Gunasekara Amrith S, Troiano John, Goh Kean S, Tjeerdema Ronald S
Department of Environmental Toxicology, College of Agricultural and Environmental Sciences, One Shields Avenue, Meyer Hall, University of California, Davis 95616-8588, USA.
Rev Environ Contam Toxicol. 2007;189:1-23. doi: 10.1007/978-0-387-35368-5_1.
Simazine, first introduced in 1956, is a popular agricultural herbicide used to inhibit photosynthesis in broadleaf weeds and grasses. It is a member of the triazine family, and according to its physicochemical properties, it is slightly soluble in water, relatively nonvolatile, capable of partitioning into organic phases, and susceptible to photolysis. Sorption and desorption studies on its behavior in soils indicate that simazine does not appreciably sorb to minerals and has the potential to leach in clay and sandy soils. The presence of organic matter in soils contributes to simazine retention but delays its degradation. The primary sorptive mechanism of simazine to OM has been proposed to be via partitioning and/or by the interaction with functional groups of the sorbent. Farming practices directly influence the movement of simazine in soils as well. Tilled fields lower the runoff of simazine when compared to untilled fields, but tilling can also contribute to its movement into groundwater. Planting cover crops on untilled land can significantly reduce simazine runoff. Such practices are important because simazine and its byproducts have been detected in groundwater in The Netherlands, Denmark, and parts of the U.S. (California, North Carolina, Illinois, and Wisconsin) at significant concentrations. Concentrations have also been detected in surface waters around the U.S. and United Kingdom. Although the physicochemical properties of simazine do not support volatilization, residues have been found in the atmosphere and correlate with its application. Although at low concentrations, simazine has also been detected in precipitation in Pennsylvania (U.S.), Greece, and Paris (France). Abiotically, simazine can be oxidized to several degradation products. Although hydrolysis does not contribute to the dissipation of simazine, photolysis does. Microbial degradation is the primary means of simazine dissipation, but the process is relatively slow and kinetically controlled. Some bacteria and fungal species capable of utilizing simazine as a sole carbon and nitrogen source at a fast rate under laboratory conditions have been identified. Metabolism of simazine in higher organisms is via cytochrome P-450-mediated oxidation and glutathione conjugation.
西玛津于1956年首次推出,是一种常用的农业除草剂,用于抑制阔叶杂草和禾本科杂草的光合作用。它是三嗪家族的一员,根据其物理化学性质,它微溶于水,挥发性相对较低,能够分配到有机相中,并且易受光解作用影响。对其在土壤中行为的吸附和解吸研究表明,西玛津不会明显吸附到矿物质上,并且有可能在黏土和沙质土壤中淋溶。土壤中有机物的存在有助于西玛津的保留,但会延迟其降解。有人提出西玛津对有机物质的主要吸附机制是通过分配和/或与吸附剂官能团的相互作用。农业实践也直接影响西玛津在土壤中的移动。与未耕种的田地相比,耕种过的田地会降低西玛津的径流,但耕作也可能导致其进入地下水。在未耕种的土地上种植覆盖作物可以显著减少西玛津的径流。这些做法很重要,因为在荷兰、丹麦以及美国的部分地区(加利福尼亚州、北卡罗来纳州、伊利诺伊州和威斯康星州)的地下水中已检测到浓度显著的西玛津及其副产品。在美国和英国周边的地表水中也检测到了其浓度。尽管西玛津的物理化学性质不支持挥发,但在大气中发现了其残留物,并且与它的施用相关。尽管浓度较低,但在美国宾夕法尼亚州、希腊和法国巴黎的降水中也检测到了西玛津。在非生物条件下,西玛津可以氧化成几种降解产物。虽然水解对西玛津的消散没有作用,但光解有作用。微生物降解是西玛津消散的主要方式,但这个过程相对较慢且受动力学控制。已经鉴定出一些在实验室条件下能够快速利用西玛津作为唯一碳源和氮源 的细菌和真菌物种。高等生物中西玛津的代谢是通过细胞色素P - 450介导的氧化作用和谷胱甘肽结合作用。