蔬菜上低残留农药的选择及其安全使用

经试验示范,筛选出供蔬菜上使用的32种高效、低毒、低残留农药,并制定了30种农药的安全间隔期。     

不同种植方式蔬菜中农药残留的差异及污染控制研究

采集了陕西地区不同种植方式的瓜果类、叶菜类蔬菜样品,研究了其中各种农药的残留情况,并分析了农药残留对环境的污染及其控制措施。结果表明:露地种植蔬菜与设施种植蔬菜相比,无论是农药残留检出率还是超标率都略高,两者的农药残留检出率分别为42.0%、36.5%,超标率分别为12.0%、8.2%;叶菜类蔬菜与瓜果类蔬菜相比,无论是农药残留检出率还是超标率都较高,两者的农药残留检出率分别为52.6%、29.6%,超标率分别为17.3%、5.4%;设施种植的瓜果类蔬菜和叶菜类蔬菜的农药残留检出率基本接近,而叶菜类蔬菜的农药残留超标率明显高于瓜果类蔬菜,露地种植的叶菜类蔬菜的农药残留检出率和超标率都远高于瓜果类蔬菜;设施种植蔬菜与露地种植蔬菜相比,甲胺磷、对硫磷、甲基对硫磷、毒死蜱、三氟氯氰菊酯和氰戊菊酯的残留检出率更高;瓜果类蔬菜与叶菜类蔬菜相比,毒死蜱、甲氰菊酯、三氟氯氰菊酯、氰戊菊酯的残留检出率更高;叶菜类蔬菜的农药施用浓度较高,施用农药后要间隔一定时间后再上市销售,并应采用更科学的施药方式,以减少农药在蔬菜中的残留和降低对环境的危害;一方面要开发并积极倡导使用高效、低毒、低残留的无公害农药,另一方面则要开发能够高效、快速降解残留农药的物质,同时还要进行农产品的清洁生产,以提高农产品的安全性,并降低环境中农药的残留危害。     

有机磷农药残留检测技术研究进展

综述了近年来有机磷农药残留检测技术的研究进展,其检测方法主要有色谱法、降解酶法、化学发光技术和生物传感技术.详细介绍了几种生物传感器(如酶传感器、微生物传感器、免疫传感器、压电传感器、纳米传感器和液晶型化学传感器)在有机磷农药检测中的应用,并展望了这一领域的发展趋势.     

城市污水处理厂不同工艺段中有机氯农药残留

建立了基于HLB固相萃取柱和气相色谱／电子捕获(IGC／ECD)分析城市污水中有机氯农药的分析方法，同时分析了北京市高碑店和北小河两个污水处理厂中4个不同工艺段水体中有机氯农药的浓度。在两个污水处理厂的水体中共检出了6种有机氯类农药，分别是α—六六六、β—六六六、γ—六六六、δ—六六六、艾氏剂和4，4′—滴滴滴，浓度在1．89—69．6ng／L之间。结果表明，曝气活性污泥法对六六六类有机氯农药的去除效果较好。     

百菌清农药残留的SPE-GC检测

对环境水样中百菌清农药残留进行了SPE-GC分析方法研究。环境水样通过Florisil柱富集、净化,3 mL乙酸乙酯洗脱,GC-ECD进行分析检测。实验表明,百菌清农药残留在0.01~10 mg/L范围内线性关系良好,相关系数为0.9993。外标法定量,检出限为0.0035 mg/L,对实际水样进行加标回收,回收率范围在93.47%~100.14%之间,6次重复测定相对标准偏差在3.97%~4.96%之间,并将方法应用于周边环境地表水的检测。该方法具有简便,快速,准确,灵敏度高等特点,能满足环境水样中农药残留分析要求。     

流动注射免疫分析及其在环境中农药残留分析研究综述

介绍了流动注射免疫分析、顺序流动注射免疫分析方法及其流动注射脂质体、荧光、化学发光、电化学等检测技术分析环境中的农药残留。     

农药残留速测技术研究进展

本文综述了国内外农药快速检测技术的研究状况。在速测技术中,色－质联用分析法已发展得比较成熟,所得结果比较可靠,但该法的测定时间仍较长;免疫分析法具有简单、快速、价廉、特异性高、需样品量少等优点;生物传感器法更方便 、快捷。     

舟山近岸海域贝类中有机氯农药残留水平及人体健康风险评估

于2012年的7月在舟山群岛新区的海域采集贝类样本,测定了其中的有机氯农药残留量,并进行了人体健康风险评估和安全食用量推算。结果表明,采集的5种贝类样本中,六六六(BHCs)的各组分均未被检出,而滴滴涕(DDTs)在各种样本中均有检出,其中僧帽牡蛎和部分縊蛏样本中DDTs总量超过《海洋生物质量标准》(GB 18421—2001)一类标准(10μg/kg);健康风险评估结果显示,贝类样本中α-BHC、β-BHC、γ-BHC、p,p’-滴滴伊(p,p’-DDE)、p,p’-滴滴滴(p,p’-DDD)、p,p’-DDT的总致癌风险指数均低于10-4,致癌风险均在可接受的安全范围,α-BHC、β-BHC、γ-BHC、p,p’-DDE的总接触风险指数均小于1,接触风险指数未超过危害剂量参考值,人体食用舟山近岸海域的贝类是安全的;按可接受的致癌风险指数进行评估,人体的贝类安全消费量为9.8~138.0g/(kg·d)(按体重计,下同),而按可接受的接触风险指数进行评估,人体的贝类安全消费量在24.6~235.0g/(kg·d)。     

农药残留的酶联免疫检测技术研究进展

简要介绍了农药残留的酶联免疫分析的技术原理,关键技术环节,综述了国内外的酶联免疫测定农药残留的研究动态,并展望了此技术的发展及应用前景。     

固相萃取毛细管气相色谱法分析水中有机磷农药残留

探索了采用固相萃取对样品进行提取富集，以及配备氮磷检测器的毛细管气相色谱(CGC)法分析水中有机磷农药痕量残留的方法。结果表明：敌敌畏、内吸磷、乐果、甲基对硫磷、马拉硫磷和对硫磷等6种农药在20min内有较好的分离；3个不同浓度的标准添加，其回收率范围为52．1％～93．7％，最低检出限范围为1．11～5．21ng／L；同时利用该方法分析太湖梅梁湾水源地和长江沿岸水厂取水口水质，6种有机磷农药均有一定程度检出，但仍未超出集中水源地供水标准。     

The study of heptenophos and triazophos residues in vegetables treated with the organophosphorus insecticides Hostaquick and Hostathion

The residues of heptenophos and triazophos (active components of Hostaquick and Hostathion) were determined in several vegetable crops during the growing period. Heptenophos residues decreased below the limit of detection (0.001 mg/kg) in most of the crops one week after the treatment. However, the decline of triazophos in vegetables below the limit of detection (0.002 mg/kg) depended on the method of crop treatment.     

Estimation of sampling uncertainty for determination of pesticide residues in plant commodities

In order to provide residue data for refining the estimated sampling uncertainty, a coordinated research program was initiated for performing field studies on residues in individual items of leafy vegetables, small and large crops. The trials were carried out in 13 countries with 3 small fruits, 5 large crops, 2 medium/large crops and 3 leafy vegetables. The 25 pesticide active ingredients applied represented the dicarboximide (3), organophosphorus (8), synthetic pyrethroids (5), phthalimides (2), organochlorine (1) and other types of pesticides (6). In addition, 11 supervised field trials were performed in grapes and lettuce by the pesticide manufacturers, and their results were provided for evaluation. The studies represented actual agriculture practice around the world, and provide reliable data for estimation of sampling uncertainty. Based on the 12346 residue data, the best estimate for the relative sampling uncertainty for composite samples, assuming sample size of 10 for small crops and leafy vegetables and 5 for large crops, with 95% confidence limits in brackets are: small commodities: 0.25 (0.20–0.29); Brassica leafy vegetables: 0.20 (0.16–0.24); large commodities: 0.33 (0.29–0.38).     

A method for the analysis of organophosphorus pesticide residues in Mexican axolotl

A method based on matrix solid-phase dispersion (MSPD) was developed for quantitative extraction of three organophosphorus pesticides (OPPs) from the Mexican axolotl, Ambystoma mexicanum. The determination was carried out using high- performance liquid chromatography (HPLC) with diode array spectrophotometric UV detection (DAD). The MSPD extraction with octadecylsilyl (C18) sorbent combined with a silica gel clean-up and acetonitrile elution was optimised for chlorpyrifos, fenthion and methyl parathion. The method was validated, yielding recovery values higher than 90%. The precision, expressed as the relative standard deviation (RSD), was less than or equal to 6% in muscle samples at spiking levels of 10 and 5 ppm. Linearity was studied from 15 to 60 ppm for chlorpyrifos and fenthion, and from 7.5 to 30 ppm for methyl parathion. The limits of detection (LODs) were found to be less than or equal to 0.5 ppm_.This method was applied to the analysis of samples from a chlorpyrifos-exposed axolotl, demonstrating its use as an analytical tool for toxicological studies.     

Organochlorine and organophosphorus pesticide residues in the Atoya river basin, Chinandega, Nicaragua

The hydrographic basin of the Atoya river, located in the Department of Chinandega, one of the main cotton producing regions in Nicaragua, is intensively contaminated by pesticides. Samples of river waters and sediments, as well as strategically selected wells have been analyzed to study variations in the concentrations of organochlorine and organophosphorus pesticide residues between the dry season (November-April) and the rainy season (May-June). Generally, higher concentrations of pesticides have been detected in the river waters and sediments in the dry season. DDT, DDD, DDE compounds and toxaphene are the most frequent organochlorine residues found in the water and sediment samples, while endrin, aldrin, dieldrin and lindane are mainly found in the waters of rivers and wells. Organophosphorus compounds were rarely detected. However, residues of ethion, methyl-parathion and ethyl-parathion were found in high concentrations in some river and well water samples. Generally, organochlorine compounds tend to accumulate in the fine grain-size fractions, rich in organic matter, except DDE, which concentrates basically in the coarse grain-size fractions.     

Determination of organochlorine and organophosphate pesticide residues in fruits,vegetables and sediments

Abstract

A method is described for the determination of organochlorine and organophosphate pesticide residues in fruits, vegetables and sediments. The concentrated solvent extract was sealed in a polymeric membrane tube, dialysed in cyclohexane and the solvent replaced with hexane. The organophosphates were analysed on a specific thermionic detector without further clean‐up. For the organochlorine pesticides the extract was eluted through 3 g of alumina and analysed on GC/ECD. The clean‐up for sediment extract was carried out on a10 g alumina column with 100 mL hexane containing 5% acetone and the eluate was concentrated to 5 mL.

The detection limit for organophosphates on a 40 g sample and a final volume of 10 mL was on the average 0.01 mg/kg. The detection limit for organochlorine pesticides, with the final volume of 25 mL, was 0.005 mg/kg for all pesticides except for p,p'‐DDT and endosulfan sulphate, which was 0.01 mg/kg.

The detection limit for oganochlorine pesticides in sediment, with the final volume of 2 mL, was less than 1 μg/kg and for organophosphate pesticides less than 10 μg/kg when the final volume was made to 0.5 mL. At the detection limits the method produced a very high coefficient of variation for both organochlorine and organophosphate pesticides.     

Determination of organochlorine and organophosphate pesticide residues in fruits, vegetables and sediments.

A method is described for the determination of organochlorine and organophosphate pesticide residues in fruits, vegetables and sediments. The concentrated solvent extract was sealed in a polymeric membrane tube, dialysed in cyclohexane and the solvent replaced with hexane. The organophosphates were analysed on a specific thermionic detector without further clean-up. For the organochlorine pesticides the extract was eluted through 3 g of alumina and analysed on GC/ECD. The clean-up for sediment extract was carried out on a 10 g alumina column with 100 mL hexane containing 5% acetone and the eluate was concentrated to 5 mL. The detection limit for organophosphates on a 40 g sample and a final volume of 10 mL was on the average 0.01 mg/kg. The detection limit for organochlorine pesticides, with the final volume of 25 mL, was 0.005 mg/kg for all pesticides except for p,p'-DDT and endosulfan sulphate, which was 0.01 mg/kg. The detection limit for organochlorine pesticides in sediment, with the final volume of 2 mL, was less than 1 microgram/kg and for organophosphate pesticides less than 10 micrograms/kg when the final volume was made to 0.5 mL. At the detection limits the method produced a very high coefficient of variation for both organochlorine and organophosphate pesticides.     

Persistence and distribution of pesticide residues in fresh agricultural food consumed in the province of Bologna

The presence of pesticide residues in fresh vegetables and fruit have been qualitatively and quantitatively determined at the laboratories of the Regional Agency for Environmental Protection (ARPA), Division of the Province of Bologna. More than 1,700 samples have been tested by routine analyses. The possible risks for consumers have been evaluated by various parameters. The most important ones were: the amount of each residue; the respective ADI (Acceptable Daily Intake) limit; the contemporary presence of different residues; an estimation of the daily intake, based on the amount of fruit and vegetables consumed per person. It has been possible to evaluate that the daily intake of pesticide residues in the province of Bologna during the period 2003–06 resulted lower than the ADI limits concerning the vegetables. According to the information on fruit consumption the daily intake of omethoate (O,O-dimethyl S-methylcarbamoylmethyl phosphorothioate) resulted higher than its ADI limit, of dicofol (2,2,2-trichloro-1,1-bis(trichloromethyl)benzenemethanol) very close to the admitted limit, under the respective limits for all the other residues.     

Uncertainty of exposure assessment of consumers to pesticide residues derived from food consumed

The sources of quantitative and qualitative uncertainties of the exposure of a consumer to a pesticide residue are identified. The contribution of quantifiable uncertainties of input parameters of deterministic model to the combined uncertainty of the estimated exposure is shown with detailed calculation using the pesticide residue content of food consumed during two days. The daily intakes of bifenthrin residues calculated for the 60 kg bodyweight of the reporting person are 0.00257 mg/kgbw and 0.00281 mg/kgbw for day 1 and day 2, respectively with 27-28% combined uncertainty. The major contributors were fruits and whole meal bread. The contribution of the individual steps to the combined uncertainty depends on the particular food item. In general, the variability of recipes, estimation of the mass of consumed food, sampling, processing of raw commodities and analysis of pesticide residues influenced most, in decreasing order, the combined uncertainty of the estimated daily exposure.     

加强肥料规范化管理控制蔬菜重金属污染

总结了中国各主要城市郊区的蔬菜重金属的污染情况,从各种调查结果看出,中国蔬菜的重金属含量总体上还处在安全食用范围内,但在城郊结合部,蔬菜中重金属的污染比较严重。肥料是重金属污染的重要来源之一,从肥料的生产和管理的角度提出了控制肥料重金属含量的方法．为蔬菜食用的安全性提供保障。