Institute for Chemical and Bioengineering, Swiss Federal Institute of Technology, ETH Zurich, 8093 Zürich, Switzerland.
Institute for Chemical and Bioengineering, Swiss Federal Institute of Technology, ETH Zurich, 8093 Zürich, Switzerland; Institute for Sustainability Sciences, Agroscope, 8046 Zürich, Switzerland.
Sci Total Environ. 2016 Dec 15;573:1132-1146. doi: 10.1016/j.scitotenv.2016.08.105. Epub 2016 Oct 1.
Short-chain chlorinated paraffins (SCCPs) show high persistence, bioaccumulation potential, and toxicity (PBT properties). Consequently, restrictions on production and use have been enforced in several countries/regions. The Stockholm Convention on Persistent Organic Pollutants recognized the PBT properties and long-range transport potential of SCCPs in 2015 and is now evaluating a possible global phase-out or restrictions. In this context, it is relevant to know which countries are producing/using SCCPs and in which amounts, and which applications contribute most to their environmental emissions. To provide a first comprehensive overview, we review and integrate all publicly available data on the global production and use of both chlorinated paraffins (CPs) as a whole and specifically SCCPs. Considerable amount of data on production/use of CPs and SCCPs are missing. Based on the available data and reported emission factors, we estimate the past and current worldwide SCCP emissions from individual applications. Using the available data as a minimum scenario, we conclude: (i) SCCP production and use is increasing, with the current worldwide production volume being 165,000t/year at least, whereas the global production of total CPs exceeds 1milliont/year. (ii) The worldwide release of SCCPs from their production and use to air, surface water, and soil between 1935 and 2012 has been in the range of 1690-41,400t, 1660-105,000t, and 9460-81,000t, respectively. (iii) The SCCP manufacture and use in PVC, the use in metal working applications and sealants/adhesives, and the use in plastics and rubber contribute most to the emissions to air, surface water, and soil. Thus, the decrease in the environmental emissions of SCCPs requires reduction of SCCP use in (almost) all applications. (iv) Emissions due to the disposal of waste SCCPs cannot be accurately estimated, because relevant information is missing. Instead, we conduct a scenario analysis to provide some insights into it.
短链氯化石蜡 (SCCPs) 具有高持久性、生物蓄积潜力和毒性 (PBT 特性)。因此,许多国家/地区已经对其生产和使用进行了限制。2015 年,《关于持久性有机污染物的斯德哥尔摩公约》确认了 SCCPs 的 PBT 特性和长距离迁移潜力,目前正在评估是否可能全面淘汰或限制其使用。在这种情况下,了解哪些国家正在生产/使用 SCCPs 及其用量,以及哪些应用对其环境排放的贡献最大,是很重要的。为了提供一个全面的概述,我们审查和整合了所有关于全球氯化石蜡(CPs)整体和具体 SCCPs 的生产和使用的公开数据。关于 CPs 和 SCCPs 的生产/使用,有相当数量的数据缺失。根据现有数据和报告的排放因子,我们估计了过去和现在全球范围内各种应用领域的 SCCP 排放量。使用现有数据作为最低情景,我们得出结论:(i) SCCP 的生产和使用正在增加,目前全球 SCCP 的年生产规模至少为 16.5 万吨/年,而全球 CPs 的总产量超过 100 万吨/年。(ii) 1935 年至 2012 年,SCCPs 从生产和使用向空气、地表水和土壤中的释放量分别在 1690-41400 吨、1660-105000 吨和 9460-81000 吨之间。(iii) SCCP 在聚氯乙烯中的制造和使用、在金属加工应用和密封剂/粘合剂中的使用以及在塑料和橡胶中的使用,对向空气、地表水和土壤中的排放贡献最大。因此,减少 SCCPs 的环境排放需要减少(几乎)所有应用领域中 SCCPs 的使用。(iv) 由于废物 SCCPs 的处置而产生的排放无法准确估计,因为相关信息缺失。相反,我们进行了情景分析,以提供一些见解。