有机磷阻燃剂TCIPP对土壤生物的毒性效应与生态风险评估

周国蕊, 钱苗苗, 门姝慧, 高富, 张依章, 闫振广

中国环境科学 ›› 2025, Vol. 45 ›› Issue (10) : 5848-5857.

PDF(1238 KB)
PDF(1238 KB)
中国环境科学 ›› 2025, Vol. 45 ›› Issue (10) : 5848-5857.
环境毒理与健康

有机磷阻燃剂TCIPP对土壤生物的毒性效应与生态风险评估

  • 周国蕊1, 钱苗苗2, 门姝慧1, 高富2, 张依章1, 闫振广1
作者信息 +

Toxic effects and ecological risk assessment of the organophosphorus flame retardant TCIPP on soil organisms

  • ZHOU Guo-rui1, QIAN Miao-miao2, MEN Shu-hui1, GAO Fu2, ZHANG Yi-zhang1, YAN Zhen-guang1
Author information +
文章历史 +

摘要

磷酸三(2-氯异丙基)酯(TCIPP)广泛存在于环境介质中,潜在生态风险值得关注,由于缺乏毒性数据等原因,我国尚未制定TCIPP的土壤安全阈值.本研究基于国际标准毒性测试方法,开展了TCIPP对5种陆生植物(大白菜、鸡毛菜、小麦、黄瓜、番茄)和1种无脊椎动物(赤子爱胜蚓)的毒性试验,并结合文献数据推导TCIPP的土壤预测无效应浓度值(PNEC)值,继而开展我国土壤中TCIPP的生态风险评估.结果表明,大白菜、鸡毛菜和番茄(根伸长和/或发芽率)对TCIPP的敏感性最高,无观察效应浓度值(NOEC)为80mg/kg,小麦(发芽率)对TCIPP的敏感性最低,NOEC为320mg/kg;赤子爱胜蚓的生长NOEC值为1mg/kg.基于物种敏感度分布法计算得出,TCIPP的土壤PNEC值为0.035mg/kg.我国不同地区土壤中TCIPP平均暴露水平范围为0.01-444ng/g.TCIPP的风险商(risk quotient, RQ)最高值为12.57,其中,工业区土壤中TCIPP的生态风险较高,农田土壤的风险相对较低.

Abstract

Tris(2-chloroisopropyl) phosphate (TCIPP), a widely present organophosphate flame retardant, poses potential ecological risks due to its persistence and bioactivity in environmental media. However, in China, soil safety thresholds for TCIPP have not yet been established, primarily due to limited toxicity data. In this study, standard toxicity tests were conducted on five terrestrial plants (Brassica pekinensis, Brassica rapa var. chinensis, Triticum aestivum, Cucumis sativus, and Solanum lycopersicum) and one invertebrate species (Eisenia fetida), to evaluate the phytotoxic and ecotoxic effects of TCIPP. By combining our results with literature data, the predicted no-effect concentration (PNEC) of TCIPP in soil was derived, and an ecological risk assessment was conducted for TCIPP in Chinese soils. Results showed that B. pekinensis, B. rapa var. chinensis, and S. lycopersicum exhibited the highest sensitivity (root elongation and/or germination rate) to TCIPP with a no-observed-effect concentration (NOEC) of 80mg/kg, while wheat T. aestivum (germination rate) showed the least sensitivity with a NOEC of 320mg/kg. The growth NOEC for E. fetida was determined to be 1mg/kg. Using the species sensitivity distribution (SSD) method, the calculated PNEC value of TCIPP in soil was 0.035mg/kg. Environmental monitoring data revealed that TCIPP concentrations in soils across different regions of China ranged from 0.01 to 444ng/g. Risk quotient (RQ) analysis indicated that TCIPP poses a high ecological risk in industrial areas (maximum RQ = 12.57), whereas agricultural soil showed relatively low risk.

关键词

TCIPP / 物种敏感度分布 / 预测无效应浓度 / 生态风险 / 土壤

Key words

TCIPP / species sensitivity distribution / predicted no effect concentration / ecological risk / soil

引用本文

导出引用
周国蕊, 钱苗苗, 门姝慧, 高富, 张依章, 闫振广. 有机磷阻燃剂TCIPP对土壤生物的毒性效应与生态风险评估[J]. 中国环境科学. 2025, 45(10): 5848-5857
ZHOU Guo-rui, QIAN Miao-miao, MEN Shu-hui, GAO Fu, ZHANG Yi-zhang, YAN Zhen-guang. Toxic effects and ecological risk assessment of the organophosphorus flame retardant TCIPP on soil organisms[J]. China Environmental Science. 2025, 45(10): 5848-5857
中图分类号: X53   

参考文献

[1] Su G, Letcher R J, Yu H. Organophosphate flame retardants and plasticizers in aqueous solution: pH-dependent hydrolysis, kinetics, and pathways [J]. Environmental Science & Technology, 2016,50(15): 8103-8111.
[2] Wei G L, Li D Q, Zhuo M N, et al. Organophosphorus flame retardants and plasticizers: Sources, occurrence, toxicity and human exposure [J]. Environmental Pollution, 2015,196:29-46.
[3] Marklund A, Andersson B, Haglund P. Screening of organophosphorus compounds and their distribution in various indoor environments [J]. Chemosphere, 2003,53(9):1137-1146.
[4] Zhang Y, Guo C, Sun S, et al. Cigarette filters-A neglected source of phthalate exposure to humans [J]. Environmental Science & Technology Letters, 2025,12(2):137-143.
[5] Hou R, Xu Y, Wang Z. Review of OPFRs in animals and humans: Absorption, bioaccumulation, metabolism, and internal exposure research [J]. Chemosphere, 2016,153:78-90.
[6] Van Den Eede N, Dirtu A C, Neels H, et al. Analytical developments and preliminary assessment of human exposure to organophosphate flame retardants from indoor dust [J]. Environment International, 2011, 37(2):454-461.
[7] Canbaz D, Logiantara A, Van ree R, et al. Immunotoxicity of organophosphate flame retardants TPHP and TDCIPP on murine dendritic cells in vitro [J]. Chemosphere, 2017,177:56-64.
[8] Godfrey A, Hooser B, Abdelmoneim A, et al. Thyroid disrupting effects of halogenated and next generation chemicals on the swim bladder development of zebrafish [J]. Aquatic Toxicology, 2017,193:228-235.
[9] 钟鸣宇.有机磷酸酯在黄渤海的环境分布及磷酸三(氯丙基)酯对紫贻贝(Mytilus galloprovincialis)的毒理效应 [D]. 烟台:中国科学院大学(中国科学院烟台海岸带研究所), 2018. Zhong M Y. Environmental distribution of organophosphate esters in the Bohai and Yellow Seas and the toxicological effects of tris- (chloropropyl) phosphate on mussel (Mytilus galloprovincialis) [D]. Yantai: University of Chinese Academy of Sciences(Yantai Institute of Coastal Zone Research), 2018.
[10] 张洛红,朱 钰,李宗睿,等.有机磷酸酯污染现状及其生物富集和生物转化研究进展 [J]. 环境化学, 2021,40(8):2355-2370. Zhang L H, Zhu Y, Li Z R, et al. Pollution status, bioaccumulation and biotransformation of organophosphate esters: A review. [J]. Environmental Chemistry, 2021,40(8):2355-2370.
[11] 何明靖,杨 婷,杨志豪,等.有机磷酸酯在三峡库区土壤中污染特征 [J]. 环境科学, 2017,38(12):5256-5261. He M J, Yan T, Yang Z H, et al. Occurrence of organophosphate esters in soils of the Three Gorges Reservoir [J]. Environmental Science, 2017,38(12):5256-5261.
[12] Wang Y, Yao Y, Li W, et al. A nationwide survey of 19organophosphate esters in soils from China: Spatial distribution and hazard assessment [J]. Science of the Total Environment, 2019,671:528-535.
[13] 王程强,钱 波,陆艳玫,等.阻燃剂TCPP暴露对小鼠的神经毒理作用观察及相关机制研究 [J]. 中国比较医学杂志, 2019,29(3):1-6. Wang C Q, Qian B, Lu Y M, et al. Neurotoxicity effects and mechanism of flame retardant TCPP exposure on of mice [J]. China Journal of Comparative Medicine, 2019,29(3):1-6.
[14] Zhong M, Wu H, Li F, et al. Proteomic analysis revealed gender- specific responses of mussels (Mytilus galloprovincialis) to trichloropropyl phosphate (TCPP) exposure [J]. Environmental Pollution, 2020,267.
[15] 皮天星,蔡磊明,蒋金花,等.新型阻燃剂TCPP对斑马鱼的毒性研究 [J]. 生态毒理学报, 2016,11(2):247-256. Pi T X, Cai L M, Jiang J H, et al. Toxicity effects of a new flame retardant tris(2-chloroisopropyl) phosphate to zebrafish (Danio rerio) [J]. Asian Journal of Ecotoxicology, 2016,11(2):247-256.
[16] 王晓南,刘征涛,王婉华,等.重金属铬(Ⅵ)的生态毒性及其土壤环境基准 [J]. 环境科学, 2014,35(8):3155-3161. Wang X N, Liu Z T, Wang W H, et al. Ecotoxicological effect and soil environmental criteria of the heavy metal Chromium(Ⅵ) [J]. Environmental Science, 2014,35(8):3155-3161.
[17] 陈丽红,刘征涛,方 征,等.老化土壤中铅对赤子爱胜蚓生长及繁殖的影响 [J]. 环境科学, 2014,35(4):1486-1490. Chen L H, Liu Z T, Fang T, et al. Effects of lead on the growth and reproduction of Eisenia fetida with aged soils [J]. Environmental Science, 2014,35(4):1486-1490.
[18] Xu J, Ke X, Krogh P H, et al. Evaluation of growth and reproduction as indicators of soil metal toxicity to the Collembolan, Sinella curviseta [J]. Insect Science, 2009,16(1):57-63.
[19] 郝 伟,姜 勇,李 琪,等.重金属铅、镉对矮小拟丽突线虫(Acrobeloides nanus)的亚急性毒性作用 [J]. 生态毒理学报, 2008, (2):139-143. Hao W, Jiang Y, Li Q, et al. Subacute toxic effects of lead and cadmium on the nematode acrobeloidesnanus [J]. Asian Journal ofEcotoxicology, 2008,(2):139-143.
[20] 王航洁,俞伟东.陆生无脊椎动物监测土壤重金属污染 [J]. 北方环境, 2011,23(5):119-120. Wang H J, Yu W D. The Research progress of terrestrial invertebrates monitoring soil heavy metal pollution [J]. Northern Environment, 2011,23(5):119-120.
[21] 刘 斌.磷酸三(2-氯丙基)酯和镉复合作用对蚯蚓的毒性研究 [D]. 泰安:山东农业大学, 2021. Liu B. Toxicity of tris (2-chloropropyl) phosphate and cadmium on earthworms [D]. Tai An: Shandong Agricultural University, 2021.
[22] GB 36600—2018 中华人民共和国生态环境部.土壤环境质量 建设用地土壤污染风险管控标准(试行) [S]. GB 36600—2018 Ministry of Ecology and Environment of the People's Republic of China. Soil environmental quality Risk control standard for soil contamination of development land [S].
[23] Zhou X, Qu M, Chen L, et al. The application of species sensitivity distribution (SSD) method in environmental risk assessment of pesticide [J]. Agrochemicals, 2017,56(11):786-90.
[24] Yang B, Yang H, Zhang C, et al. SSD Model selection method based on machine learning algorithm [J]. Journal of Physics: Conference Series, 2021:012082.
[25] Huang X, Li X, Zheng L, et al. Comprehensive assessment of health and ecological risk of cadmium in agricultural soils across China: A tiered framework [J]. Journal of Hazardous Materials, 2024,465.
[26] OECD. Guideline for testing of chemicals, NO. 208: Seeding emergence and seeding growth Test [S].
[27] OECD. Guidelines for the testing of chemicals, No. 207: Earthworm, acute toxicity tests [S].
[28] OECD. Guidelines for the Testing of Chemicals, No. 222: Earthworm Reproduction Test (Eisenia fetida/andrei) [S].
[29] 胡习邦,关晓彤,谢紫霞,等.农用地土壤中邻苯二甲酸二乙基已基酯的污染现状及生态风险评估 [J]. 生态环境学报, 2023,32(12): 2083-2093. Hu X B, Guan X T, Xie Z X, et al. Pollution status and ecological risk assessment of diethylhexyl phthalate in agricultural soil [J]. Ecology and Environmental Sciences, 32(12):2083-2093.
[30] Technical guidance document (TGD) on risk assessment of chemical substances (2nd edition) [R]. European Commission, European Chemical Bureau, Joint Research Centre, 2003.
[31] Vanvlaardingen Pla, Traastp, Wintersenam, et al. ETX2.0, a program to calculate hazardous concentrations and fraction affected,based on normally distributed toxicity data [R]. Bilthoven, B A: National Institute for Public Health and the Environment, 2004.
[32] Environment Agency(EA). Derivation and use of soil screening values for assessing ecological risk(Science Report share id26) [R]. Bristol: Environment Agency, 2017.
[33] HJ 831—2022 淡水水生生物水质基准推导技术指南 [S]. HJ 831—2022 Technical guideline for deriving water quality criteria for freshwater organisms [S].
[34] 施时迪,白 义,马勇军.重金属污染对土壤动物的毒性效应研究进展 [J]. 中国农学通报, 2010,26(14):288-293. Shi S D, Bai Y, Ma Y J. Research advances in heavy metal toxicity Effect to Soil Animals [J]. Chinese Agricultural Science Bulletin, 2010,26(14):288-293.
[35] Epa U. Ecological soil screening levels for lead [R]. Washington,D C: Office of Solid Waste and Emergency Response, 2005.
[36] European Commission. Identification and evaluation of data on flame retardants in consumer products. [R]. Belgium: European Commission Health & Consumers DG, 2011.
[37] 吴中平.氯代有机磷酸酯污染土壤的植物-微生物联合修复 [D]. 沈阳:沈阳大学, 2022. Wu Z P. Combined phyto-microbial remediation of chlorinated organophosphate contaminated soils [D]. Shen Yang: Shenyang University, 2022.
[38] 单 岳.土壤中有机磷酸酯的植物吸收积累规律研究 [D]. 沈阳:沈阳大学, 2020. Shan Y. Study on plant absorption and accumulation of organophosphates in soil [D]. Shen Yang: Shenyang University, 2020.
[39] Wang Y, Sun H W, Zhu H K, et al. Occurrence and distribution of organophosphate flame retardants (OPFRs) in soil and outdoor settled dust from a multi-waste recycling area in China [J]. Science of the Total Environment, 2018,625:1056-1064.
[40] Han B, Chen L, Li Y, et al. Spatial distribution and risk assessment of 11organophosphate flame retardants in soils from different regions of agricultural farmlands in China’s mainland [J]. Science of the Total Environment, 2022,842.
[41] Wang C, Yuan R Y, Wei S Q, et al. Occurrence, correlation, and partitioning of organophosphate esters in soil and tree bark from a megacity, Western China [J]. Environmental Science and Pollution Research, 2023,30(2):4359-4371.
[42] 杨志豪,何明靖,杨 婷,等.有机磷酸酯在重庆不同城市功能区土壤的分布特征及来源 [J]. 环境科学, 2018,39(11):5135-5141. Yang Z H, He M J, Yang T, et al. Occurrence and distribution of the organophosphate esters in soils of mixed land use area in Chongqing City [J]. Environmental Science, 2018,39(11):5135-5141.
[43] He M J, Yang T, Yang Z H, et al. Occurrence and distribution of organophosphate esters in surface soil and street dust from Chongqing, China: Implications for human exposure [J]. Archives of Environmental Contamination and Toxicology, 2017,73(3):349-361.
[44] Wang Y, Zhang Z H, Bao M J, et al. Characteristics and risk assessment of organophosphate esters and phthalates in soils and vegetation from Dalian, northeast China [J]. Environmental Pollution, 2021,284.
[45] Zhang Q, Wang Y X, Jiang X X, et al. Spatial occurrence and composition profile of organophosphate esters (OPEs) in farmland soils from different regions of China: Implications for human exposure [J]. Environmental Pollution, 2021,276.
[46] Cui K Y, Wen J X, Zeng F, et al. Occurrence and distribution of organophosphate esters in urban soils of the subtropical city, Guangzhou, China [J]. Chemosphere, 2017,175:514-520.
[47] Sun Y L, Zhu H K. A pilot study of organophosphate esters in surface soils collected from Jinan City, China: implications for risk assessments [J]. Environmental Science and Pollution Research, 2021, 28(3):3344-3353.
[48] 朱 彤.我国典型地区村镇水土环境中有机磷酸酯的污染特征、来源解析及生态风险 [D]. 重庆:重庆大学, 2022. Zhu T. Occurrence, source and ecological risks of organophosphate esters in the water and soil environment of villages in typical regions of China [D]. Chong Qing: Chongqing University, 2022.
[49] Tang J, Sun J, Ke Z, et al. Organophosphate esters in surface soils from a heavily urbanized region of Eastern China: Occurrence, distribution, and ecological risk assessment [J]. Environmental Pollution, 2021,291.
[50] 刘丽娅,印红玲,蹇林洁,等.青藏高原东缘冻土中有机磷酸酯的污染特征 [J]. 环境科学, 2021,42(7):3549-3554. Liu L Y, Yin H L, Jian L J, et al. Pollution characteristics of organophosphate esters in frozen soil on the eastern edge of Qinghai- Tibet Plateau [J]. Environmental Science, 2021,42(7):3549-3554.
[51] Luo Q, Gu L Y, Shan Y, et al. Human health risk assessment of organophosphate esters in urban topsoils of Shenyang, China [J]. Polish Journal of Environmental Studies, 2020,29(4):2731-2742.

基金

国家重点研发计划项目(2022YFC3703200)

PDF(1238 KB)

Accesses

Citation

Detail

段落导航
相关文章

/