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我国氯化石蜡的环境赋存、人群暴露与管控:现状及展望

宋博宇 白露 黎娟 高鹏 张彩丽 高洁玉 王亚韡

宋博宇, 白露, 黎娟, 高鹏, 张彩丽, 高洁玉, 王亚韡. 我国氯化石蜡的环境赋存、人群暴露与管控:现状及展望[J]. 环境科学研究, 2022, 35(9): 2077-2091. doi: 10.13198/j.issn.1001-6929.2022.06.27
引用本文: 宋博宇, 白露, 黎娟, 高鹏, 张彩丽, 高洁玉, 王亚韡. 我国氯化石蜡的环境赋存、人群暴露与管控:现状及展望[J]. 环境科学研究, 2022, 35(9): 2077-2091. doi: 10.13198/j.issn.1001-6929.2022.06.27
SONG Boyu, BAI Lu, LI Juan, GAO Peng, ZHANG Caili, GAO Jieyu, WANG Yawei. Occurrence, Population Exposure and Control of Chlorinated Paraffins in China: Current Situation and Prospect[J]. Research of Environmental Sciences, 2022, 35(9): 2077-2091. doi: 10.13198/j.issn.1001-6929.2022.06.27
Citation: SONG Boyu, BAI Lu, LI Juan, GAO Peng, ZHANG Caili, GAO Jieyu, WANG Yawei. Occurrence, Population Exposure and Control of Chlorinated Paraffins in China: Current Situation and Prospect[J]. Research of Environmental Sciences, 2022, 35(9): 2077-2091. doi: 10.13198/j.issn.1001-6929.2022.06.27

我国氯化石蜡的环境赋存、人群暴露与管控:现状及展望

doi: 10.13198/j.issn.1001-6929.2022.06.27
基金项目: 国家自然科学基金项目(No.21625702, 22136006, 22021003)
详细信息
    作者简介:

    宋博宇(1988-),男,吉林公主岭人,高级工程师,硕士,主要从事POPs控制技术与管理政策研究,song.boyu@fecomee.org.cn

  • 中图分类号: X503

Occurrence, Population Exposure and Control of Chlorinated Paraffins in China: Current Situation and Prospect

Funds: National Natural Science Foundation of China (No.21625702, 22136006, 22021003)
  • 摘要: 氯化石蜡(Chlorinated paraffin,CPs)是一类人工合成化学品,被广泛用作阻燃剂和增塑剂,在生产和使用过程中释放到多种环境介质中(如水、沉积物、灰尘、空气和土壤等). 短链氯化石蜡(SCCPs)作为新增持久性有机污染物已于2017年被正式列入《关于持久性有机物的斯德哥尔摩公约》附件A中,中链氯化石蜡(MCCPs)因具有和SCCPs相似的性质和环境效应,已被列入持久性有机污染物候选名单. 我国是CPs的生产和使用大国,但对该类物质的风险评估与管控还存在不足. 本文通过收集并深入讨论已发表的CPs相关文章,在系统梳理不同介质中CPs赋存情况的基础上,利用释放因子解析方法,估算了CPs在生产和使用过程中进入到环境的量,发现土壤介质是环境中CPs的汇. 人类活动、经济活动和经济水平等对CPs在不同区域的赋存具有重要影响. 对人群暴露途径解析表明,职业暴露场景显著高于其他场景;生态风险和人体暴露风险评估表明,目前CPs对我国生态环境与人体健康的危害整体上还处于较低水平. 另外,本文介绍了国内外对于SCCPs和MCCPs的管控措施,并基于化学品管理和风险评估的考虑,提出未来亟需深入开展MCCPs和LCCPs (长链氯化石蜡)的迁移转化和风险研究,特别是评估CPs管控造成的潜在经济、社会和环境影响. 相关数据及分析可更好地为CPs产品的管控和国家开展履约行动提供科学数据和技术支撑,并为将来可能的CPs淘汰政策的制定提供参考.

     

  • 图  1  2019年中国SCCPs和MCCPs从生产、使用到排放的质量平衡分析

    Figure  1.  Mass balance of SCCPs and MCCPs in China from production, use to emission in 2019

    图  2  CPs的生命周期

    Figure  2.  The CPs life cycle

    图  3  国际CPs管控进程时间轴

    Figure  3.  Timeline of international control process of CPs

    表  1  不同环境介质中CPs的含量

    Table  1.   CPs concentration in different environmental media

    地区时间样品类别单位SCCPs含量MCCPs含量数据来源
    中间值范围中间值范围
    中国18个城市2008年气相ng/m311613.5~517文献[12]
    中国山东省2016年气相ng/m398~988文献[11]
    印度2006年气相ng/m310.2<2.65~47.43.62<1.8~38.2文献[13]
    日本2008年气相ng/m31.190.28~14.2文献[12]
    韩国2008年气相ng/m31.120.60~8.96文献[12]
    瑞士2011年气相ng/m34.31.8~17文献[14]
    巴基斯坦2011年气相ng/m35.13<2.65~14.24.21<1.8~9.45文献[13]
    瑞士2013年气相ng/m32.71.1~42文献[14]
    挪威2013—2014年气相ng/m39.61.7~541.2<0.35~13文献[15]
    中国10个城市2013—2014年颗粒相ng/m319.91.98~27415.61.27~312文献[16]
    中国山东省2016年颗粒相ng/m332~454文献[11]
    中国北京市2016年颗粒相ng/m314.99.2~19.61.70.6~2.7文献[17]
    中国北京市2016年河流ng/L45677~652文献[18]
    中国北京市2016年湖泊ng/L124<18~377文献[18]
    中国上海市2016年河流ng/L27815.0~1 64093940.3~3 870文献[19]
    美国2000—2004年河流ng/L1.1940.606~1.9350.0074<0.000 5~0.047文献[20]
    法国2015年河流ng/L<50~200文献[21]
    中国31个省份2016年土壤ng/g1)37439~1 609860127~1 969文献[22]
    中国台州市2017年土壤ng/g1)68.5~2.20×105507~4.40×106文献[23]
    中国江苏省2018年土壤ng/g1)15437.5~995.712115.1~739.6文献[24]
    挪威2008年土壤ng/g1)22<0.6~490文献[25]
    英国2008年土壤ng/g1)50<0.8~570文献[25]
    瑞士1989—2014年土壤ng/g1)3.0~355.1~160文献[26]
    中国山东省2009年河流沉积物ng/g1)1608.4~2 0003601.8~3 200文献[27]
    中国山东省2009年海洋沉积物ng/g1)11.05~229.06~63文献[27]
    中国珠三角地区2013年海洋沉积物ng/g1)17346.3~1 540868102~6 650文献[28]
    中国深圳市2013年海洋沉积物ng/g1)40114.7~57454110.9~2 500文献[28]
    中国香港2013年海洋沉积物ng/g1)12.2<0.6~75.912.5<1.0~286文献[28]
    中国上海市2016年河流沉积物ng/g1)89.3<1.70~2 02094710.1~10 800文献[19]
    西班牙2003年海洋沉积物ng/g1)0.460.21~2.09文献[29]
    日本2013年海洋沉积物ng/g1)8.01.3~27.416.63.2~56.8文献[28]
    注:1)表示以干质量计.
    下载: 导出CSV

    表  2  CPs在母乳及血液中的暴露浓度

    Table  2.   Exposure concentration of CPs in breast milk and blood

    地区时间样品类别单位SCCPs含量MCCPs含量LCCPs含量数据来源
    中间值范围中间值范围中间值范围
    中国11个省份2017年城市母乳ng/g1)393131~808494.594~1 714文献[58]
    中国11个省份2017年农村母乳ng/g1)478.5139~1 543572211~1 089文献[58]
    中国12个省份2007年城市母乳ng/g1)681170~6 15060.418.7~350文献[59]
    中国8个省份2007年农村母乳ng/g1)30368~1 58035.79.05~139文献[60]
    中国16个省份2011年城市母乳ng/g1)733131~1610013722.3~1 501文献[59]
    中国16个省份2011年农村母乳ng/g1)36065.6~2 31045.49.51~146文献[60]
    中国北京市2007—2009年城市母乳ng/g1)28<20~54文献[61]
    中国绍兴市2010年城市母乳ng/g1)37.9<12~12412138~18714.64.90~184文献[62]
    中国上海市2015—2016年城市母乳ng/g1)35.0<12~67670.138~1 26010.5<1.1~56.9文献[62]
    中国嘉兴市2015—2016年城市母乳ng/g1)28.6<12~64263.0<16~5475.23<1.1~18.4文献[62]
    中国绵阳市2018年城市母乳ng/mL82.629.2~27126.111.0~164文献[63]
    英国2001—2002年母乳ng/g1)180<80~82021.06.2~320文献[64]
    日本2007—2010年母乳ng/g1)<20<20文献[61]
    韩国2007—2010年母乳ng/g1)<20<20文献[61]
    瑞典2011年母乳ng/g1)15.6<12~24.137.3<16~77.74.28<1.1~21.4文献[62]
    挪威2014年母乳ng/g1)10.2<12~12043.1<16~3114.26<1.1~29.0文献[62]
    瑞典2016年母乳ng/g1)<12<12~27.821.0<16~60.02.80<1.1~9.34文献[62]
    中国深圳市2012年全血ng/g2)9814~3500216.3~3204.51.0~21文献[65]
    中国北京市2013年母体血清ng/g2)11321.7~373113.76~31.8文献[66]
    中国北京市2013年脐带血清ng/g2)248.51~1073.891.33~12.9文献[66]
    中国大连市2015年血浆ng/g2)26<12.6~203文献[67]
    中国武汉市2015—2016年母体血清ng/mL6615.9~58412629.3~1 006文献[26]
    中国武汉市2015—2016年脐带血清ng/mL378.46~22334.213.6~90.1文献[26]
    中国广州市2016—2017年母体血浆ng/mL5.933.28~10.42.881.30~5.50文献[68]
    中国广州市2016—2017年脐带血浆ng/mL2.650.89~4.131.180.89~1.69文献[68]
    中国广州市2018年血清ng/mL1.71.0~5.51.6<1.0~2.7文献[69]
    中国绵阳市2018年母体血清ng/mL20251.0~62057.817.4~225文献[63]
    中国绵阳市2018年脐带血清ng/mL88.013.3~24226.611.9~67.8文献[63]
    中国济南市2018—2019年血清ng/g2)10724.2~38413423.8~371文献[70]
    澳大利亚2002—2015年血清ng/g2)0.56<0.13~0.681.0<0.12~3.1文献[71]
    注:1)表示以脂质量计;2)表示以湿质量计.
    下载: 导出CSV

    表  3  CPs的国内外管控措施

    Table  3.   Management and control of CPs at home and abroad

    资料来源限制条件
    欧盟《持久性有机污染物法规》(EU)2019/1021 继续允许生产、投放市场和使用含有SCCPs质量分数低于1%(质量)的物质或混合物或含有浓度低于0.15%(质量)的SCCPs的消费产品;
    允许使用采矿业中的传送带和2015年12月4日或之前已使用的SCCPs大坝密封剂,以及2012年7月10日或之前已使用的除上述以外含SCCPs的物品
    欧盟REACH法规SVHC清单 物品中含有的SCCPs、MCCPs浓度超过0.1%,欧盟生产商或进口商应履行法规规定的告知或通报等义务
    欧盟2022年第10次联合执法行动 重点检查REACH法规和POPs法规相关有害物质限制的合规性
    挪威《消费性产品中禁用特定有害物质》PoHS 考虑到SCCPs已经被限制,PoHS增加了消费品MCCPs不超过0.1%的限制
    加拿大环境保护法(CEPA) 将SCCP列入首要的控制物质清单
    美国环境保护局(US EPA) 将SCCP列入TRI (Toxic Release Inventory)有毒物质排放清单
    OEKO-TEX STANDARD 100®及LEATHER STANDARD by OEKO-TEXR® SCCPs或MCCPs含量小于10 mg/kg,CPs总量小于50 mg/kg
    欧盟RoHS指令 均质材料中,MCCPs浓度不得超过0.1%(质量)
    中国重点管控新污染物清单(2021版) 自2024年1月1日起,SCCPs禁止生产、使用和进出口,以下用途除外:在天然及合成橡胶工业中生产传送带时使用的添加剂;采矿业和林业使用的橡胶输送带的备件;皮革业,尤其是皮革加脂;润滑油添加剂,尤其用于汽车、发电机和风能设施的发动机以及油气勘探钻井和生产柴油的炼油厂;户外装饰灯管;防水和阻燃油漆;黏合剂;金属加工;柔性聚氯乙烯的第二增塑剂(但玩具及儿童产品中的使用除外).
    废弃的SCCPs应当按照危险废物实施环境管理
    下载: 导出CSV
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