PPCPs在土壤-作物系统行为特征及环境风险的研究进展

doi:10.16085/j.issn.1000-6613.2020-1099

化工进展 ›› 2021, Vol. 40 ›› Issue (5): 2827-2838.DOI: 10.16085/j.issn.1000-6613.2020-1099

PPCPs在土壤-作物系统行为特征及环境风险的研究进展

李松旌¹^,²(), 樊向阳¹^,³^,⁴(), 崔二苹¹^,³^,⁴, 胡超¹^,³^,⁴, 崔丙健¹^,³^,⁴, 刘源¹^,³^,⁴, 李中阳¹^,³^,⁴, 景若瑶¹^,², 李胜曙¹^,²

^1.中国农业科学院农田灌溉研究所，河南新乡 453002
^2.中国农业科学院研究生院，北京 100081
^3.中国农业科学院农业水资源高效安全利用重点开放实验室，河南新乡 453002
^4.中国农业科学院新乡农业水土环境野外科学观测试验站，河南新乡 453002

收稿日期:2020-06-15 出版日期:2021-05-06 发布日期:2021-05-24
通讯作者: 樊向阳
作者简介:李松旌（1996—），男，硕士研究生，研究方向为农业水资源安全高效利用。E-mail：627888123@qq.com。
基金资助:
中央级公益性科研院所基本科研业务费专项(FIRI202003-01);国家自然科学基金(51479201);河南省科技攻关项目(192102110094)

Advances in behavioral characteristics and environmental risks of PPCPs in soil-crop systems

LI Songjing¹^,²(), FAN Xiangyang¹^,³^,⁴(), CUI Erping¹^,³^,⁴, HU Chao¹^,³^,⁴, CUI Bingjian¹^,³^,⁴, LIU Yuan¹^,³^,⁴, LI Zhongyang¹^,³^,⁴, JING Ruoyao¹^,², LI Shengshu¹^,²

^1.Farmland Irrigation Research Institute, Chinese Academy of Agricultural Sciences, Xinxiang 453002, Henan, China
^2.Graduate School of Chinese Academy of Agricultural Sciences, Beijing 100081, China
^3.Key Laboratory of High-efficient and Safe Utilization of Agriculture Water Resources, Chinese Academy of Agricultural Sciences, Xinxiang 453002, Henan, China
^4.Agricultural Water Soil Environmental Field Research Station of Xinxiang, Chinese Academy of Agricultural Sciences, Xinxiang 453002, Henan, China

Received:2020-06-15 Online:2021-05-06 Published:2021-05-24
Contact: FAN Xiangyang

摘要/Abstract

摘要：

随着药品和个人护理品（PPCPs）生产和使用量的增加，PPCPs及其代谢产物在水体、土壤环境中的检出量、检出种类与日俱增。本文基于国内外已有的相关文献，总结了典型PPCPs通过不同途径进入土壤-作物系统的环境风险，并从PPCPs在土壤-作物系统中的降解行为特征和迁移累积规律等方面对PPCPs环境行为及归趋的最新研究进展进行了综述，指出目前研究存在的PPCPs种类、浓度、输入方式以及环境背景的单一性等突出问题，并对该领域未来研究趋势进行了展望，如不同类别PPCPs的环境行为特征、与土壤微环境的互作机制、降解或螯合产物及其环境行为与风险等方面的研究，对于探明PPCPs对生态环境的影响规律及对人类健康的潜在危害具有重要意义。

关键词: 药品和个人护理品, 土壤-作物系统, 环境风险, 行为特征, 降解

Abstract:

With the increase of the production and usage of pharmaceutical and personal care products (PPCPs), the amounts and types of PPCPs as well as their metabolites detected in water and soil environment are increased. In this paper, the environmental risks of typical PPCPs entering the soil-crop system through different ways are summarized based on relevant literature. In addition, the latest research on environmental behavior and fate of PPCPs is reviewed from the aspects of PPCPs degradation behavior characteristics and the laws of migration and accumulation in the soil-crop system. It also points out the outstanding problems of PPCPs in the current research, such as the simplicity of PPCPs types, concentrations, input modes, and environmental backgrounds. The future research trends in this field are prospected, for instance, the environmental behavior characteristics of different types of PPCPs, the interaction mechanisms between PPCPs and soil microenvironment, degradation or chelation products, and their environmental behaviors and risks. This review is of great significance to investigate the influence of PPCPs on the ecological environment and its potential harm to human health.

Key words: pharmaceuticals and personal care products (PPCPs), soil-crop systems, environmental risks, behavioral characteristics, degradation

中图分类号:

李松旌, 樊向阳, 崔二苹, 胡超, 崔丙健, 刘源, 李中阳, 景若瑶, 李胜曙. PPCPs在土壤-作物系统行为特征及环境风险的研究进展[J]. 化工进展, 2021, 40(5): 2827-2838.

LI Songjing, FAN Xiangyang, CUI Erping, HU Chao, CUI Bingjian, LIU Yuan, LI Zhongyang, JING Ruoyao, LI Shengshu. Advances in behavioral characteristics and environmental risks of PPCPs in soil-crop systems[J]. Chemical Industry and Engineering Progress, 2021, 40(5): 2827-2838.

图/表 4

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PPCPs	进水浓度(均值/最大值)/μg·L^-1	出水浓度(均值/最大值)/μg·L^-1	国家，地区	年份/年	参考文献
咖啡因	12.005/16.783	0.023/0.026	中国，北京	2010	[45]
	0.973/—	0.046/—	中国，湖南	2014	[46]
	2.349/3.217	0.18/0.6	韩国，蔚山	2010	[47]
	57.4/—	33.7/—	挪威	2002	[48]
	80/—	0.017/—	美国，北卡罗来纳州	2008	[49]
布洛芬	1.38/—	0.18/—	中国，上海	2010—2011	[50]
	0.75/1.089	0.05/0.179	日本，东京	2001—2003	[51]
	2.265/2.853	0.04/0.075	韩国，蔚山	2010	[47]
	14.6/83.5	1.96/ 24.6	法国	1997—2007	[52]
	1.681/2.986	0.263/0.424	英国，塔夫河	2007	[53]
	8.45/16.5	0.384/0.773	加拿大，泰晤士河沿岸	2002	[54]
三氯生	—/0.774	—/0.182	中国，上海	2009	[55]
	0.547/0.785	0.112/0.149	韩国，蔚山	2010	[47]
	0.51/1.024	0.026/0.331	日本，东京	2001—2003	[51]
	0.38/—	0.15/0.43	法国	1997—2007	[52]
	5.58/17.1	0.452/1.189	加拿大，泰晤士河沿岸	2002	[54]
萘普生	0.012/0.032	0.011/0.02	中国，北京	2010	[45]
	2.584/5.033	0.166/0.111	韩国，蔚山	2010	[47]
	0.138/0.237	0.076/0.14	日本，东京	2001—2003	[51]
	0.838/1.457	0.37/0.703	英国，塔夫河	2007	[53]
	4.83/8.5	2.74/5.09	西班牙，塞维利亚	2004	[56]
	26.4/611	1.89/33.9	法国	1997—2007	[52]
卡马西平	0.003/—	0.003/—	中国，湖南	2014	[46]
	0.141/0.267	0.087/0.162	日本，东京	2001—2003	[51]
	0.327/—	0.188/—	韩国，釜山	2008	[57]
	0.968/1.9	0.674/2.3	法国	1997—2007	[52]
	1.694/2.73	2.499/4.596	英国，塔夫河	2007	[53]
	0.53/3.78	0.58/1.18	西班牙，塞维利亚	2004	[56]

PPCPs	进水浓度(均值/最大值)/μg·L^-1	出水浓度(均值/最大值)/μg·L^-1	国家，地区	年份/年	参考文献
咖啡因	12.005/16.783	0.023/0.026	中国，北京	2010	[45]
	0.973/—	0.046/—	中国，湖南	2014	[46]
	2.349/3.217	0.18/0.6	韩国，蔚山	2010	[47]
	57.4/—	33.7/—	挪威	2002	[48]
	80/—	0.017/—	美国，北卡罗来纳州	2008	[49]
布洛芬	1.38/—	0.18/—	中国，上海	2010—2011	[50]
	0.75/1.089	0.05/0.179	日本，东京	2001—2003	[51]
	2.265/2.853	0.04/0.075	韩国，蔚山	2010	[47]
	14.6/83.5	1.96/ 24.6	法国	1997—2007	[52]
	1.681/2.986	0.263/0.424	英国，塔夫河	2007	[53]
	8.45/16.5	0.384/0.773	加拿大，泰晤士河沿岸	2002	[54]
三氯生	—/0.774	—/0.182	中国，上海	2009	[55]
	0.547/0.785	0.112/0.149	韩国，蔚山	2010	[47]
	0.51/1.024	0.026/0.331	日本，东京	2001—2003	[51]
	0.38/—	0.15/0.43	法国	1997—2007	[52]
	5.58/17.1	0.452/1.189	加拿大，泰晤士河沿岸	2002	[54]
萘普生	0.012/0.032	0.011/0.02	中国，北京	2010	[45]
	2.584/5.033	0.166/0.111	韩国，蔚山	2010	[47]
	0.138/0.237	0.076/0.14	日本，东京	2001—2003	[51]
	0.838/1.457	0.37/0.703	英国，塔夫河	2007	[53]
	4.83/8.5	2.74/5.09	西班牙，塞维利亚	2004	[56]
	26.4/611	1.89/33.9	法国	1997—2007	[52]
卡马西平	0.003/—	0.003/—	中国，湖南	2014	[46]
	0.141/0.267	0.087/0.162	日本，东京	2001—2003	[51]
	0.327/—	0.188/—	韩国，釜山	2008	[57]
	0.968/1.9	0.674/2.3	法国	1997—2007	[52]
	1.694/2.73	2.499/4.596	英国，塔夫河	2007	[53]
	0.53/3.78	0.58/1.18	西班牙，塞维利亚	2004	[56]

PPCPs	浓度/μg·kg^-1	国家，地区	年份/年	参考文献
咖啡因	2.59	中国，北京	2014	[99]
咖啡因	1.1	美国，亚利桑那州	2009	[100]
布洛芬	318.5	美国，得克萨斯州	2010	[101]
	0.008	美国，加利福尼亚州	2013	[18]
	1.51	中国，河北	2008	[102]
	0.003	美国，加利福尼亚州	2009	[100]
	8.16	美国，得克萨斯州	2010	[101]
萘普生	0.024	美国，加利福尼亚州	2013	[18]
	0.013	美国，加利福尼亚州	2009	[100]
	1.06	中国，河北	2008	[102]
卡马西平	1.8	中国，北京	2014	[99]
	0.02	中国，河北	2008	[102]
	0.18	美国，亚利桑那州	2009	[100]

PPCPs	浓度/μg·kg^-1	国家，地区	年份/年	参考文献
咖啡因	2.59	中国，北京	2014	[99]
咖啡因	1.1	美国，亚利桑那州	2009	[100]
布洛芬	318.5	美国，得克萨斯州	2010	[101]
	0.008	美国，加利福尼亚州	2013	[18]
	1.51	中国，河北	2008	[102]
	0.003	美国，加利福尼亚州	2009	[100]
	8.16	美国，得克萨斯州	2010	[101]
萘普生	0.024	美国，加利福尼亚州	2013	[18]
	0.013	美国，加利福尼亚州	2009	[100]
	1.06	中国，河北	2008	[102]
卡马西平	1.8	中国，北京	2014	[99]
	0.02	中国，河北	2008	[102]
	0.18	美国，亚利桑那州	2009	[100]

PPCPs	浓度	种植媒介	作物类型	检查结果	参考文献
咖啡因	500ng·L^-1	活性污泥	卷心莴苣	未检测到	[119]
	500ng·L^-1	活性污泥	菠菜	未检测到	[119]
	与其他混合物混合	土壤	红薯	0.05~0.24ng·g^-1	[120]
	与其他混合物混合	土壤	胡萝卜	0.05~0.24ng·g^-1	[120]
	与其他混合物混合	土壤	番茄	可检测到	[121]
	与其他混合物混合	土壤	黄瓜	可检测到	[121]
布洛芬	500ng·L^-1	活性污泥	卷心莴苣	未检测到	[119]
	500ng·L^-1	活性污泥	菠菜	未检测到	[119]
	与其他混合物混合	土壤	红薯	0.05~0.24ng·g^-1	[120]
	与其他混合物混合	土壤	胡萝卜	0.05~0.24ng·g^-1	[120]
	与其他混合物混合	土壤	番茄	可检测到	[121]
	与其他混合物混合	土壤	黄瓜	可检测到	[121]
	1.27mg·L^-1	土壤	黑麦草	未检测到	[122]
	100ng·L^-1	营养液	莴苣	可检测到	[123]
萘普生	178.2ng·L^-1	水培	莴苣	可检测到	[118]
萘普生	178.2ng·L^-1	水培	羽衣甘蓝	可检测到	[118]

PPCPs在土壤-作物系统行为特征及环境风险的研究进展

Advances in behavioral characteristics and environmental risks of PPCPs in soil-crop systems

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