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多环麝香和镉对小麦(Triticum aestivum)种子萌发和幼苗生长的生态毒理学效应。

Ecotoxicological effects of polycyclic musks and cadmium on seed germination and seedling growth of wheat (Triticum aestivum).

机构信息

Key Laboratory of Pollution Processes and Environmental Criteria, Ministry of Education/College of Environmental Science and Engineering, Nankai University, Tianjin 300071, China.

出版信息

J Environ Sci (China). 2010;22(12):1966-73. doi: 10.1016/s1001-0742(09)60347-8.

Abstract

Single and joint toxic effects of polycyclic musks including 1,3,4,6,7,8-hexahydro-4,6,6,6,7,8,8-hexamethylcyclopenta[g]-2-benzopyran (HHCB) and 7-acetyl-1,1,3,4,4,6-hexamethyl-l,2,3,4-tetrahydronapthalene (AHTN) and cadmium (Cd) on seed germination and seedling growth of wheat (Triticum aestivum) were investigated. The results showed that the toxicity sequence of HHCB toxic to wheat seed germination and seedling growth was similar to that of AHTN, that is, germination rate > shoot elongation > root elongation, while the toxicity of Cd was in the sequence of root elongation > shoot elongation > germination rate, according to the LC50 and EC50 values. It is suggested that polycyclic musks and Cd had different toxicological mechanisms. Root and shoot elongation of wheat might be good bioindicators for the contamination of polycyclic musks and Cd in soil. The mixture of polycyclic musks and Cd had synergistic effects on T. aestivum according to the equi-toxic mixture approach when root elongation was selected as the toxicological endpoint. Thus, the joint toxicity of HHCB and Cd was significantly higher than the single toxicity of HHCB or Cd, which was also confirmed by the EC50 mix value of the mixture (EC50 mix = 0.530 TUmix). The EC(50mix) value of the mixture of AHTN and Cd was 0.614 TUmix, which indicated that the mixture toxicity was strengthened when AHTN coexisted with Cd.

摘要

研究了多环麝香(包括 1,3,4,6,7,8-六氢-4,6,6,6,7,8,8-六甲基环戊[g]-2-苯并吡喃(HHCB)和 7-乙酰基-1,1,3,4,4,6-六甲基-1,2,3,4-四氢萘(AHTN)与镉(Cd)对小麦(Triticum aestivum)种子萌发和幼苗生长的单一和联合毒性效应。结果表明,HHCB 对小麦种子萌发和幼苗生长的毒性顺序与 AHTN 相似,即发芽率>芽伸长>根伸长,而 Cd 的毒性顺序为根伸长>芽伸长>发芽率,根据 LC50 和 EC50 值。这表明多环麝香和 Cd 具有不同的毒理学机制。小麦的根和芽伸长可能是土壤中多环麝香和 Cd 污染的良好生物标志物。根据等毒性混合物方法,当选择根伸长作为毒理学终点时,多环麝香和 Cd 的混合物对 T. aestivum 具有协同作用。因此,HHCB 和 Cd 的联合毒性明显高于 HHCB 或 Cd 的单一毒性,这也得到了混合物 EC50 mix 值(EC50 mix = 0.530 TUmix)的证实。AHTN 和 Cd 混合物的 EC(50mix)值为 0.614 TUmix,表明当 AHTN 与 Cd 共存时,混合物毒性增强。

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