Department of Pesticide Regulation, California Environmental Protection Agency, 1001 I Street, Sacramento, CA, 95812-4015, USA.
Rev Environ Contam Toxicol. 2013;223:107-40. doi: 10.1007/978-1-4614-5577-6_5.
Diazinon, first introduced in USA in 1956, is a broad-spectrum contact organophosphate pesticide that has been used as an insecticide, and nematicide. It has been ond of the most widely used insecticides in the USA for household and agricultural pest control. In 2004, residential use of diazinon was discontinued; as a result, the total amount applied has drastically decreased. [corrected]. Consequently, the amounts of diazinon applied have been drastically decreased. For example, in California, the amount of diazinon applied decreased from 501,784 kg in 2000 to 64,122 kg in 2010. Diazinon has a K(oc) value of 40-432 and is considered to be moderately mobile in soils. Diazinon residues have been detected in groundwater, drinking water wells, monitoring wells, and agricultural well. The highest detection frequencies and highest percentages of exceedance of the water quality criterion value of 0.1 μg/L have been reported from the top five agricultural counties n California that had the highest diazinon use. Diazinon is transported in air via atmospheric processes such as direct air movement and wet deposition in snow and rain, although concentrations decrease with distance and evaluation from the source. In the environment, diazinon undergoes degradation by several processes, the most important of which is microbial degradation in soils. The rate of diazinon degradation is affected by pH, soil type, organic amendments, soil moisture, and the concentration of diazinon in the soil, with soil pH being a major influencing factor in diazinon degradation rate. Studies indicate tha soil organic matter is the most important factor that influences diazinon sorption by soils, although clay content and soil ph also play an important role in diazinon sorption. Diazinon is very highly to moderately toxic aquatic arganisms, Diazinon inhibits the enzyme acetylcholinesterase, which hydrolyzes the neurotransmitter acetylcholine and leads to a suite of intermediate syndromes including anorexia, diarrhea, generalized weakness, muscle tremors, abnormal posturing and behavior, depression, and health. Differences in metabolism among species and exposure concentrations play a vital role in diazinon's bioaccumulation among different aquatic organisms in a wide range of accumulating rates and efficiencies.
敌敌畏于 1956 年首次在美国问世,是一种广谱接触有机磷杀虫剂,曾用作杀虫剂和杀线虫剂。它是美国用于家庭和农业害虫防治最广泛使用的杀虫剂之一。2004 年,停止了敌敌畏的住宅用途;因此,施用量急剧减少。[纠正]。因此,施用量大大减少。例如,在加利福尼亚州,敌敌畏的施用量从 2000 年的 501784 公斤减少到 2010 年的 64122 公斤。敌敌畏的 Koc 值为 40-432,被认为在土壤中具有中等移动性。敌敌畏残留已在地下水、饮用水井、监测井和农业井中检测到。在加利福尼亚州五个使用敌敌畏最多的农业县中,报告的最高检测频率和超过 0.1μg/L 水质标准值的最高百分比。敌敌畏通过大气过程如直接空气运动和雨雪中的湿沉降在空气中运输,尽管浓度随距离和来源评估而降低。在环境中,敌敌畏通过几种过程降解,其中最重要的是土壤中的微生物降解。敌敌畏的降解速度受 pH 值、土壤类型、有机改良剂、土壤湿度和土壤中敌敌畏的浓度影响,土壤 pH 值是影响敌敌畏降解速度的主要因素。研究表明,土壤有机质是影响土壤中敌敌畏吸附的最重要因素,尽管粘土含量和土壤 ph 值也在敌敌畏吸附中发挥重要作用。敌敌畏对水生有机物具有高度至中度毒性,敌敌畏抑制酶乙酰胆碱酯酶,水解神经递质乙酰胆碱,导致一系列中间综合征,包括厌食、腹泻、全身无力、肌肉震颤、姿势和行为异常、抑郁和健康。不同物种之间的代谢差异和暴露浓度在敌敌畏在广泛的积累率和效率范围内在不同水生生物中的生物积累中起着至关重要的作用。