基于不同毒性终点的壬基酚生态风险评价

李雯雯; 王晓南; 高祥云; 李霁; 范博; 王尚洪; 刘征涛

doi:10.13198/j.issn.1001-6929.2019.03.14

基于不同毒性终点的壬基酚生态风险评价

doi: 10.13198/j.issn.1001-6929.2019.03.14

李雯雯^{1, 2,},
王晓南²,
高祥云²,
李霁²,
范博^{2, 3},
王尚洪^1, ,,
刘征涛^2, ,

1.
南昌大学生命科学学院, 江西南昌 330031
2.
中国环境科学研究院, 环境基准与风险评估国家重点实验室, 国家环境保护化学品生态效应与风险评估重点实验室, 北京 100012
3.
南昌大学, 鄱阳湖环境与资源利用教育部重点实验室, 江西南昌 330047

基金项目:

国家水体污染控制与治理科技重大专项 2017ZX07301-002

国家自然科学基金项目 41521003

环境基准与风险评估国家重点实验室自由探索基金项目

详细信息

作者简介:
李雯雯(1993-), 女, 河南信阳人, 1206523204@qq.com

通讯作者:
王尚洪(1972-), 男, 江西丰城人, 副研究员, 博士, 主要从事动物生理生态学研究, 2002shwang@163.com

刘征涛(1965-), 男, 江苏江阴人, 研究员, 博士, 主要从事环境安全与风险评估研究, liuzt@craes.org.cn

中图分类号: X171.5
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- 被引次数: 0
出版历程
- 收稿日期: 2018-10-17
- 修回日期: 2019-02-28
- 刊出日期: 2019-07-25

Ecological Risk Assessment of Nonylphenol based on Different Toxic Endpoints

LI Wenwen^{1, 2
,},
WANG Xiaonan²,
GAO Xiangyun²,
LI Ji²,
FAN Bo^{2, 3},
WANG Shanghong^{1
, ,},
LIU Zhengtao^{2
, ,}

1.
The College of Life Science, Nanchang University, Nanchang 330031, China
2.
State Key Laboratory of Environmental Criteria and Risk Assessment, State Environmental Protection Key Laboratory of Ecological Effects and Risk Assessment of Chemicals, Chinese Research Academy of Environmental Sciences, Beijing 100012, China
3.
The Key Laboratory of Poyang Lake Environment and Resource Utilization Ministry of Education, Nanchang University, Nanchang 330047, China

Funds:

Major Science and Technology Program for Water Pollution Control and Treatment, China 2017ZX07301-002

National Natural Science Foundation of China 41521003

Open Project of State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences

摘要

摘要: NP（nonylphenol，壬基酚）作为一种具有雌激素效应的持久性有机污染物，可对水生态系统产生不可忽视的有害影响，并且随着生产及使用量的增加，NP在国内外水环境中被不同程度地检测出来，引起较大关注，因此有必要对其生态风险进行研究.通过综述部分淡水水体中NP的污染现状，采用物种敏感性分布法（SSD）和联合概率曲线法（JPC）对NP的生态风险进行分析；构建基于生长和发育、生物化学、繁殖和细胞毒性终点的物种敏感度分布曲线；基于4个毒性终点数据，采用联合概率曲线法评估国内外部分淡水水体中NP的生态风险.结果表明：①我国辽河、珠江和骆马湖的ρ（NP）均高于国内平均水平，且总体上我国ρ（NP）平均值为0.709 μg/L.②基于生长和发育、生物化学、繁殖和细胞毒性终点推导的HC₅（5%物种受损有害浓度）值分别为0.694、0.589、0.142和0.317 μg/L.③在所调查水体中，以生长和发育为毒性终点的生态风险相对较小，处于可接受水平；以繁殖、细胞和生物化学为毒性终点的生态风险较高，应采取相关措施保障水生生物的安全.因此，NP对水生生物繁殖的毒性较明显，应持续关注其长期危害.
- 壬基酚 /
- 物种敏感度分布法 /
- 联合概率曲线 /
- 生态风险 /
- 淡水
Abstract: Nonylphenol (NP), a major persistent organic pollutant with estrogen effect, has adverse effects on the aquatic ecosystem. With the increase in production and use, NP has been detected at different levels in the domestic and foreign aquatic environment, causing great concern worldwide. Therefore, it is necessary to investigate its ecological risk. In this study, the current situation of NP pollution in some freshwater bodies was reviewed, and the ecological risk of NP was analyzed using the species sensitivity distribution (SSD) method and the joint probability curve (JPC) method. The SSD curves were constructed based on endpoints of growth and development, biochemistry, reproduction and cytotoxicity. Based on the four toxicity endpoint data, the JPC method was used to assess the ecological risk of NP in some freshwater bodies. The results showed that:(1) The average level of NP in the Liaohe River, the Zhujiang River and Luoma Lake were higher than the average level of domestic freshwater bodies, and the average exposure concentration of NP in China was 0.709 μg/L. (2) HC₅ values based on the endpoints of growth and development, biochemistry, reproduction and cytotoxicity were 0.694, 0.589, 0.142 and 0.317 μg/L, respectively. (3) In the investigated water bodies, the ecological risk based on the end point of growth and development was relatively small and at an acceptable level, while the ecological risk based on the end point of reproduction, cell and biochemistry was high, relevant measures should be taken to ensure the safety of aquatic species. Moreover, the toxicity of NP to reproduction of aquatic organism is obvious, and the long-term adverse effects of NP on aquatic species should be concerned continuously.
- nonylphenol /
- species sensitivity distribution /
- joint probability curve /
- ecological risk assessment /
- freshwater

HTML全文

图 1 基于不同毒性终点的SSD曲线

Figure 1. Species sensitivity distributions(SSDs) for NP based on different measured endpoints

下载: 全尺寸图片幻灯片

图 2 不同国家基于不同毒性终点的NP联合概率曲线

Figure 2. Joint probability curves (JPCs) for ecological risk of NP in surface water from different countries based on different toxicity endpoints

下载: 全尺寸图片幻灯片

表 1 我国主要淡水水体中ρ(NP)

Table 1. Summary of NP concentrations in surface waters of China

流域	ρ(NP)/(μg/L)		数据来源
流域	范围	平均值	数据来源
长江	0.1~0.289	0.212	文献[31]
辽河	0.418~2.066	0.809	文献[32]
黄河	0.166~1.188	0.534	文献[33]
珠江	0.124~3.95	1.443	文献[34]
筼筜湖	0.579~0.66	0.612	文献[35]
大辽河	nd~0.777	0.664	文献[36]
太湖	0.262~0.443	0.544	文献[37]
骆马湖	nd~1.758	1.21	文献[38]
注：“nd”表示未检出.下同.

下载: 导出CSV

表 2 国外部分淡水水体中ρ(NP)

Table 2. Summary of NP concentrations in surface waters of abroad

国别	流域名称	ρ(NP)/(μg/L)		数据来源
国别	流域名称	范围	平均值	数据来源
加拿大	圣劳伦斯河上游和劳伦特大湖盆地地表水	0.013~0.92	0.203	文献[39]
希腊	莱斯沃斯岛	0.012~0.21	0.091	文献[40]
希腊	中部内陆水体	nd~2.54	0.479	文献[40]
韩国	马山湾	0.101~0.928	0.349	文献[41]
	米尼奥河	0.033~1.03	0.132	文献[42]
西班牙	曼扎纳雷斯河	0.185~2.483	0.902	文献[43]
	贾拉马河	0.096~0.869	0.442	文献[43]
法国	塞纳河	0.057~0.153	0.099	文献[44]

下载: 导出CSV

表 3 基于不同毒性终点的物种敏感度分布曲线(SSD)参数

Table 3. Parameters of species sensitivity distributions (SSD) for NP based on different endpoints

毒性终点	数量/个	ρ(NP)/(μg/L)		HC₅/(μg/L)
毒性终点	数量/个	平均值	标准差	HC₅/(μg/L)
生长和发育	9	153	291	0.694
生物化学	8	183	337	0.581
繁殖	8	126	235	0.142
细胞	10	84	124	0.317

下载: 导出CSV

表 4 NP对各国基于不同毒性终点的5%水生生物造成危害的概率

Table 4. Probability of NP causing harm to 5% aquatic species in various countries based on different toxicity endpoints

毒性终点	5%水生生物造成危害的概率/%
毒性终点	中国	西班牙	希腊	加拿大	韩国
生长和发育	4.0	3.7	2.2	1.7	1.9
生物化学	6.7	6.3	4.3	3.7	4.3
繁殖	10.4	9.8	6.8	5.9	6.3
细胞	9.6	9.0	6.1	5.2	5.5

下载: 导出CSV

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