无锡某地区土壤中有机氯农药污染状况调查

调查分析了无锡市某地区土壤有机氯农药污染状况。数据表明,该地区土壤有机氯农药主要残留组分为p,p＇-DDE和p,p’-DDT,其浓度处于较低水平,对生态环境和人类健康无显著危害。     

苏南某市春季蔬菜中农药残留调查

2003年3月对苏南某市蔬菜中有机氯、拟除虫菊酯及氨基甲酸酯类农药残留状况的调查结果表明:有机氯农药残留量较低,检出范围为ND～31.7μg·kg-1,蔬菜基地蔬菜中六六六类农药检出量高于传统菜地;蔬菜中滴滴涕类残留物主要组分为p,p′ DDE和p,p′ DDD。拟除虫菊酯类农药检出范围为ND～46.9μg·kg-1,检出量较高的是氯氰菊酯、氰戊菊酯、溴氰菊酯。氨基甲酸酯类农药检出范围为ND～111.9μg·kg-1,其中灭虫威和3-羟基克百威检出量和检出率最高,且蔬菜基地样品中的检出量低于传统菜地。蔬菜样品中克百威大部分已降解为3-羟基克百威,涕灭威、亚砜涕灭威与砜涕灭威检出量都很低,其中砜涕灭威平均检出量最低。供试区春季蔬菜中所检测的各种农药除克百威和涕灭威外,其余残留量均低于国家无公害蔬菜农药残留量标准。     

微生物降解蔬菜残留农药研究

从富集培养物中筛选到以甲胺磷为唯一碳源生长的菌株ＮＭＪ５和以乐果为唯一碳源生长的菌株ＮＭＬ３,经鉴定分别为芽孢杆菌属（Ｂａｃｉｌｕｓｓｐ．）和假单胞菌属（Ｐｓｅｕｄｏｍｏｎａｓｓｐ．）．它们利用甲胺磷、乐果生长的最适条件及在无机盐培养基中农药最大耐受浓度分别为ｐＨ７．５,ｔ＝３５℃,ρ＝１０００ｍｇ／Ｌ和ｐＨ７．５,ｔ＝３０℃,ρ＝２０００ｍｇ／Ｌ．在无碳基础培养基内单菌株培养８ｄ,５２４ｍｇ／Ｌ的甲胺磷好气降解４２．５％,厌气降解３５．９％,２５０ｍｇ／Ｌ的乐果好气降解５０．２％,厌气降解１６．４％．小区试验表明,ＮＭＪ５、ＮＭＬ３的菌液制剂对普通白菜的变种南农矮脚黄（Ｂｒａｓｉｃａｃａｍｐｅｓｔｒｉｓｓｐ．ｃｈｉｎｅｎｓｉｓＬ．ｖａｒ．ｃｏｍｍｕｎｉｓＴｓｅｎｅｔＬｅｅ）中残留的甲胺磷、乐果有明显的去除作用．     

甲胺磷对土壤中磷酸酶和脱氢酶活性的影响

报道了土壤中施入不同浓度有机磷杀虫剂甲胺磷（ｍｅｔｈａｍｉｄｏｐｈｏｓ）后对土壤磷酸酶和脱氢酶活性的影响。结果表明：甲胺磷对脱氢酶和３种磷酸酶的活性均有不同程度的抑制。其抑制强度和作用时间随浓度升高而加剧和延长，但随着时间的推移，这种抑制作用逐渐消失，并产生微弱的刺激效应。甲胺磷对土壤酸性磷酸酶活性的影响大于中性和碱性磷酸酶。初步讨论了酶活性与微生物生长的变化情况。     

珠三角地区POPs农药的污染现状及控制对策

概述了中国及国际社会对持久性有机污染物（Persistent Organic Pollutants,POPs）的关注情况。并通过对POPs农药在珠江三角洲地区（Pearl River Delta Area,PRD）使用情况的调查，以及对珠江三角洲地区POPs农药在各环境介质中的污染现状的文献综述，结合环境污染数据以及POPs农药污染调查工作中得到的数据和信息，对该地区POPs污染的可能原因和环境中可能存在的新近污染源进行了初步探讨。同时也指出了当前珠江三角洲地区在POPs农药削减与淘汰工作中所遭遇到的缺乏完善的管理体系等困难，并针对问题提出了包括加大科研投入，加强基础研究，掌握污染物来源和去向，加强替代药物的研究，建立和实施更严格的环境法规以及标准，加强环境监测能力建设，建立POPs农药污染的信息公开机制等一系列的控制对策。     

水中痕量有机磷农药的高效液相色谱/质谱分析

农药对饮用水以及饮用水源的污染在西方发达国家是一项极为关注的课题。有机磷农药作为农药中的一大类,至今仍是世界上生产和使用最多的农药品种。因此,饮用水以及饮用水源中痕量有机磷农药残留的状况受到人们关注。水中痕量有机磷农药的分析方法正在不断地改进,针对ＧＣ／ＭＳ测定某些有机磷农药时存在热分解以及在气相色谱柱上发生吸附的不足。结合高灵敏度、高选择性的质谱鉴定器,本文主要介绍最新的ＨＰＬＣ／ＡＰＩＭＳ方法在水中痕量有机磷农药测定方面的进展和应用。     

Assessment of the impact of pesticide residues on microbiological and biochemical parameters of tea garden soils in India

The main aim of this study was to assess the impact of pesticidal residues on soil microbial and biochemical parameters of the tea garden soils. The microbial biomass carbon (MBC), basal (BSR) and substrate induced respirations (SIR), β -glucosidase activity and fluorescein diacetate hydrolyzing activity (FDHA) of six tea garden soils, along with two adjacent forest soils (control) in West Bengal, India were measured. The biomass and its activities and biochemical parameters were generally lower in the tea garden soils than the control soils. The MBC of the soils ranged from 295.5 to 767.5 μ g g^{? 1}. The BSR and SIR ranged from 1.65 to 3.08 μ g CO₂-C g^{? 1} soil h^{? 1} and 3.08 to 10.76 μ g CO₂-C g^{? 1}h^{? 1} respectively. The β -glucosidase and FDHA of the soils varied from 33.3 and 76.3 μ g para-nitrophenol g^{? 1} soil h^{? 1} and 60.5 to 173.5 μ g fluorescein g^{? 1}h^{? 1}respectively. The tea garden soils contained variable residues of organophosphorus and organochlorine pesticides, which negatively affected the MBC, BSR, SIR, FDHA and β -glucosidase activity. Ethion and chlorpyriphos pesticide residues in all the tea garden soils varied from 5.00 to 527.8 ppb and 17.6 to 478.1 ppb respectively. The α endosulfan, β endosulfan and endosulfan sulfate pesticide residues in the tea garden soils ranged from 7.40 to 81.40 ppb, 8.50 to 256.1 ppb and 55 to 95.9 ppb respectively. Canonical correlation analysis shows that 93% of the total variation was associated with the negative impact of chlorpyriphos, β and α endosulfan and endosulfan sulfate on MBC, BSR and FDHA. At the same time ethion had negative impact on SIR and β -glucosidase. Data demonstrated that the pesticide residues had a strong impact on the microbial and biochemical components of soil quality.     

An alkaline phosphatase from Bacillus amyloliquefaciens YP6 of new application in biodegradation of five broad-spectrum organophosphorus pesticides

In recent decades, biodegradation has been considered a promising and eco-friendly way to eliminate organophosphorus pesticides (OPs) from the environment. To enrich current biodegrading-enzyme resources, an alkaline phosphatase (AP3) from Bacillus amyloliquefaciens YP6 was characterized and utilized to test the potential for new applications in the biodegradation of five broad-spectrum OPs. Characterization of AP3 demonstrated that activity was optimal at 40?°C and pH 10.3. The activity of AP3 was enhanced by Mg²⁺, Ca²⁺, and Cu²⁺, and strongly inhibited by Mn²⁺, EDTA, and L-Cys. Compared to disodium phenyl phosphate, p-nitrophenyl phosphate (pNPP) was more suitable to AP3, and the V_m, K_m, k_cat, k_cat/K_m values of AP3 for pNPP were 4,033?U mg^?1, 12.2?mmol L^?1, 3.3?×?10⁶ s^?1, and 2.7?×?10⁸ s^?1mol^?1L, respectively. Degradation of the five OPs, which included chlorpyrifos, dichlorvos, dipterex, phoxim, and triazophos, was 18.7%, 53.0%, 5.5%, 68.3%, and 96.3%, respectively, after treatment with AP3 for 1?h. After treatment of the OP for 8?h, AP3 activities remained more than 80%, with the exception of phoxim. It can be postulated that AP3 may have a broad OP-degradation ability and could possibly provide excellent potential for biodegradation and bioremediation in polluted ecosystems.     

Concentration and dissipation of chlorantraniliprole and thiamethoxam residues in maize straw,maize, and soil

To study the dissipation rates and final residual levels of chlorantraniliprole and thiamethoxam in maize straw, maize, and soil, two independent field trials were conducted during the 2014 cropping season in Beijing and Anhui Provinces of China. A 40% wettable powder (20% chlorantraniliprole?+?20% thiamethoxam) was sprayed onto maize straw and soil at an application rate of 118 g of active ingredient per hectare (g a.i.ha^?1). The residual concentrations were determined by ultra-high-performance liquid chromatography–tandem mass spectrometry. The chlorantraniliprole half-lives in maize straw and soil were 9.0–10.8 and 9.5–21.7 days, respectively. The thiamethoxam half-lives in maize straw and soil were 8.4–9.8 and 4.3–11.7 days, respectively. The final residues of chlorantraniliprole and thiamethoxam in maize straw, maize, and soil were measured after the pesticides had been sprayed two and three times with an interval of 7 days using 1 and 1.5 times the recommended rate (72 g a.i. ha^?1 and 108 g a.i. ha^?1, respectively). Representative maize straw, maize, and soil samples were collected after the last treatment at pre-harvest intervals of 7, 14, and 28 days. The chlorantraniliprole residue was below 0.01 mg kg^?1 in maize, between 0.01 and 0.31 mg kg^?1 in maize straw, and between 0.03 and 1.91 mg kg^?1 in soil. The thiamethoxam residue concentrations in maize, maize straw, and soil were <0.01, <0.01, and 0.01–0.03 mg kg^?1, respectively. The final pesticide residues on maize were lower than the maximum residue limit (MRL) of 0.02 mg kg^?1 after a 14-day pre-harvest interval. Therefore, a dosage of 72 g a.i. ha^?1 was recommended, as it can be considered safe to human beings and animals.     

含氮农药的好氧生物降解性能及废水治理对策

从动力学角度出发,利用长期驯化的菌种,对乙草胺,阿特拉津,西草净,赛克津等４种含氮农药的好氧生物降解性能进行了研究,并对含氮农药废水提出了治理对策,结果表明,４种含氮农药的好氧生物降解性能都很差,均属于难生物降解有机物,降解过程均符合一级降解动力学模式,它们的生物降解速率常数分别为０．００３５３Ｌ（ｇ．ｈ）,０．００５７７Ｌ／（ｇ．ｈ）,０．００１６０Ｌ／（ｇ．ｈ）,０。０４５６Ｌ／（ｇ．ｈ）进一