贵阳市“两湖一库”周边蜘蛛体内镉含量及暴露风险
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摘要
调查了高镉地质背景区蜘蛛(肖蛸科、园蛛科、蟹蛛科和络新妇科)及其生境水体、土壤和植物中的镉含量,探讨了蜘蛛体内镉的来源、影响因子及存在风险。结果表明,研究区蜘蛛体内的平均镉含量为1. 82±1. 37μg/g(n=130),表现为园蛛科>肖蛸科>络新妇科≈蟹蛛科。蜘蛛体重与体内镉含量表现出弱的负相关关系(r=-0. 17,p=0. 08),暗示了蜘蛛生长发育过程中的生物稀释效应。狩猎型蟹蛛科和结网型园蛛科蜘蛛体内镉含量与对应土壤镉含量呈显著正相关关系(r=0. 61,0. 97),并且它们对土壤的生物富集因子均大于1,表明这两类蜘蛛可以用来指示土壤镉污染。生物有毒物质残留指数显示,研究区蜘蛛受高镉地质背景影响,体内存在着一定的镉暴露风险。
The cadmium concentrations in spiders( Tetragnathidae,Araneidae,Thomisidae,and Nephilidae) of a high cadmium geological background region and in their dwelling environment compartments( water,soils and plants) were investigated to discuss sources,influencing factors and exposure risks of cadmium in spiders. The results showed that cadmium concentrations in spiders followed a decreasing order of Araneidae > Tetragnathidae > Nephilidae ≈ Thomisidae,with an average of 1. 82 ± 1. 37 μg/g( n = 130).A weak negative correlation( r =-0. 17,p = 0. 08) between the cadmium concentration in spider and the weight of spider was observed,which may be resulted in the bio-dilution effect. Significant positive correlations( r = 0. 61,0. 97) between the cadmium concentration in soil and those in Thomisidae and Araneidae were observed. The bioaccumulation factors of cadmium in these two species were greater than 1,suggesting these two species could be selected as biomarkers for cadmium pollution in soil. The biological index for toxicant residues( β) indicated that the cadmium exposure risk of spiders in regions of the high geological background of cadmium should be noted.
The cadmium concentrations in spiders( Tetragnathidae,Araneidae,Thomisidae,and Nephilidae) of a high cadmium geological background region and in their dwelling environment compartments( water,soils and plants) were investigated to discuss sources,influencing factors and exposure risks of cadmium in spiders. The results showed that cadmium concentrations in spiders followed a decreasing order of Araneidae > Tetragnathidae > Nephilidae ≈ Thomisidae,with an average of 1. 82 ± 1. 37 μg/g( n = 130).A weak negative correlation( r =-0. 17,p = 0. 08) between the cadmium concentration in spider and the weight of spider was observed,which may be resulted in the bio-dilution effect. Significant positive correlations( r = 0. 61,0. 97) between the cadmium concentration in soil and those in Thomisidae and Araneidae were observed. The bioaccumulation factors of cadmium in these two species were greater than 1,suggesting these two species could be selected as biomarkers for cadmium pollution in soil. The biological index for toxicant residues( β) indicated that the cadmium exposure risk of spiders in regions of the high geological background of cadmium should be noted.
引文
[1] Pedersen S A,Kristiansen E,Andersen R A,et al. Cadmium is deposited in the gut content of larvae of the beetle Tenebrio molitor and involves a Cd-binding protein of the low cysteine type[J]. Comparative Biochemistry and Physiology Part C:Toxicology&Pharmacology,2008,148(3):217-222.
[2] Laing G D,Bogaert N,Tack F M G,et al. Heavy metal contents(Cd,Cu,Zn)in spiders(Pirata piraticus)living in intertidal sediments of the river Scheldt estuary(Belgium)as affected by substrate characteristics[J]. Science of the Total Environment,2002,289(1):71-81.
[3] Hendrickx F,Maelfait J P,Langenbick F. Absence of cadmium excretion and high assimilation result in cadmium biomagnification in a wolf spider[J]. Ecotoxicology and Environmental Safety,2003,55(3):287-292.
[4] Kammenga J E,Dallinger R,Donker M H,et al. Biomarkers in terrestrial invertebrates for ecotoxicological soil risk assessment[J]. Reviews of Environmental Contamination and Toxicology,2000,164(164):93-147.
[5] Wilczek G,Babczyńska A,Wilczek P,et al. Cellular stress reactions assessed by gender and species in spiders from areas variously polluted with heavy metals[J]. Ecotoxicology and Environmental Safety,2008,70(1):127-137.
[6] Jung M P,Lee J H. Bioaccumulation of heavy metals in the wolf spider,Pardosa astrigera L. Koch(Araneae:Lycosidae)[J]. Environmental Monitoring and Assessment,2012,184(3):1773-1779.
[7] Hunter B A,Johnson M S,Thompson D J. Ecotoxicology of copper and cadmium in a contaminated grassland ecosystem. II. Invertebrates[J].Journal of Applied Ecology,1987:587-599.
[8] Naef-Daenzer L,Naef-Daenzer B,Nager R G. Prey selection and foraging performance of breeding Great Tits Parus major in relation to food availability[J]. Journal of Avian Biology,2000,31(2):206-214.
[9]曾广铭,吉玉碧,谭红,等.贵州省农业土壤中镉的背景值研究[J].现代农业科技,2007(3):73-74.
[10]田林锋,胡继伟,罗桂林,等.贵州百花湖鱼体器官及肌肉组织中重金属的分布特征及其与水体重金属污染水平的相关性[J].水产学报,2012,36(5):714-722.
[11]张勇.贵州百花湖汞污染研究及污染控制成果浅析[D].太原:太原理工大学,2016.
[12]闫海鱼,冯新斌,刘霆,等.贵州百花湖鱼体汞污染现状[J].生态学杂志,2008,27(8):1357-1361.
[13]白薇扬,冯新斌,金志升,等.河流对阿哈水库汞迁移转化过程的影响[J].矿物学报,2007,27(2):218-224.
[14]何邵麟.贵州表生沉积物地球化学背景特征[J].贵州地质,1998,15(2):149-156.
[15]田林锋,胡继伟,罗桂林等.贵州百花湖沉积物重金属稳定性及潜在生态风险性研究[J].环境科学学报,2012,32(4):885-894.
[16]曾艳,张维,陈敬安,等.红枫湖入库河流沉积物中重金属污染状况分析[J].地球与环境,2010,38(4):470-475.
[17]梁莉莉,王中良,宋柳霆.贵阳市红枫湖水体悬浮物中重金属污染及潜在生态风险评价[J].矿物岩石地球化学通报,2008,27(2):119-125.
[18]李榜江,王龙昌,龙明忠,等.贵阳市花溪区煤矿废弃地重金属污染评价[J].贵州农业科学,2014(4):130-135.
[19]中华人民共和国国家卫生和计划生育委员会. GB 5009. 15-2014食品安全国家标准食品中镉的测定[S].北京:中国标准出版社,2015.
[20]中华人民共和国农业部. NY/T 1377-2007土壤pH的测定[S].北京:中国农业出版社,2007.
[21]中华人民共和国农业部. NY/T 1121. 6-2006土壤有机质的测定[S].北京:中国农业出版社,2006.
[22]张俊霞,朱明生,宋大祥.肖蛸科蜘蛛的捕食行为[J].蛛形学报,2002,11(1):61-64.
[23]孟祥伟.花蟹蛛属(蜘蛛目:蟹蛛科)的分类学探究[D].南充:西华师范大学,2015.
[24]陆引罡,王巩.贵州贵阳市郊区菜园土壤重金属污染的初步调查[J].土壤通报,2001,32(5):235-237.
[25] Ramirez M G,Mc Callum J E B,Landry J M,et al. Relationships between physiological characteristics and trace metal body burdens of banded garden spiders Argiope trifasciata(Araneae,Araneidae)[J]. Ecotoxicology and Environmental Safety,2011,74(4):1081-1088.
[26]赵敬钊.温度对蜘蛛个体发育的影响[J].蛛形学报,2001,10(1):58-64.
[27]郭胜涛.中国园蛛属分类研究(蜘蛛目:圆蛛科)[D].保定:河北大学,2011.
[28] Yoshida M. Predatory behavior of three Japanese species of Metleucauge(Araneae,Tetragnathidae)[J]. Journal of Arachnology,1989,17(1):15-25.
[29] Yoshida M. Predatory behavior of Leucauge magnifica(Araneae:Tetragnathidae)[J]. Acta Arachnologica,2000,49(2):117-123.
[30] Robinson M H,Robinson B C. Ecology and behavior of the giant wood spider Nephila maculata(Fabricius)in New Guinea[J]. Smithsonion Libraries,1973,149(149):1-76.
[31] Migula P,Wilczek G,Babczyńska A. Effects of heavy metal contamination[M]. Heidelerg:Springer,2013:403-414.
[32] Klaassen C D,Liu J,Choudhuri S. Metallothionein:an intracellular protein to protect against cadmium toxicity[J]. Annual Review of Pharmacology and Toxicology,1999,39(1):267-294.
[33] Babczyńska A,Wilczek G,Wilczek P,et al. Metallothioneins and energy budget indices in cadmium and copper exposed spiders Agelena labyrinthica in relation to their developmental stage,gender and origin[J]. Comparative Biochemistry&Physiology Toxicology&Pharmacology Cbp,2011,154(3):161-171.
[34] Van Straalen N M,Krivolutsky,D A. Critical body concentrations:their use in bioindication[A]. In Bioindicator systems for soil pollution[M].Dordrecht:Kluwer Academic Publishers,1996:5-16.
[35] Jung M P,Kim H,Kim S T,et al. Risk analysis of heavy metal contaminated habitats using a wolf spider,Pardosa astrigera(Araneae:Lycosidae)[C]. Environment Health Risk,2007.
[36] Babczyńska A,Migula P. Cadmium-fenitrothion interaction in the spider pardosa lugubris and the fruit fly drosophila melanogaster[J]. Bulletin of Environmental Contamination&Toxicology,2002,69(4):586-592.
[2] Laing G D,Bogaert N,Tack F M G,et al. Heavy metal contents(Cd,Cu,Zn)in spiders(Pirata piraticus)living in intertidal sediments of the river Scheldt estuary(Belgium)as affected by substrate characteristics[J]. Science of the Total Environment,2002,289(1):71-81.
[3] Hendrickx F,Maelfait J P,Langenbick F. Absence of cadmium excretion and high assimilation result in cadmium biomagnification in a wolf spider[J]. Ecotoxicology and Environmental Safety,2003,55(3):287-292.
[4] Kammenga J E,Dallinger R,Donker M H,et al. Biomarkers in terrestrial invertebrates for ecotoxicological soil risk assessment[J]. Reviews of Environmental Contamination and Toxicology,2000,164(164):93-147.
[5] Wilczek G,Babczyńska A,Wilczek P,et al. Cellular stress reactions assessed by gender and species in spiders from areas variously polluted with heavy metals[J]. Ecotoxicology and Environmental Safety,2008,70(1):127-137.
[6] Jung M P,Lee J H. Bioaccumulation of heavy metals in the wolf spider,Pardosa astrigera L. Koch(Araneae:Lycosidae)[J]. Environmental Monitoring and Assessment,2012,184(3):1773-1779.
[7] Hunter B A,Johnson M S,Thompson D J. Ecotoxicology of copper and cadmium in a contaminated grassland ecosystem. II. Invertebrates[J].Journal of Applied Ecology,1987:587-599.
[8] Naef-Daenzer L,Naef-Daenzer B,Nager R G. Prey selection and foraging performance of breeding Great Tits Parus major in relation to food availability[J]. Journal of Avian Biology,2000,31(2):206-214.
[9]曾广铭,吉玉碧,谭红,等.贵州省农业土壤中镉的背景值研究[J].现代农业科技,2007(3):73-74.
[10]田林锋,胡继伟,罗桂林,等.贵州百花湖鱼体器官及肌肉组织中重金属的分布特征及其与水体重金属污染水平的相关性[J].水产学报,2012,36(5):714-722.
[11]张勇.贵州百花湖汞污染研究及污染控制成果浅析[D].太原:太原理工大学,2016.
[12]闫海鱼,冯新斌,刘霆,等.贵州百花湖鱼体汞污染现状[J].生态学杂志,2008,27(8):1357-1361.
[13]白薇扬,冯新斌,金志升,等.河流对阿哈水库汞迁移转化过程的影响[J].矿物学报,2007,27(2):218-224.
[14]何邵麟.贵州表生沉积物地球化学背景特征[J].贵州地质,1998,15(2):149-156.
[15]田林锋,胡继伟,罗桂林等.贵州百花湖沉积物重金属稳定性及潜在生态风险性研究[J].环境科学学报,2012,32(4):885-894.
[16]曾艳,张维,陈敬安,等.红枫湖入库河流沉积物中重金属污染状况分析[J].地球与环境,2010,38(4):470-475.
[17]梁莉莉,王中良,宋柳霆.贵阳市红枫湖水体悬浮物中重金属污染及潜在生态风险评价[J].矿物岩石地球化学通报,2008,27(2):119-125.
[18]李榜江,王龙昌,龙明忠,等.贵阳市花溪区煤矿废弃地重金属污染评价[J].贵州农业科学,2014(4):130-135.
[19]中华人民共和国国家卫生和计划生育委员会. GB 5009. 15-2014食品安全国家标准食品中镉的测定[S].北京:中国标准出版社,2015.
[20]中华人民共和国农业部. NY/T 1377-2007土壤pH的测定[S].北京:中国农业出版社,2007.
[21]中华人民共和国农业部. NY/T 1121. 6-2006土壤有机质的测定[S].北京:中国农业出版社,2006.
[22]张俊霞,朱明生,宋大祥.肖蛸科蜘蛛的捕食行为[J].蛛形学报,2002,11(1):61-64.
[23]孟祥伟.花蟹蛛属(蜘蛛目:蟹蛛科)的分类学探究[D].南充:西华师范大学,2015.
[24]陆引罡,王巩.贵州贵阳市郊区菜园土壤重金属污染的初步调查[J].土壤通报,2001,32(5):235-237.
[25] Ramirez M G,Mc Callum J E B,Landry J M,et al. Relationships between physiological characteristics and trace metal body burdens of banded garden spiders Argiope trifasciata(Araneae,Araneidae)[J]. Ecotoxicology and Environmental Safety,2011,74(4):1081-1088.
[26]赵敬钊.温度对蜘蛛个体发育的影响[J].蛛形学报,2001,10(1):58-64.
[27]郭胜涛.中国园蛛属分类研究(蜘蛛目:圆蛛科)[D].保定:河北大学,2011.
[28] Yoshida M. Predatory behavior of three Japanese species of Metleucauge(Araneae,Tetragnathidae)[J]. Journal of Arachnology,1989,17(1):15-25.
[29] Yoshida M. Predatory behavior of Leucauge magnifica(Araneae:Tetragnathidae)[J]. Acta Arachnologica,2000,49(2):117-123.
[30] Robinson M H,Robinson B C. Ecology and behavior of the giant wood spider Nephila maculata(Fabricius)in New Guinea[J]. Smithsonion Libraries,1973,149(149):1-76.
[31] Migula P,Wilczek G,Babczyńska A. Effects of heavy metal contamination[M]. Heidelerg:Springer,2013:403-414.
[32] Klaassen C D,Liu J,Choudhuri S. Metallothionein:an intracellular protein to protect against cadmium toxicity[J]. Annual Review of Pharmacology and Toxicology,1999,39(1):267-294.
[33] Babczyńska A,Wilczek G,Wilczek P,et al. Metallothioneins and energy budget indices in cadmium and copper exposed spiders Agelena labyrinthica in relation to their developmental stage,gender and origin[J]. Comparative Biochemistry&Physiology Toxicology&Pharmacology Cbp,2011,154(3):161-171.
[34] Van Straalen N M,Krivolutsky,D A. Critical body concentrations:their use in bioindication[A]. In Bioindicator systems for soil pollution[M].Dordrecht:Kluwer Academic Publishers,1996:5-16.
[35] Jung M P,Kim H,Kim S T,et al. Risk analysis of heavy metal contaminated habitats using a wolf spider,Pardosa astrigera(Araneae:Lycosidae)[C]. Environment Health Risk,2007.
[36] Babczyńska A,Migula P. Cadmium-fenitrothion interaction in the spider pardosa lugubris and the fruit fly drosophila melanogaster[J]. Bulletin of Environmental Contamination&Toxicology,2002,69(4):586-592.
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