GB 36600-2018 English PDFUS$359.00 · In stock
Delivery: <= 4 days. True-PDF full-copy in English will be manually translated and delivered via email. GB 36600-2018: Soil environmental quality -- Risk control standard for soil contamination of development land Status: Valid GB 36600: Historical versions
Basic dataStandard ID: GB 36600-2018 (GB36600-2018)Description (Translated English): Soil environmental quality -- Risk control standard for soil contamination of development land Sector / Industry: National Standard Classification of Chinese Standard: Z64 Word Count Estimation: 18,187 Date of Issue: 2018-06-22 Date of Implementation: 2018-08-01 Older Standard (superseded by this standard): HJ/T 350-2007 Regulation (derived from): Ministry of Ecology and Environment Announcement No.13 of 2018 Issuing agency(ies): State Administration for Market Regulation, China National Standardization Administration GB 36600-2018: Soil environmental quality -- Risk control standard for soil contamination of development land---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. Soil environmental quality - Risk control standard for soil contamination of development land If Standard Ministry of Ecology and Environment State market supervision and administration Ministry of Environmental Protection State Administration of Quality Supervision, Inspection and Quarantine Published on.2018-06-22 2018-08-01 implementation Soil environmental quality Soil and water risk management and control standards for construction land (Trial) Soil environmental quality Risk control standard for soil contamination of development land release ICS National Standards of People's Republic of China ContentForeword...ii 1 Scope...1 2 Normative references...1 3 Terms and Definitions...2 4 Construction land classification...3 5 Screening value and control value of soil pollution risk of construction land...3 6 Monitoring requirements...6 7 Implementation and supervision...13 Appendix A (informative) Soil environmental background values of arsenic, cobalt and vanadium...14ForewordTo implement the "Environmental Protection Law of the People's Republic of China", strengthen the supervision of soil environment for construction land, and control pollution plots. This standard is formulated for the risks of human health and the safety of human settlements. This standard specifies the screening values and control values of soil pollution risks for construction land that protect human health, as well as monitoring and implementation. With supervision requirements. This standard is the first release. The following standards are the series of standards for soil environmental survey, monitoring, assessment and restoration of construction land in conjunction with this standard. HJ 25.1 Technical Guidelines for Site Environmental Investigation HJ 25.2 Site Environmental Monitoring Technical Guidelines HJ 25.3 Technical Guidelines for Risk Assessment of Contaminated Sites HJ 25.4 Technical Guidelines for Soil Remediation in Contaminated Sites From the date of implementation of this standard, the “Evaluation Standard for Soil Environmental Quality of Exhibition Sites (Provisional)” (HJ 350-2007) stop. This standard was formulated by the Department of Soil and Environmental Management of the Ministry of Ecology and Environment and the Department of Science and Technology Standards. This standard is mainly drafted by. Nanjing Institute of Environmental Sciences, Ministry of Ecology and Environment, China Academy of Environmental Sciences. This standard is approved by the Ministry of Ecology and Environment on May 17,.2018. This standard has been implemented since August 1,.2018. This standard is explained by the Ministry of Ecology and Environment. Soil environmental quality Soil and water risk management and control standards for construction land1 Scope of applicationThis standard specifies the screening values and control values of soil pollution risks for construction land that protect human health, as well as monitoring and implementation. With supervision requirements. This standard applies to soil pollution risk screening and risk control of construction land.2 Normative referencesThe contents of this standard refer to the following documents or their terms. For undated references, the latest version is appropriate. Used in this standard. GB/T 14550 Determination of soil quality BHC and DDT - Gas chromatography GB/T 17136 Determination of total mercury in soil mass - Cold atomic absorption spectrophotometric method GB/T 17138 Determination of copper and zinc - Flame atomic absorption spectrophotometric method GB/T 17139 Determination of nickel in soil quality - Flame atomic absorption spectrophotometric method GB/T 17141 Determination of lead and cadmium by graphite furnace atomic absorption spectrophotometric method GB/T 22105 Determination of total mercury, total arsenic and total lead GB 50137 Urban land classification and planning construction land standard HJ 25.1 Technical Guidelines for Site Environmental Investigation HJ 25.2 Site Environmental Monitoring Technical Guidelines HJ 25.3 Technical Guidelines for Risk Assessment of Contaminated Sites HJ 25.4 Technical Guidelines for Soil Remediation in Contaminated Sites HJ 77.4 Determination of Dioxins in Soils and Sediments Isotope Dilution High Resolution Gas Chromatography - High Resolution Mass spectrometry HJ 605 Determination of Volatile Organic Compounds in Soils and Sediments by Purge and Trap/Gas Chromatography-Mass Spectrometry HJ 642 Determination of Volatile Organic Compounds in Soils and Sediments by Headspace/Gas Chromatography-Mass Spectrometry HJ 680 Determination of mercury and arsenic, selenium, tellurium and thorium in soils and sediments - Microwave digestion/atomic fluorescence method HJ 703 Determination of soil and sediment phenolic compounds - Gas chromatography HJ 735 Determination of Volatile Halohydrocarbons in Soils and Sediments by Purge and Trap/Gas Chromatography-Mass Spectrometry HJ 736 Determination of volatile halogenated hydrocarbons in soils and sediments - Headspace/gas chromatography - mass spectrometry HJ 737 Determination of soil and sediments - Graphite furnace atomic absorption spectrophotometric method HJ 741 Determination of volatile organic compounds in soils and sediments - Headspace/gas chromatography HJ 742 Determination of volatile aromatic hydrocarbons in soils and sediments - Headspace/gas chromatography HJ 743 Determination of polychlorinated biphenyls in soils and sediments - Gas chromatography - mass spectrometry HJ 745 Determination of soil cyanide and total cyanide - Spectrophotometric method HJ 780 Determination of inorganic elements in soils and sediments - Dispersion X-ray spectroscopy HJ 784 Determination of polycyclic aromatic hydrocarbons in soils and sediments - High performance liquid chromatography HJ 803 Determination of 12 Metal Elements in Soils and Sediments Aqueous Extract - Inductively Coupled Plasma Spectral method HJ 805 Determination of Polycyclic Aromatic Hydrocarbons in Soils and Sediments - Gas Chromatography - Mass Spectrometry HJ 834 Determination of semi-volatile organic compounds in soils and sediments - Gas chromatography - mass spectrometry HJ 835 Determination of organochlorine pesticides in soils and sediments - Gas chromatography - mass spectrometry HJ 921 Determination of organochlorine pesticides in soils and sediments - Gas chromatography HJ 922 Determination of soil and sediment polychlorinated biphenyls - Gas chromatography HJ 923 Determination of total mercury in soils and sediments - catalyzed pyrolysis - cold atomic absorption spectrophotometric method CJJ/T 85 Urban Green Space Classification Standard3 Terms and definitionsThe following terms and definitions apply to this standard. 3.1 Construction land Refers to the construction of buildings and structures, including urban and rural residential and public facilities, industrial and mining land, and transportation facilities. Land for application, land for tourism, land for military facilities, etc. 3.2 Soil contamination risk of development land Refers to the long-term exposure of the living and working people on the construction land to soil contaminants due to chronic toxic effects or carcinogenic effects. Adverse effects on health. 3.3 Exposure pathway Refers to the way in which the pollutants in the soil of the construction land arrive and are exposed to the human body. Mainly include. (1) oral intake of soil (2) skin contact with soil; (3) inhalation of soil particles; (4) inhalation of air from surface soil in outdoor air (5) inhaling gaseous pollutants from the underlying soil in outdoor air; (6) inhaling indoor air from under A gaseous pollutant in the layer of soil. 3.4 Soil screening risk screening value for construction land Development land Refers to the fact that under certain land use modes, the content of pollutants in the soil of construction land is equal to or lower than this value, Kang’s risk can be ignored; if it exceeds this value, there may be risks to human health, and further detailed investigations should be carried out. Risk assessment to determine the specific pollution range and risk level. 3.5 Risk of soil pollution risk for construction land Development land It means that under certain land use modes, if the content of pollutants in the soil of construction land exceeds this value, it usually exists for human health. In the event of unacceptable risks, risk management or repair measures should be taken. 3.6 Soil background value Refers to the statistical value based on the background content of the soil environment. Usually expressed as a certain quantile value of the background content of the soil environment. among them The soil environmental background content refers to the soil element that is only affected by geochemical processes and non-point source inputs under certain time conditions. The content of the element or compound.4 Construction land classification4.1 In the construction land, the urban construction land can be divided into the following two categories according to the different exposure conditions of the protected objects. 4.1.1 Type 1 land use. including residential land (R) in urban construction land specified in GB 50137, public management and public Primary and secondary school land (A33), medical and health land (A5), and social welfare facility land (A6) in the common service land, And community parks in park green space (G1) or children's park land. 4.1.2 Type II land use. including industrial land (M) in urban construction land specified in GB 50137, logistics storage land (W), commercial service facility land (B), road and transportation facility land (S), utility land (U), public pipe Land for public and public services (A) (except A33, A5, A6), and green space and square land (G) (community in G1) Garden or children's park land, etc.). 4.2 In the construction land, other construction land can be classified according to 4.1.5 Construction land soil pollution risk screening value and control value5.1 Screening values and control values of soil pollution risk for construction land to protect human health are shown in Tables 1 and 2, where Table 1 is basic. Items, Table 2 are other items. See 3.3 for the exposure pathways considered in this standard. Table 1 Screening values and control values of soil pollution risk of construction land (basic items) Unit. mg/kg Serial number pollutant item CAS number Filter value control value the first sort Land use Second class Land use the first sort Land use Second class Land use Heavy metals and inorganics 1 arsenic 7440-38-2.201 601 120 140 2 Cadmium 7440-43-9 20 65 47 172 3 Chromium (hexavalent) 18540-29-9 3.0 5.7 30 78 4 copper 7440-50-8.2000 18000 8000 36000 5 lead 7439-92-1 400 800 800 2500 6 Mercury 7439-97-6 8 38 33 82 7 Nickel 7440-02-0 150 900 600.2000 Volatile organic compounds 8 carbon tetrachloride 56-23-5 0.9 2.8 9 36 9 Chloroform 67-66-3 0.3 0.9 5 10 10 methyl chloride 74-87-3 12 37 21 120 11 1,1-dichloroethane 75-34-3 3 9 20 100 12 1,2-dichloroethane 107-06-2 0.52 5 6 21 13 1,1-dichloroethylene 75-35-4 12 66 40.200 14 cis-1,2-dichloroethylene 156-59-2 66 596.200.2000 15 anti-1,2-dichloroethylene 156-60-5 10 54 31 163 16 dichloromethane 75-09-2 94 616 300.2000 17 1,2-dichloropropane 78-87-5 1 5 5 47 18 1,1,1,2-tetrachloroethane 630-20-6 2.6 10 26 100 19 1,1,2,2-tetrachloroethane 79-34-5 1.6 6.8 14 50 20 Tetrachloroethylene 127-18-4 11 53 34 183 Serial number pollutant item CAS number Filter value control value the first sort Land use Second class Land use the first sort Land use Second class Land use 21 1,1,1-trichloroethane 71-55-6 701 840 840 840 22 1,1,2-trichloroethane 79-00-5 0.6 2.8 5 15 23 Trichloroethylene 79-01-6 0.7 2.8 7 20 24 1,2,3-trichloropropane 96-18-4 0.05 0.5 0.5 5 25 Vinyl Chloride 75-01-4 0.12 0.43 1.2 4.3 26 benzene 71-43-2 1 4 10 40 27 chlorobenzene 108-90-7 68 270.200 1000 28 1,2-dichlorobenzene 95-50-1 560 560 560 560 29 1,4-dichlorobenzene 106-46-7 5.6 20 56.200 30 ethylbenzene 100-41-4 7.2 28 72 280 31 styrene 100-42-5 1290 1290 1290 1290 32 toluene 108-88-3 1200 1200 1200 1200 33 x-xylene p-xylene 108-38-3, 106-42-3 163 570 500 570 34 o-xylene 95-47-6 222 640 640 640 Semi-volatile organic matter 35 nitrobenzene 98-95-3 34 76 190 760 36 aniline 62-53-3 92 260 211 663 37 2-Chlorophenol 95-57-8 250 2256 500 4500 38 benzo[a]蒽56-55-3 5.5 15 55 151 39 benzo[a]芘50-32-8 0.55 1.5 5.5 15 40 benzo[b]fluoranthene 205-99-2 5.5 15 55 151 41 benzo[k]fluoranthene 207-08-9 55 151 550 1500 42 䓛218-01-9 490 1293 4900 12900 43 dibenzo[a, h]蒽53-70-3 0.55 1.5 5.5 15 44 茚[1,2,3-cd]芘193-39-5 5.5 15 55 151 45 naphthalene 91-20-3 25 70 255 700 Note. 1 The specific pollutant content in the soil exceeds the screening value, but is equal to or lower than the background value of the soil environment (see 3.6). Incorporate pollution land management. The background value of the soil environment can be found in Appendix A. Table 2 Screening values and control values of soil pollution risk of construction land (other items) Unit. mg/kg Serial number pollutant item CAS number Filter value control value the first sort Land use Second class Land use the first sort Land use Second class Land use Heavy metals and inorganics 1 锑7440-36-0 20 180 40 360 2 铍7440-41-7 15 29 98 290 3 Cobalt 7440-48-4.201 701 190 350 4 methylmercury 22967-92-6 5.0 45 10 120 Serial number pollutant item CAS number Filter value control value the first sort Land use Second class Land use the first sort Land use Second class Land use 5 vanadium 7440-62-2 1651 752 330 1500 6 cyanide 57-12-5 22 135 44 270 Volatile organic compounds 7 monobromodichloromethane 75-27-4 0.29 1.2 2.9 12 8 bromoform 75-25-2 32 103 320 1030 9 dibromochloromethane 124-48-1 9.3 33 93 330 10 1,2-dibromoethane 106-93-4 0.07 0.24 0.7 2.4 Semi-volatile organic matter 11 Hexachlorocyclopentadiene 77-47-4 1.1 5.2 2.3 10 12 2,4-Dinitrotoluene 121-14-2 1.8 5.2 18 52 13 2,4-dichlorophenol 120-83-2 117 843 234 1690 14 2,4,6-trichlorophenol 88-06-2 39 137 78 560 15 2,4-dinitrophenol 51-28-5 78 562 156 1130 16 pentachlorophenol 87-86-5 1.1 2.7 12 27 Di(2-ethylhexyl) phthalate Ester 117-81-7 42 121 420 1210 18 butyl benzyl phthalate 85-68-7 312 900 3120 9000 19 di-n-octyl phthalate 117-84-0 390 2812 800 5700 20 3,3'-Dichlorobenzidine 91-94-1 1.3 3.6 13 36 Organic pesticides 21 Atrazine 1912-24-9 2.6 7.4 26 74 22 Chlordane 2 12789-03-6 2.0 6.2 20 62 23 p,p'-Drips 72-54-8 2.5 7.1 25 71 24 p,p'-Dripper 72-55-9 2.0 7.0 20 70 25 DDT 3 50-29-3 2.0 6.7 21 67 26 Dichlorvos 62-73-7 1.8 5.0 18 50 27 Dimethoate 60-51-5 86 619 170 1240 28 endosulfan 4 115-29-7 234 1687 470 3400 29 heptachlor 76-44-8 0.13 0.37 1.3 3.7 30 α-六六六319-84-6 0.09 0.3 0.9 3 31 β-六六六319-85-7 0.32 0.92 3.2 9.2 32 γ-六六六58-89-9 0.62 1.9 6.2 19 33 Hexachlorobenzene 118-74-1 0.33 1 3.3 10 34 mirex 2385-85-5 0.03 0.09 0.3 0.9 Polychlorinated biphenyls, polybrominated biphenyls and dioxins 35 PCBs (total) 5 - 0.14 0.38 1.4 3.8 3,3',4,4',5-pentachlorobiphenyl (PCB 126) 57465-28-8 4×10-5 1×10-4 4×10-4 1×10-3 3,3',4,4',5,5'-hexachlorobiphenyl (PCB 169) 32774-16-6 1×10-4 4×10-4 1×10-3 4×10-3 Serial number pollutant item CAS number Filter value control value the first sort Land use Second class Land use the first sort Land use Second class Land use 38 Dioxins (total toxicity equivalent) - 1×10-5 4×10-5 1×10-4 4×10-4 39 Polybrominated biphenyls (total) - 0.02 0.06 0.2 0.6 Petroleum hydrocarbons 40 Petroleum Hydrocarbons (C10-C40) - 826 4500 5000 9000 Note. 1 The specific pollutant content in the soil exceeds the screening value, but is equal to or lower than the background value of the soil environment (see 3.6). Incorporate pollution land management. The background value of the soil environment can be found in Appendix A. 2 Chlordane is the sum of the contents of α-chlordane and γ-chlordane. 3 DDT is the sum of the contents of o, p'-DDT, p, p'-DDT. 4 Endosulfan is the sum of the contents of α-endosulfan and β-endosulfan. 5 PCBs (total) are PCB 77, PCB 81, PCB105, PCB114, PCB118, PCB123, PCB 126, PCB156, The total content of twelve substances in PCB157, PCB167, PCB169 and PCB189. 5.2 Determination of soil pollution risk for construction land screening of pollutants 5.2.1 The items listed in Table 1 are the mandatory items for screening the soil pollution risk of construction land in the preliminary investigation stage. 5.2.2 The selection of the soil pollution risk screening for construction land in the preliminary investigation stage is based on HJ 25.1, HJ 25.2 and related technologies. The regulations are determined and may include, but are not limited to, the items listed in Table 2. 5.3 Use of soil pollution risk screening values and control values for construction land 5.3.1 If the planned use of the construction land is the first type of land use, the screening values and control values of the first type of land in Tables 1 and 2 shall apply. If the planned use is for the second type of land use, the screening values and control values for the second type of land in Tables 1 and 2 shall apply. Unplanned use is not clear The screening values and regulatory values of the first type of land in Tables 1 and 2 shall apply. 5.3.2 If the pollutant content in the soil of the construction land is equal to or lower than the risk screening value, the soil pollution risk of the construction land is generally Can be ignored in the case. 5.3.3 It is determined through preliminary investigation that the content of pollutants in the soil of construction land is higher than the risk screening value, which should be based on HJ 25.1. Detailed investigations are carried out on standards such as HJ 25.2 and related technical requirements. 5.3.4 It is determined by detailed investigation that the pollutant content in the soil of construction land is equal to or lower than the risk control value, which should be based on HJ. 25.3 and other relevant technical requirements, carry out risk assessment, determine the level of risk, determine whether risk management or control is required Repair measures. 5.3.5 Through detailed investigation to determine that the content of pollutants in the soil of construction land is higher than the risk control value, which usually exists for human health. Risks are not acceptable and risk management or remediation measures should be taken. 5.3.6 If the construction land needs to be repaired, its restoration target should be based on HJ 25.3, HJ 25.4 and other related technologies. The requirements are determined and should be lower than the risk control value. 5.3.7 Contaminant items not listed in Tables 1 and 2 may be risked according to HJ 25.3 and other related technical requirements. Evaluate and derive soil contamination risk screening values for specific pollutants.6 Monitoring requirements6.1 Soil environmental survey and monitoring of construction land shall be carried out in accordance with HJ 25.1, HJ 25.2 and relevant technical regulations. 6.2 Analytical methods for soil contaminants are carried out according to Table 3. Contaminant projects with analytical method standards are not yet formulated, pending analysis ......Tips & Frequently Asked Questions:Question 1: How long will the true-PDF of GB 36600-2018_English be delivered?Answer: Upon your order, we will start to translate GB 36600-2018_English as soon as possible, and keep you informed of the progress. The lead time is typically 2 ~ 4 working days. 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