flue and the concentration of carbon dioxide and carbon monoxide, expressed as CE. Its calculation formula is. CE=[CO2]/([CO2] [CO]) ×100% (3) In the formula. [CO2] and [CO]- are the concentrations of CO2 and CO in the exhaust after combustion, respectively. [GB 18484] 3.11 Dioxins dioxins Refers to the general term for polychlorinated dibenzo-p-dioxin and polychlorinated dibenzofurans [GB 18484]. 3.12 dioxin toxicity equivalent (TEQ) toxic equivalent Refers to the ratio of the dioxin-toxic congener to the affinity of 2,3,7,8-tetrachlorodibenzo-p-dioxin to the Ah receptor. TEQ indicates that its calculation formula is. TEQ=∑ (dioxin toxicity congener concentration × TEF) (4) In the formula. TEF (Toxicity Equivalency Factor) - dioxin toxicity equivalent factor. [GB 18484]4 Contaminants and pollution loads4.1 Wastes containing PCBs are mainly capacitors, transformers, liquids and PCBs contaminated with PCBs, concrete Structures and other items contaminated with PCBs. 4.2 The content of chlorine in the incineration waste should be controlled within 20%.5 General requirements5.1 General provisions 5.1.1 Incineration disposal of wastes containing PCBs shall be carried out in accordance with GB 13015. 5.1.2 Containing PCBs Waste incineration disposal project air pollution control should meet the requirements of GB 18597. 5.1.3 Process waste water containing PCBs waste incineration disposal project can be recycled after treatment or by flashing Reason. 5.1.4 Solid waste newly generated in the operation of waste incineration disposal project including PCBs is hazardous waste. 5.1.5 Boundary noise of waste incineration disposal project with PCBs shall comply with the requirements of GB 12348. 5.1.6 Wastewater incineration disposal project with PCBs should be equipped with an online monitoring system for flue gas, and the monitoring indicators should meet the relevant HJ/T 167 Claim. 5.2 Engineering composition 5.2.1 PCB-containing waste incineration disposal project consists of main works and auxiliary works. 5.2.2 Main works of waste incineration disposal projects including PCBs include. characteristic analysis system, storage system, pretreatment and transmission System, incineration system, flue gas purification system, process wastewater treatment system, automation control system, monitoring system, emergency response System, etc. 5.2.3 Auxiliary works including PCBs waste incineration disposal projects include. plant wall, road, fire, power supply and distribution, auxiliary oil Material supply, water supply and drainage, HVAC, maintenance, warehousing, communications and occupational safety protection. 5.3 Site selection 5.3.1 The site conditions of waste incineration disposal projects with PCBs shall comply with the relevant requirements set forth in HJ/T 176 and shall meet the environmental impact. Respond to the relevant requirements of the evaluation report. 5.4 General design 5.4.1 The general plan design of the waste incineration disposal project with PCBs shall be based on the nature of the waste containing PCBs and its incineration disposal. Point, fully consider pre-inspection, receiving metering, unloading, storage and pre-treatment, incineration, ash treatment, flue gas purification, process waste The main disposal process such as water treatment is determined by comprehensive comparison of several schemes. 5.4.2 Vertical design of waste incineration disposal projects with PCBs should fully consider the relative standards of each vulnerable area and accident pool High, and thus ensure that the wastewater in the polluted area and the initial rainwater on the ground are smoothly discharged into the accident pool, and the capacity design of the accident pool should be satisfied. Relevant provisions in HJ/T 167. 5.4.3 Pre-treatment facilities, feed facilities, incineration disposal facilities, and process wastewater treatment facilities for PCB incineration disposal projects The installation should not be set up in the open air, and the workshop where the above facilities are installed should have sufficient space to meet the process operation. 5.4.4 Containing PCBs Waste incineration disposal project site entrance and exit should achieve separation of people flow and logistics. 5.4.5 Containing PCBs Waste incineration disposal works should be fenced or fenced at the boundary of the plant to prevent livestock and unrelated personnel enter. 5.5 General layout 5.5.1 Waste disposal and disposal projects with PCBs should be arranged with the incineration plant as the main body, and other facilities should be based on PCBs. The waste disposal process is reasonably arranged to ensure that the relevant equipment is in good contact and the functions are fully utilized to ensure safe operation. Should avoid The production work area intersects with the office area. 5.5.2 Location of pre-inspection areas, weighing instruments, storage areas and PCB-containing wastes containing PCBs waste incineration disposal projects The in-plant transportation route should be reasonably arranged to minimize the number of waste transportation and the transshipment distance. 5.5.3 Wastewater incineration disposal project including PCBs The inflow line of the incineration line shall be consistent with the dominant wind direction of the plant, and the chimney shall be located under the plant area. Wind direction. The water supply facility should be built at the leading wind direction of the plant. 5.6 Factory road 5.6.1 Road load grades in the plant containing wastes incineration disposal project shall comply with the relevant provisions of GB J22 and be able to meet For transportation, fire protection and various pipelines, cement concrete or asphalt concrete should be used for the road surface. 5.6.2 Waste roads containing PCBs Waste incineration disposal works should be arranged in a circular shape, and the road width should not be less than 6m. Outside the plant For fire-fighting roads, the width of the road should not be less than 3.5m. 5.6.3 Including wastes in the incineration disposal project area of the PCBs, temporary parking lots for waste transportation vehicles can be set up near the logistics entrances and exits.6 Process design of waste incineration disposal engineering with PCBs6.1 Wastewater incineration disposal process with PCBs 6.1.1 Containing PCBs Waste incineration disposal mainly includes waste receiving, characteristic analysis, classified storage, pretreatment, transportation and feeding, Process links such as incineration disposal, flue gas purification and process wastewater treatment. 6.1.2 Wastewater incineration disposal process with PCBs It is necessary to achieve effective connection of various process links. The specific process is shown in Figure 1. 6.2 Receiving waste 6.2.1 Wastes incineration disposal projects with PCBs should be set up in the pre-inspection area of the plant. The design of the pre-inspection area should meet the following requirements. a) The location and area of the pre-screening area should meet the requirements for vehicle access; b) The ground in the pre-examination area shall be hard covered, and the seepage prevention shall meet the relevant requirements in GB 18597; c) Isolation channels should be installed around the pre-inspection area to prevent accidental leakage of liquid waste. 6.2.2 Wastewater incineration disposal projects with PCBs shall be equipped with weighing scales, and the configuration requirements shall be in accordance with the relevant provisions of HJ/T 176. 6.3 Analysis of the characteristics of waste 6.3.1 Containing PCBs Waste incineration disposal engineering characteristics analysis and identification laboratory should have sample pretreatment, PCBs content determination, yuan Functions such as elemental analysis, calorific value measurement and moisture measurement, which can be used for the physical properties of PCB-containing waste, PCBs content, and halogen. The content of the element, the content of S, the content of N, the composition and content of heavy metal elements were analyzed. Refer to 7.1 for the equipment requirements for analytical instruments. 6.3.2 The analysis of PCBs containing PCBs waste should be carried out according to the current national analytical methods. 6.3.3 Containing PCBs Waste incineration disposal projects shall establish a storage system for the identification and identification of PCBs containing waste characteristics. Waste receiving with PCBs Preflight and characterization Classified storage Pretreatment Waste transportation and feeding Incineration disposal Flue gas purification process wastewater Gas purification emission emission Water treatment Return water Solid salt, sludge Incineration residue Incineration fly ash Figure 1 Process flow of waste incineration disposal project with PCBs 6.4 Storage of waste 6.4.1 Storage of wastes containing PCBs shall comply with the requirements of GB 18597 and shall be set according to the relevant requirements of GB 15662.2. knowledge. 6.4.2 Waste storage with PCBs should be based on the predicted total inventory capacity, the type of waste, the requirements of the supporting facilities and the existing site Design and construction. The functional area division in the library can be divided into waste unloading area, storage area and pretreatment area. 6.4.3 Containing PCBs There should be an isolation channel around the waste storage to prevent accidental leakage of liquid waste. 6.4.4 Wastes with PCBs The site of the unloading area should be covered with steel plated ground with cofferdams to prevent seepage when PCBs are scattered. Translucent hair. 6.4.5 Waste storage areas containing PCBs should be partitioned and designed to store different types of waste. The storage area should be based on PCBs. Waste types and predicted storage quantities Construction of sectional storage bins and storage tanks shall be designed to meet the relevant provisions of GB 18597. 6.4.6 Containing PCBs The waste storage should be equipped with mechanical ventilation to achieve a micro-negative pressure in the warehouse. The air discharged from the reservoir should After initial filtration and adsorption treatment, the incinerator is discharged or introduced into the operating incinerator for incineration. 6.4.7 Waste storage with PCBs shall be constructed in accordance with GB J16 and GB J140, and a complete fire protection system shall be constructed and the fire shall be properly arranged. Disaster warning and fire extinguishing equipment. 6.4.8 Waste storage areas containing PCBs should be equipped with loading and unloading equipment such as cranes, hanging electric grabs, small forklifts and small forklifts. And according to the need to configure removable solid material belt conveyors and special containers, tools and so on. 6.4.9 Containing PCBs Waste storage should be equipped with absorbent cotton, sawdust, sand, iron shovel, iron trough and other materials required for emergency treatment. And items. 6.5 Waste pretreatment 6.5.1 Containing PCBs Waste pretreatment generally includes sorting and classification, transformer oil discharge, disassembly, cleaning, capacitor shearing, Concrete structures are broken and other materials are broken, liquid filtration, material mixing, etc. 6.5.2 Wastes containing PCBs should be sorted first, and equipme......Tips & Frequently Asked Questions:Question 1: How long will the true-PDF of HJ 2037-2013_English be delivered?Answer: Upon your order, we will start to translate HJ 2037-2013_English as soon as possible, and keep you informed of the progress. The lead time is typically 2 ~ 4 working days. The lengthier the document the longer the lead time.Question 2: Can I share the purchased PDF of HJ 2037-2013_English with my colleagues?Answer: Yes. 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