UNITED NATIONS BC UNEP/CHW/POP-SIWG.2/9 Distr.: General 09 February 2017 English only POPs SIWG meeting Bonn, Germany, 20-22 February 2017 Item 6 (b) of the provisional agenda Thirteenth meeting of the Conference of the Parties: Basel assessment of new Stockholm POPs chemicals Basel assessment of new Stockholm POPs chemicals Note by the Secretariat The annex to the present note sets out the draft assessment of candidate POPs under the Stockholm Convention. The present note, including its annex, has not been formally edited. UNEP/CHW/POPs-SIWG.2/1. 1 UNEP/CHW/POP-SIWG.2/9 Annex Basel Convention Draft assessment of candidate POPs under the Stockholm Convention Issue: Draft assessment of candidate POPs considered for listing in the Stockholm Convention at the eighth meeting of the Conference of the Parties to determine how they can be addressed by Basel Convention POPs technical guidelines. Chemicals addressed are: 1. Hexachlorobutadiene (HCBD) in Annex C 2. Decabromodiohenyl ether 3. Short-chained chlorinated paraffins (SCCPs) Substances Description Waste stream Hexachlorobutadiene (HCBD) Chemical identity and properties [1]: At room temperature: non-flammable, incombustible, clear, oily and colourless liquid; turpentine-like odor; Water solubility: 3.2 mg/L at 25 °C poorly soluble in water Chemical formula C4Cl6, Smiles notation: Cl2C=CClClC=CCl2 Molecular mass: 260.8 g/mol Melting point: -18 °C Boiling point: 212 °C at 101.3 kPa 3 Density: 1.68 g/cm at 20 °C Vapour pressure: 20 Pa (0.15 mm Hg) at 20 °C Log octanol/water partition coefficient (log Kow): 4.78 or 4.90 Air emissions Solid residues CAS Number: 87-68-3 1 How does Basel capture the chemical1 Y6 : Wastes from the production, formulation and use of organic solvents UN class 9, H11 Toxic (Delayed or chronic): Substances or wastes which, if they are inhaled or ingested or if they penetrate the skin, may involve delayed or chronic effects, including carcinogenicity UN class 9, H12 Ecotoxic: Substances or wastes Action for POW Include into PoW for the updating of the TG for the SIWG 2017-2019 Waste contaminated with hexachlorobutadiene is captured by Basel Convention annexes. Recommended actions To be added to the unintentional POPs technical guidelines. The following listing of entries from the Basel Conventio and categories of waste to be controlled (Y codes) is not comprehensive, nor definitive. It is based on a preliminary scientific assessment and may be subject to change such that new entries and categories of waste may be added or removed when developing or updating the technical guidelines. 2 Substances Description Short-chained chlorinated paraffins When HCBD is released into the environment, it tends to persist in the air, soil or water to which it was released and can accumulate in organisms. Transport between media: Expected to occur by volatilization and adsorption to suspended particulate matter. Use and production: None here since is intentional production already covered Unintentional generation in processes related to the following activities: production of certain chlorinated hydrocarbons; production of magnesium; incineration processes; and production of polyvinyl chloride, ethylene dichloride and vinyl chloride monomer IARC evaluation [2]: There is limited evidence in experimental animals for the carcinogenicity of hexachlorobutadiene. Hexachlorobutadiene is not classifiable as to its carcinogenicity to humans (Group 3). Chemical identity and properties: Chlorinated alkanes, chain-length: C10-C13, CAS Number (principal): 85535-84-8 Identity: chlorination: >48% (w/w); At temperature: non-flammable, incombustible, clear, oily/viscous and colourless liquid (yellowish) Water solubility: poorly soluble in water Chemical formula (general): CxH(2x-y+2)Cly Waste stream How does Basel capture the chemical1 which if released present or may present immediate or delayed adverse impacts to the environment by means of bioaccumulation and/or toxic effects upon biotic systems. Action for POW Leachates/wastewater from: non-point sources [4]; Leachates from plastics, paints or coatings Leather waste [5] SCCPs can be found as a contaminant in medium-chain CCPs (MCCPs; C14-C17) Y10: Waste substances and articles containing or contaminated with PCBs and/or PCTs or PBBs Y12: Wastes from production, formulation and use of inks, dyes, pigments, paints. Lacquers, varnish Y17: Wastes resulting Include into PoW for the updating of the TG for the SIWG 2017-2019 Recommended actions Develop a selfstanding TG (PCB TG as a model) 3 UNEP/CHW/POP-SIWG.2/9 Substances Chlorinated paraffins have the general molecular formula CxH(2x-y+2)Cly whereby for the short-chain paraffins (SCCPs) x=1013 and y=1-13 Description Waste stream How does Basel capture the chemical1 from surface treatment of metal and plastics Y18: Wastes arising from industrial waste disposal operations Y45: Organohalogen compounds other than substances referred to in Y39, Y41, Y42, Y43, Y44) Y46: Wastes collected from households H11 Toxic (Delayed or chronic): Substances or wastes which, if they are inhaled or ingested or if they penetrate the skin, may involve delayed or chronic effects, including carcinogenicity H12 Ecotoxic: Substances or wastes which if released present or may present immediate or delayed adverse impacts to the environment by means of bioaccumulation and/or toxic effects upon biotic systems. Action for POW Solid waste from producers and users of BDE-209; more specifically: Plastics in electric and electronic equipment Y13?: wastes from production, formulation and use of resins, latex, plasticizers, glues/adhesives Include into PoW for the updating of the TG for the SIWG 2017-2019 where x=10-13, y=1-13 Molecular mass: 320 g/mol–500 g/mol Log octanol/water partition coefficient (log Kow): 4.39 to 8.69 preferentially partition/concentrate to high organic carbon-containing sewage sludge POPs characteristics of chlorinated paraffins: Chlorinated naphthalenes were identified as meeting the ecological categorization criteria for persistence, bioaccumulation potential and inherent toxicity to nonhuman organisms Use and production: Substitute to certain PCB applications Metalworking; Plasticiser in plastics, esp. polyvinyl chloride (PVC) [3] Rubber conveyor belts Dam sealants Decabromodiphenyl ether Chemical identity and properties [6], [7]: Solid @20 °C and 1013 hPa; Odorless Melting point: 304 °C Vapour pressure: 0 Pa @21 °C 4 Recommended actions Substances Description CAS Number: 1163-19-5 IUPAC name: 2,3,4,5,6pentabromo-1-(2,3,4,5,6pentabromophenoxy) benzene BDE-209 Low pOW: 6.625 Water solubility: 100 ng/L @25 °C Soluble in organic solvents: no quantitative information found Waste stream POPs characteristics of decabromodiphenyl ether: When released to the environment, decaBDE is found in soil (50%) or sediment (49.3%; 0.6% in water [7] LC50 (rat): 2,000 mg/kg b.w. (practically not acutely toxic) [7] Half-life in environment from hours to years Production and use: c-DecaBDE consists of PBDE-209 at >97% [8]; the remainder are nonabrominated congeners[6] Another reference refer to Chinese products with higher content of octa- and nonabrominated congeners: 8.2% to 10.4% [9] Trade names include: bromkal82-0de, FR1210, Great Lakes DE-83R, SAYTEX 102E Flame Retardant Used a flame retardant in plastics for electric and electronic equipment, construction and building sector; in textile applications such as furniture (computers, TV sets, etc); Shredder light fraction (SLF) from automobiles [10]; Pipings in pyrotechnical devices; Fuel system applications (hoses, tanks) Textiles/furniture from household/ public buildings How does Basel capture the chemical1 Y18?: wastes arising from industrial waste operations Y45: Organohalogen compounds other than substances referred to in Y39, Y41, Y42, Y43, Y44) Y46 : Wastes collected from households H13: Capable by any means, after disposal of yielding another material, which possesses any of the characteristics listed above Action for POW Incorporate into existing POP-BDE guidelines; Reconsider low POP content; Include into pretreatment “mechanical separation” May need specification with view to membrane filtration; Here: flotation is needed 5 UNEP/CHW/POP-SIWG.2/9 Abbreviations: ASR Automotive shredder residue (used in Norway/Bipro report but not explained [11] Comments related to: A. Hexachlorobutadiene: a. Incorporate into unintentional POPs TG; thus, action for “contaminated with…” and not “consisting of, containing” B. SCCPs: a. Information: wastewater in China [4]: 90% of ∑SCCPs were in the range of 0.80–20.0 μg/g; only 5% were above 22 ug/g dw; corresponding to 20 mg/kg d.w. (possible half of a low POP content C. DecaBDE: a. For waste issues: concentrations in the waste stream matter b. Especially or screening, decaBDE is captured by XFS c. I have eliminated (from the TG on c-penta and c-octaBDE TG): i. Y40 ethers (although chemically an ether, does not exhibit properties of ethers) ii. H11 Toxic (Delayed or chronic): Substances or wastes which, if they are inhaled or ingested or if they penetrate the skin, may involve delayed or chronic effects, including carcinogenicity – does not enter easily (and completely into organisms)/tissue) iii. H12 Ecotoxic: Substances or wastes which if released present or may present immediate or delayed adverse impacts to the environment by means of bioaccumulation and/or toxic effects upon biotic systems – low body burdens, low toxicity) References 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. 6 IPCS, Hexachlorobutadiene, in Environmental Health Criteria. 1994. IARC, Some Chemicals that Cause Tumours of the Kidney or Urinary Bladder in Rodents and Some Other Substances, in IARC Monographs. 1999. p. 1. Commission, E., OPINION OF THE CSTEE ON “Short-Chain Chlorinated Paraffins (SCCPs)”. 2002. Zeng, L., et al., Levels and distribution patterns of short chain chlorinated paraffins in sewage sludge of wastewater treatment plants in China. Environmental Pollution, 2012. 160: p. 88-94. ChemVerbotsV, SCCPs. Germany. IPCS, Brominatedd diphenyl ethers, in Environmental Health Criteria. 1994. ECHA, Bis(pentabromophenyl) ether. Profile in ECHA database, 2017 acessed. La Guardia, M.J., R.C. Hale, and E. Harvey, Detailed polybrominated diphenyl ether (PBDE) congener composition of the widely used penta-, octa-, and deca-PBDE technical flame-retardant mixtures. Environmental science & technology, 2006. 40(20): p. 6247-6254. Chen, S.-J., et al., Brominated flame retardants in children’s toys: concentration, composition, and children’s exposure and risk assessment. Environmental science & technology, 2009. 43(11): p. 4200-4206. Norwegian Environment Agency, Delivery part one: Collect and summarise infomration on the management of plastic waste with c-decaBDE from e-waste and ELVs in Norway, including relevant regulations and policies. Literature study - Deca-BDE in waste streams. Final report. 2016. p. 12. Norwegian Environment Agency, Literature study - Deca-BDE in waste streams. Final report. 2015. p. 160.
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