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我国典型含PFOS/PFOSF废物处置技术可行性分析与建议
引用本文:张磊,郑哲,陈文静,宁禹航,陈自强,王坚,杜涛.我国典型含PFOS/PFOSF废物处置技术可行性分析与建议[J].环境科学研究,2022,35(8):1974-1985.
作者姓名:张磊  郑哲  陈文静  宁禹航  陈自强  王坚  杜涛
作者单位:1.沈阳环境科学研究院,国家环境保护危险废物处置工程技术(沈阳)中心,辽宁 沈阳 110167
基金项目:国家重点研发计划项目(No.2018YFC1802100);全球环境基金-中国PFOS优先行业削减与淘汰项目(No.CS16)
摘    要:为促进我国全氟辛基磺酸及其盐类和全氟辛基磺酰氟(PFOS/PFOSF)的削减和逐步淘汰,防控环境风险,迫切需要对淘汰、废弃的含PFOS/PFOSF产品、副产物以及生产和使用过程中产生的含PFOS/PFOSF废物进行安全无害化处理处置. 调研和数据分析结果表明,2021年我国已停产PFOSF,2002—2020年我国PFOS/PFOSF的生产总量约为2 120 t. 我国典型含PFOS/PFOSF液态废物包括废弃消防泡沫、消防泡沫使用后收集的残液、废弃电镀镀液、工艺或清洗废水、废有机溶剂,以及固态/半固态废物有蒸(精)馏釜残、废水处理污泥、污染土壤、电镀滤渣、废吸附剂和过滤材料等. 目前针对液态废物,可行的PFOS/PFOSF非破坏处理技术主要有活性炭和树脂吸附、膜滤、混凝,可行的PFOS/PFOSF破坏处理技术有焚烧/水泥窑、超声降解和亚/超临界水处理技术,但在应用时都有一定的前置条件;针对固态/半固态废物,可行的PFOS/PFOSF非破坏处理技术包括稳定化和废物填埋,而焚烧/水泥窑是目前最为可行的PFOS/PFOSF破坏处理技术. 建议根据我国典型含PFOS/PFOSF废物的特点采取相应可行的处理处置技术,在应用成熟技术的同时,适当尝试采用亚/超临界水处理技术、超声降解技术以及其他较新的技术;对PFOS/PFOSF物质含量≥50 mg/kg的废物采用可行的破坏技术处置,对PFOS/PFOSF物质含量<50 mg/kg的废物经稳定化预处理后方可进入填埋场. 

关 键 词:全氟辛基磺酸及其盐类和全氟辛基磺酰氟(PFOS/PFOSF)    废物特点    处置    可行性分析    处置方案
收稿时间:2022-04-07

Feasibility Analysis and Recommendations of Disposal Technology of PFOS/PFOSF-Containing Wastes in China
Institution:1.National Environmental Engineering Technology Center for Hazardous Waste Treatment, Shenyang Academy of Environmental Sciences, Shenyang 110167, China2.School of Metallurgy, Northeastern University, Shenyang 110819, China3.Foreign Environmental Cooperation Center, Ministry of Ecology and Environment, Beijing 100035, China4.Shenyang Huanke Testing Technology Co., Ltd., Shenyang 110167, China5.Shenyang Research Institute of Chemical Industry, Shenyang 110021, China
Abstract:In order to promote the reduction and phase-out of perfluorooctane sulfonic acid and its salts and perfluorooctane sulfonyl fluoride (PFOS/PFOSF), and prevent and control environmental risks, it is urgent to carry out safe and harmless treatment of the products, by-products and wastes containing PFOS/PFOSF produced during production and use. The survey and data analysis show that China stopped production of PFOSF in 2021, and the total production of PFOS/PFOSF during 2002-2020 is about 2120 t. Typical liquid wastes containing PFOS/PFOSF include waste firefighting foam, residual liquid collected after use of firefighting foam, waste electroplating solution, process or cleaning wastewater, waste organic solvent, etc. Solid/semisolid wastes include distillation (rectification) still residue, wastewater treatment sludge, contaminated soil, electroplating filter residue, waste adsorbent and filter material, etc. At present, the feasible non-destructive treatment technologies for PFOS/PFOSF liquid wastes mainly include activated carbon and resin adsorption, membrane filtration and coagulation. The feasible PFOS/PFOSF destruction treatment technologies include incineration/cement kiln, ultrasonic degradation and sub/supercritical water treatment, but they all have certain preconditions in their application. For solid/semisolid wastes, feasible PFOS/PFOSF non-destructive treatment technologies include stabilization and landfill, and incineration/cement kiln is currently the most feasible PFOS/PFOSF destructed treatment technology. It is recommended to adopt appropriate treatment and disposal technologies according to the characteristics of typical PFOS/PFOSF wastes, while applying mature technologies, try to adopt sub/supercritical water treatment technology, ultrasonic degradation technology and other relatively new technologies. Wastes with PFOS/PFOSF content ≥50 mg/kg should be treated with PFOS/PFOSF destruction technologies, and wastes with PFOS/PFOSF content <50 mg/kg can be landfilled after stabilization pretreatment. 
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