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首页> 外文期刊>QSAR & combinatorial science >Quantitative Structure Activity Relationships for Predicting the Bioaccumulation of POPs in Terrestrial Food-Webs
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Quantitative Structure Activity Relationships for Predicting the Bioaccumulation of POPs in Terrestrial Food-Webs

机译:定量结构活动关系预测陆地食物网中持久性有机污染物的生物累积

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摘要

K_(ow) based QSARs are used to assess the bioaccumulation potential of thousands of commercial chemicals in Canada and internationally. The QSARs, which are based on information from aquatic organisms, identify chemicals with a log K_(ow) > 5 to have a potential to biomagnify in food-chains. This study investigates whether K_(ow) based QSARs are also effective in identifying biomagnifying chemicals in terrestrial food-chains. First, a terrestrial bioaccumulation model is developed and used to hypothesize the general relationship between the chemical's octanol-air and octanol-water partition and its biomagni-fication potential. Secondly, field observations of the bioaccumulation of persistent organic pollutants in wolves are used to test the hypothesis and explore the fundamental differences between QSARs for bioaccumulation in aquatic and terrestrial food-chains. The results indicate that (i) QSARs for bioaccumulation in terrestrial food-chains should include both octanol-air (K_(OA)) and octanol water partition coefficients (K_(ow)); (ii) chemicals with a log K_(OA) > approximately 5 can biomagnify in terrestrial food-chains if log KOW > 2 and the rate chemical transformation or metabolism is low; (iii) biomagnification factors in terrestrial food-chains are much greater than those in aquatic food-chains; (iv) biomagnification factors of very hydrophobic substances (log K_(ow) > 7) in terrestrial biota do not drop off with increasing K_(ow) as has been observed in aquatic biota. The relevance of these findings is that current regulations and protocols may misidentify (i) low KOW but high K_(OA) chemicals as having no bioaccumulation potential and (ii) very hydrophobic (log K_(ow) > 8.5) which appear not to biomagnify in aquatic organisms but have the potential to biomagnify in terrestrial food-chains. Considering that 67.9% of the approximately 12000 organic chemicals on Canada's Domestic Substances List exhibit high K_(OA) but low K_(ow), this represents a major gap in our methods for screening bioaccumulative substances.
机译:基于K_(ow)的QSAR用于评估加拿大和国际上数千种商业化学品的生物蓄积潜力。 QSAR基于水生生物的信息,识别出log K_(ow)> 5的化学物质具有在食物链中生物放大的潜力。这项研究调查了基于K_(ow)的QSAR在识别陆地食物链中的生物放大化学品方面是否也有效。首先,建立了陆地生物积累模型,并用来假设该化学物质的辛醇-空气和辛醇-水分配与其生物放大潜力之间的一般关系。其次,对狼中持久性有机污染物生物蓄积的实地观察用于检验假设,并探索QSAR在水生和陆地食物链中生物蓄积的基本差异。结果表明:(i)地面食物链中生物富集的QSAR应同时包括辛醇空气(K_(OA))和辛醇水分配系数(K_(ow)); (ii)如果log KOW> 2且化学转化或新陈代谢率低,则log K_(OA)> 5左右的化学物质可以在陆地食物链中生物放大; (iii)陆地食物链中的生物放大因子远大于水生食物链中的生物放大因子; (iv)陆生生物区中非常疏水的物质(log K_(ow)> 7)的生物放大系数不会随着水生生物区中K_(ow)的增加而下降。这些发现的相关性在于,当前的法规和协议可能会误认为(i)低KOW但高K_(OA)化学品无生物蓄积潜力,并且(ii)疏水性很强(log K_(ow)> 8.5),似乎无法生物放大在水生生物中存在,但有可能在陆地食物链中生物放大。考虑到加拿大国内物质清单中约12,000种有机化学品中有67.9%的K_(OA)高但K_(ow)低,这代表了我们筛选生物蓄积性物质的方法中的一个主要空白。

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