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拟除虫菊酯的物理和化学性质。

Physical and chemical properties of pyrethroids.

作者信息

Laskowski Dennis A

机构信息

D.A. Laskowski Consulting, 4600 Hickory Court, Zionsville, IN 46077, USA.

出版信息

Rev Environ Contam Toxicol. 2002;174:49-170. doi: 10.1007/978-1-4757-4260-2_3.

Abstract

The physical and chemical properties of the pyrethroids bifenthrin, cyfluthrin, cypermethrin (also zetacypermethrin), deltamethrin, esfenvalerate (also fenvalerate), fenpropathrin, lambda-cyhalothrin (also cyhalothrin), permethrin, and tralomethrin have been reviewed and summarized in this paper. Physical properties included molecular weight, octanol-water partition coefficient, vapor pressure, water solubility, Henry's law constant, fish biocencentration factor, and soil sorption, desorption, and Freundlich coefficients. Chemical properties included rates of degradation in water as a result of hydrolysis, photodecomposition, aerobic or anaerobic degradation by microorganisms in the absence of light, and also rates of degradation in soil incubated under aerobic or anaerobic conditions. Collectively, the pyrethroids display a highly nonpolar nature of low water solubility, low volatility, high octanol-water partition coefficients, and have high affinity for soil and sediment particulate matter. Pyrethroids have low mobility in soil and are sorbed strongly to the sediments of natural water systems. Although attracted to living organisms because of their nonpolar nature, their capability to bioconcentrate is mitigated by their metabolism and subsequent elimination by the organisms. In fish, bioconcentration factors (BCF) ranged from 360 and 6000. Pyrethroids in water solution tend to be stable at acid and neutral pH but [table: see text] become increasingly susceptible to hydrolysis at pH values beyond neutral. Exceptions at higher pH are bifenthrin (stable), esfenvalerate (stable), and permethrin (half-life, 240 d). Pyrethroids vary in susceptibility to sunlight. Cyfluthrin and tralomethrin in water had half-lives of 0.67 and 2.5 d; lambda-cyhalothrin, esfenvalerate, deltamethrin, permethrin, and cypermethrin were intermediate with a range of 17-110 d; and bifenthrin and fenpropathrin showed the least susceptibility with half-lives of 400 and 600 d, respectively. Pyrethroids on soil can also undergo photolysis, often at rates similar to that in water. Half-lives ranged from 5 to 170 d. [table: see text] Pyrethroids are degradable in soils with half-lives ranging from 3 to 96 d aerobically, and 5 to 430 d anaerobically. For those pyrethroids studied in water (cypermethrin, deltamethrin, esfenvalerate, fenpropathrin, and lambda-cyhalothrin), aerobic and anaerobic degradation often continued at rates similar to that displayed in soil.

摘要

本文对拟除虫菊酯类杀虫剂联苯菊酯、氟氯氰菊酯、氯氰菊酯(也叫高效氯氰菊酯)、溴氰菊酯、乙氰菊酯(也叫氰戊菊酯)、甲氰菊酯、高效氯氟氰菊酯(也叫氯氟氰菊酯)、氯菊酯和四溴菊酯的物理化学性质进行了综述和总结。物理性质包括分子量、正辛醇 - 水分配系数、蒸气压、水溶性、亨利定律常数、鱼类生物富集因子以及土壤吸附、解吸和弗罗因德利希系数。化学性质包括在水中因水解、光解、在无光条件下微生物的好氧或厌氧降解而导致的降解速率,以及在好氧或厌氧条件下培养的土壤中的降解速率。总体而言,拟除虫菊酯类呈现出高度非极性的性质,水溶性低、挥发性低、正辛醇 - 水分配系数高,并且对土壤和沉积物颗粒物具有高亲和力。拟除虫菊酯在土壤中迁移性低,并且强烈吸附于天然水系统的沉积物中。尽管由于其非极性性质而对生物体有吸引力,但其生物富集能力会因生物体的代谢和随后的消除而减弱。在鱼类中,生物富集因子(BCF)范围为360至6000。水溶液中的拟除虫菊酯在酸性和中性pH值下往往是稳定的,但在pH值超过中性时变得越来越容易水解。在较高pH值下的例外情况是联苯菊酯(稳定)、乙氰菊酯(稳定)和氯菊酯(半衰期为240天)。拟除虫菊酯对阳光的敏感性各不相同。水中的氟氯氰菊酯和四溴菊酯的半衰期分别为0.67天和2.5天;高效氯氟氰菊酯、乙氰菊酯、溴氰菊酯、氯菊酯和氯氰菊酯处于中间水平,半衰期范围为17至110天;而联苯菊酯和甲氰菊酯的敏感性最低,半衰期分别为400天和600天。土壤中的拟除虫菊酯也会发生光解,其速率通常与水中相似。半衰期范围为5至170天。拟除虫菊酯在土壤中可降解,好氧条件下半衰期为3至96天,厌氧条件下半衰期为5至430天。对于在水中研究的那些拟除虫菊酯(氯氰菊酯、溴氰菊酯、乙氰菊酯、甲氰菊酯和高效氯氟氰菊酯),好氧和厌氧降解速率通常与在土壤中显示的速率相似。

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