基于不同测试终点的设施菜地土壤Cd与新污染物复合污染毒性阈值及预测模型

刘佳晓, 王萌, 孙晓艺, 俞磊, 王静, 周如烟, 秦璐瑶, 陈世宝

中国环境科学 ›› 2026, Vol. 46 ›› Issue (1) : 416-428.

PDF(2353 KB)
PDF(2353 KB)
中国环境科学 ›› 2026, Vol. 46 ›› Issue (1) : 416-428.
新污染物

基于不同测试终点的设施菜地土壤Cd与新污染物复合污染毒性阈值及预测模型

  • 刘佳晓, 王萌, 孙晓艺, 俞磊, 王静, 周如烟, 秦璐瑶, 陈世宝
作者信息 +

Toxicity thresholds and prediction models of combined pollution by cadmium and emerging contaminant in greenhousevegetable soils based on different test endpoints

  • LIU Jia-xiao, WANG Meng, SUN Xiao-yi, YU Lei, WANG Jing, ZHOU Ru-yan, QIN Lu-yao, CHEN Shi-bao
Author information +
文章历史 +

摘要

采用小白菜生长、赤子爱胜蚓生长和土壤微生物基质诱导呼吸(SIR)为毒性测试终点,对我国6种不同性质设施菜地土壤中Cd与四环素和吡虫啉单一及复合污染的毒性阈值(ECx)进行测定,并构建了污染物毒性与土壤主要影响因子间的量化关系及预测模型.结果表明:不同性质设施菜地土壤中污染物对不同测试终点的毒性剂量-效应关系呈现出明显的S型曲线,以小白菜为例,Cd的毒性阈值EC10为0.6~8.5,EC50为4.3~14.7mg/kg;Cd与四环素复合污染的毒性阈值EC10为0.1~2.2mg/kg,EC50为1.2~6.9mg/kg;Cd与吡虫啉复合污染的毒性阈值EC10为0.1~3.7mg/kg,EC50为1.4~10.0mg/kg;污染物毒性阈值在不同测试终点间呈较大差异,如Cd和四环素毒性阈值由大到小顺序依次为小白菜>蚯蚓>微生物,复合污染条件下的毒性阈值小于单一污染;小白菜生长对土壤污染物表现出低剂量刺激效应,最大刺激效应为103%~110%;pH值是影响和预测土壤中污染物毒性阈值的主控因子,基于土壤pH值、CEC、OC含量的归趋化预测模型可有效预测设施菜地土壤中Cd与新污染物复合污染的生态风险毒性阈值.

Abstract

Toxicity thresholds (ECx) forCd, and in combination with tetracycline and imidacloprid, were determined based onthe soils collected from six typical greenhouse vegetable farms in China. Three toxicity endpoints includingthe growth of Brassica napus, the growth of the red earthworm Aedes aegypti and the soil microbial substrate-induced respiration (SIR) were applied, and the quantitative relationships and prediction models were established between the toxicity of the pollutants and key soil properties. The results showed that the toxicity dose-effect relationships of the pollutantsacross different soils and test endpoints typically followed a distinct S-shaped curve. For example, the toxicity thresholds forCd alone on B. napuswere 0.6~8.5mg/kg (EC10) and 4.3~14.7mg/kg (EC50), respectively. For the combined pollution of Cd and tetracycline, the corresponding values were 0.1~2.2mg/kg (EC10) and 1.2~6.9mg/kg(EC50). For the combination of Cd and imidacloprid, the values were 0.1~3.7mg/kg (EC10) and 1.4~10.0mg/kg(EC50). The toxicity thresholds of pollutants varied significantlydepending on the test endpoints, e.g., the sensitivity order for Cd and tetracycline was Chinese cabbage > earthworm > microorganisms, the toxicity thresholds for the combined pollutants were consistently lower than those for the single pollutants, indicating a synergistic effect. Additionally, a low-dose stimulation effect (hormesis) on the growth of B. napus was observed, with a maximum stimulation rate of 103% to 110%. Soil pH was identified as the primary factor controlling and predicting the toxicity thresholds. A comprehensive prediction model based on soil pH, cation exchange capacity (CEC), and organic carbon (OC) content was developed, which can effectively predict the toxicity thresholds and assess the ecological risks associated with the combined pollution of Cd and emerging contaminants in greenhouse vegetable soils.

关键词

Cd / 复合污染 / 剂量-效应 / 低剂量毒物 / 刺激效应

Key words

Cadmium / emerging contaminants / toxicity thresholds / predicative modeling / hormesis

引用本文

导出引用
刘佳晓, 王萌, 孙晓艺, 俞磊, 王静, 周如烟, 秦璐瑶, 陈世宝. 基于不同测试终点的设施菜地土壤Cd与新污染物复合污染毒性阈值及预测模型[J]. 中国环境科学. 2026, 46(1): 416-428
LIU Jia-xiao, WANG Meng, SUN Xiao-yi, YU Lei, WANG Jing, ZHOU Ru-yan, QIN Lu-yao, CHEN Shi-bao. Toxicity thresholds and prediction models of combined pollution by cadmium and emerging contaminant in greenhousevegetable soils based on different test endpoints[J]. China Environmental Science. 2026, 46(1): 416-428
中图分类号: X53   

参考文献

[1] 黄标,胡文友,虞云龙,等.我国设施蔬菜产地土壤环境质量问题及管理对策[J]. 中国科学院院刊, 2015,30:449-457. Huang B, Hu W Y, Yu Y L, et al. Soil environmental quality problems and management countermeasures of facility vegetable production areas in China[J]. Proceedings of the Chinese Academy of Sciences, 2015,30:449-457.
[2] Wu X W, Cheng L Y, Cao Z Y, et al. Accumulation of chlorothalo-nil successively applied to soil and its effect on microbial activity in soil[J]. Ecotoxicology and Environmental Safety, 2012,81:65-69.
[3] Han M H, Fang H J, Wang Y P, et al. Pollution, human exposure and harmful effects of neonicotinoid pesticides[J]. Shanghai Journal of Preventive Medicine, 2021,33(6):534-543.
[4] GB2763-2021食品安全国家标准食品中农药最大残留限量[S]. GB2763-2021 National standard for food safety maximum residue limits for pesticides in food[S].
[5] Tao Y, Jia C H, Jing J J, et al. Occurrence and dietary riskassessment of 37 pesticides in wheat fields in the suburbs of Beijing, China[J]. Food Chemistry, 2021,350:129245.
[6] Li M, Yang L, Yen H, et al. Occurrence, spatial distribution and ecological risks of antibiotics in soil in urban agglomeration[J]. Journal of Environmental Sciences, 2023,125(3):678-690.
[7] HJ/T 333-2006温室蔬菜产地环境质量评价标准[S]. HJ/T 333-2006 Standard for evaluating the environmental quality of greenhouse vegetable production areas[S].
[8] GB2762-2022食品中污染物限量[S]. GB2762-2022 Limits of contaminants in food[S].
[9] 骆永明,滕应.中国土壤污染与修复科技研究进展和展望[J]. 土壤学报, 2020,57(5):1137-1142. LuoY M, Teng Y. Progress and prospects of research on soil pollution and remediation science and technology in China[J]. Journal of Soil Science, 2020,57(5):1137-1142.
[10] 马喆,王美娥,霍彦慧,等.场地土壤重金属镉和铅复合污染毒性阈值的推导及其应用[J]. 生态毒理学报, 2021,16(5):259-270. Ma Z, Wang M E, Huo Y H, et al. Derivation and application of toxicity thresholds for heavy metals Cd and Pb in site soils[J]. Journal of Ecotoxicology, 2021,16(5):259-270.
[11] 赵丹,吴畏达,孙倩,等.场地复合污染的生态效应与风险评估研究进展和展望[J]. 环境科学研究, 2023,36(1):30-43. Zhan D, WuW D, Sun Q, et al. Progress and prospects of ecological effects and risk assessment of complex site pollution[J]. Environmental Science Research, 2023,36(1):30-43.
[12] 戚与珊,张薇,刘鸣达,等.环丙沙星和铜复合污染对小麦早期生长的影响[J]. 生态学杂志, 2014,33(9):2376-2381. Qi Y S, Zhang W, Liu M D, et al. Effects of combined ciprofloxacin and copper contamination on early growth of wheat[J]. Journal of Ecology, 2014,33(9):2376-2381.
[13] Steevens J A, Benson W H. Toxicological interactions of chlorpyrifos and methyl mercury in the amphipod, Hyalella Azteca[J]. Toxicological Sciences, 1999,52(2):168-177.
[14] 王冰洁,姜蕾,潘波,等.Cu2+、Pb2+与2种除草剂单一及复合污染对蚯蚓的急性毒性[J]. 农药, 2020,59(6):425-429. Wang B J, Jiang L, Pan B, et al. Acute toxicity of Cu2+, Pb2+ and 2herbicides with single and combined contamination to earthworms[J]. Pesticide, 2020,59(6):425-429.
[15] 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. Ecotoxicity of heavy metal chromium (VI) and its soil environmental benchmark[J]. Environmental Science, 2014,35(8):3155-3161.
[16] 李泽姣,崔岩山,蔡晓琳,等.土壤铬污染对赤子爱胜蚓抗氧化酶活性的影响[J]. 中国科学院大学学报, 2020,37(1):20-26. Li Z J, Cui Y S, Cai X L, et al. Effects of soil chromium pollution on antioxidant enzyme activities of the earthworm Eisenia fetida[J]. Journal of University of Chinese Academy of Sciences, 2020,37(1): 20-26.
[17] Zhang X, Zhang X, L L, et al. The toxicity of hexa-valent chromium to soil microbial processes concerning soil properties and aging time[J]. Environmental Research, 2021:111941.
[18] Haanstra L, Doelman P, Voshaarjh O, et al. The use of sigmoidal dose response curves in soil ecotoxicological research[J]. Plantand Soil, 1985,84(2):293-297.
[19] 冯承莲,赵晓丽,侯红,等.中国环境基准理论与方法学研究进展及主要科学问题[J]. 生态毒理学报, 2015,10(1):16. Feng C L, Zhao X L, Hou H, et al. Research progress and major scientific issues of environmental benchmarking theory and methodology in China[J]. Journal of Ecotoxicology, 2015,10(1):16.
[20] 陈世宝,林蕾,魏威,等.基于不同测试终点的土壤锌毒性阈值及预测模型[J]. 中国环境科学, 2013,33(5):922-930. Chen S B, Lin L, Wei W, et al. Soil zinc toxicity thresholds and prediction models based on different test endpoints[J]. China Environmental Science, 2013,33(5):922-930.
[21] Qin L Y, Wang L F, Sun X Y, et al. Ecological toxicity (ECx) of Pb and its prediction models in Chinese soils with different physiochemical properties[J]. The Science of the Total Environment, 2022,853: 158769.
[22] 禹明慧,孟祥怀,段昌群,等.蚯蚓介导下镉胁迫对土壤理化性质和玉米生长的影响[J]. 环境化学, 2020,39(10):2654-2665. Yu M H, Meng X H, Duan C Q, et al. Effects of earthworm-mediated cadmium stress on soil physicochemical properties and maize growth[J]. Environmental Chemistry, 2020,39(10):2654-2665.
[23] 肖倩倩.几个灰飞虱P450基因的体外表达与对吡虫啉的代谢研究[D]. 南京:南京农业大学, 2019. Xiao Q Q. In vitro expression of P450gene and metabolism of imidacloprid in several grey ticks[D]. Nanjing: Nanjing Agricultural University, 2019.
[24] 张壬午,李治祥,白清云,等.化学农药对生态环境安全评价研究——Ⅱ.化学农药对蚯蚓的毒性与评价[J]. 农村生态环境, 1986, 2(2):14-18. Zhang R W, Li Z X, Bai Q Y, et al. Evaluation of chemical pesticides on ecological safety--II. Toxicity and evaluation of chemical pesticides on earthworms[J]. Rural Ecological Environment, 1986, 2(2):14-18.
[25] 谭曜,石守江,刘汉伟,等.吡虫啉对蚯蚓的急性毒性试验研究[J]. 检验检疫学刊, 2014,24(5):4-8. Tan Y, Shi S J, Liu H W, et al. Experimental study on the acute toxicity of imidacloprid to earthworms[J]. Journal of Inspection and Quarantine, 2014,24(5):4-8.
[26] 刘海龙.基于蚯蚓生物毒性的土壤Cd生态阈值研究[D]. 苏州:苏州科技学院, 2015. Liu H. L. Research on soil Cd ecological threshold based on earthworm biotoxicity[D]. Suzhou: Suzhou Institute of Science and Technology, 2015.
[27] 黄世聪,陈丽珂,张政杰,等.四环素对不同品种蔬菜毒性阈值及其敏感性分布[J]. 生态环境学报, 2023,32(11):1988-1995. Huang S C, Chen LK, Zhang ZJ, et al. Toxicity thresholds and sensitivity distribution of tetracycline in different vegetable species[J]. Journal of Ecology and Environment, 2023,32(11):1988-1995.
[28] Wu C A, He K B, Li H Z, et al. Transgenerational combined toxicity effects of neonicotinoids and triazole pesticides at environmentally relevant concentrations on D. magna: From individual to population level[J]. Journal of Hazardous Materials, 2025,486:137023.
[29] 万玉山,温馨,杨彦.四溴双酚A和镉复合污染对不同生物体的安全阈值[J]. 中国环境科学, 2019,39(4):1765-1775. Wan Y S, Wen X, Yang Y. Safety thresholds for tetrabromobisphenol A and cadmium combined contamination in different organisms[J]. China Environmental Science, 2019,39(4):1765-1775.
[30] Baguer A J, Jensen J, Krogh P H. et al. Effects of the antibiotics oxytetracycline and tylosin on soil fauna[J]. Chemosphere, 2000,40(7):751-757.
[31] 李通,金彩霞,朱雯斐,等.环丙沙星与Cu复合污染对玉米萝卜和小白菜3种作物生态毒性研究[J]. 农业环境科学学报, 2013,32(1): 15-20. Li T, Jin C X, Zhu W F, et al. Ecotoxicity of ciprofloxacin and Cu on three crops of maize, radish and cabbage[J]. Journal of Agricultural and Environmental Sciences, 2013,32(1):15-20.
[32] 赵文岩,黄卫丽,赵红梅,等.链霉素和铜单一及复合污染对蚯蚓的急性毒性研究[C]. 中国化学会第28届学术年会第2分会场摘要集,成都, 2012. Zhao W Y, Huang W L, Zhao H M, et al. Acute toxicity of streptomycin and copper to earthworms by single and combined contamination[C]. Abstracts of Session 2 of the 28 th Annual Meeting of the Chinese Chemical Society, Chengdu, 2012.
[33] 陈敏杰,钱懿宏,于青燕,等.典型四环素类抗生素对土壤微生物及植物生长的影响[J]. 生态毒理学报, 2019,14(6):276-283. Chen M J, Qian Y H, Yu Q Y, et al. Effects of typical tetracycline antibiotics on soil microorganisms and plant growth[J]. Journal of Ecotoxicology, 2019,14(6):276-283.
[34] 刘智敏,顾雪元,王晓蓉,等.化学提取法预测土壤中镉对蚯蚓的毒性效应[J]. 农业环境科学学报, 2013,32(10):1971-1978. Liu Z M, Gu X Y, Wang X R, et al. Prediction of toxic effects of cadmium in soil on earthworms by chemical extraction[J]. Journal of Agricultural and Environmental Sciences, 2013,32(10):1971-1978.
[35] 王萌,俞磊,秦璐瑶,等.土壤环境基准的科学问题与研究方法:以Cd为例[J]. 地学前缘, 2024,31(2):147-156. Wang M, Yu L, Qin L Y, et al. Scientific issues and research methods of soil environmental benchmarks: The case of Cd[J]. Geological Frontiers, 2024,31(2):147-156.
[36] ChenS, Meng W, LiS,etal. Overview on current criteria for heavy metals and its hint for the revision of soil environmental quality standards in China[J]. Journal of Integrative Agriculture, 2018,17(4): 765-774.
[37] Berry, Raymond, Giancarlo LM, et al.A Dose of Experimental Hormesis: When Mild Stress Protects and Improves Animal Performance.[J]. Comparative Biochemistry and Physiology Part A:Molecular and Integrative Physiology, 2020,242:110658.
[38] Belz, Regina G, Stephen O D, et al. Modelling biphasic hormetic dose responses to predict sub-NOAEL effects using plant biology as an example[J]. Current Opinion in Toxicology, 2022,29:36-42.
[39] Eze M O, Georgesc, Hoseg C, et al. Dose-response analysis of diesel fuel phytotoxicity on selected plant species[J]. Chemosphere, 2021, 263:128382.
[40] Ye J Y, Tian W T, Zhou M, et al. STOP1activates NRT1.1-mediated nitrate uptake to create a favorable rhizospheric pH for plant adaptation to acidity[J]. The Plant cell, 2021:3658-3674.
[41] 黄世聪,陈丽珂,张政杰,等.四环素对不同品种蔬菜毒性阈值及其敏感性分布[J]. 生态环境学报, 2023,32(11):1988-1995. Huang S C, Chen L K, Zhang Z J, et al. Toxicity thresholds and sensitivity distribution of tetracycline in different vegetable species[J]. Journal of Ecology and Environment, 2023,32(11):1988-1995.
[42] Calabrese E J, Agathokleous E, Kozumbo W J, et al. Estimating the range of the maximum hermetic stimulatory response[J]. Environmental Research, 2019,170:337-343.
[43] Zhang X, Lin Z. Hormesis-induced gap between the guidelines and reality in ecological risk assessment[J]. Chemosphere, 2019,243: 125348.
[44] 章海波,骆永明,李志博,等.土壤环境质量指导值与标准研究Ⅲ.污染土壤的生态风险评估[J]. 土壤学报, 2007,(2):338-349. Zhang H B, Luo Y M, Li Z B, et al. Study on guideline values and standards for soil environmental quality III. Ecological risk assessment of contaminated soils[J]. Journal of Soil Science, 2007,(2):338-349.
[45] 孙晓艺.基于生态风险的土壤中铬(Cr)环境质量基准(HC5)研究[D]. 北京:中国农业科学院, 2024. Sun X Y. Research on environmental quality benchmark (HC5) of chromium (Cr) in soil based on ecological risk[D]. Beijing: Chinese Academy of Agricultural Sciences, 2024.
[46] 宋文恩,陈世宝.基于水稻根伸长的不同土壤中镉(Cd)毒性阈值(ECx)及预测模型[J]. 中国农业科学, 2014,(17):3434-3443. Song W E, Chen S B. Cadmium (Cd) toxicity thresholds (ECx) and prediction models in different soils based on rice root elongation[J]. Chinese Agricultural Science, 2014,(17):3434-3443.
[47] Lin L, Zhu B, Qu X, et al. Are Ni-Cd toxicity models derived from simple bioassay applicable to natural soils? A bioassay-MSMs coupling approach[J]. Journal of Hazardous Materials, 2022,440: 129830.

基金

国家重点研发计划课题(2024YFD1700902,2023YFC3708703);中国农业科学院科技创新工程(CAAS-CSGLCA-202302)

PDF(2353 KB)

Accesses

Citation

Detail

段落导航
相关文章

/