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。     

汉沽污水库生物净化效应——DDT、666对斜生栅藻[Scendesmus Obliquus(Turp)KuTZ]生长量、色素含量及吸收光谱的影响

我国大部分地区长期使用有机氯农药做为杀虫剂,另一方面工厂排放污水中的有机氯农药,致使土壤,水系,大气,生物都存在不同程度有机氯农药的残留,对环境造成一定的污染。 环境中残留的农药,一方面可以经过生物的富集转移到食物中,影响人类健康。另一方面生物对农药也有一定自净能力。定量估计浮游植物的繁殖情况,对研究它们参与水域自净,     

汉沽污水库生物净化效应——(五)、DDT对两种单细胞藻(Chamydomonas reinhardi Dang and Scendesmus Obliquus(Turp)Kütz)的生物效应

前言 目前我国虽然对有机氯农药已采取限制,并将取消生产,但有些地区仍然以有机氯农药作为毒饵使用,以及历年来长期使用有机氯农药,在土壤、水体中造成一定的残留,使环境受到污染。     

农药污染土壤的生物修复技术

本文综述了土壤农药有机污染的生物修复技术 ,重点分析了植物、微生物对土壤农药污染的修复机制以及影响因子 ,介绍了几种生物修复技术     

农药污染土壤的生物修复技术

本文综述了土壤农药有机污染的生物修复技术,重点分析了植物、微生物对土壤农药污染的修复机制以及影响因子,介绍了几种生物修复技术。     

南方平原地区农药污染农田生态环境质量评价

本文根据南方热带亚热带平原地区农田生态环境特征,以广东省佛山市农田环境为例,从卫生毒理学和生态学角度出发,探讨了加权污染指数法在农药污染农田环境质量评价中的应用,提出了利用植物对农药的吸收系数和土壤中农药的流失系数确定评价因子权重系数的方法。根据南方平原生态环境特点确定土壤中的农药“残留允许量”;并认为农药标准具有较强的区域性和地带性,不宜制定单一的标准,南方热带亚热带地区农业土壤农药标准应严于北方。     

农药在土壤中的结合残留

文章综述了土壤中农药的结合残留问题。有人认为,结合态农药残留物不仅不可提取,而且生物活性也较低,是一种减少污染的有效办法。也有认为,结合态农药残留物在一定条件下可被土壤生物吸收和释放,会对生态系统产生一定的影响。因此,这一问题已引起环境工作者的重视。     

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。     

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     

表面活性剂强化植物-微生物联合修复双对氯苯基三氯乙烷污染土壤研究

通过实验对比研究植物(油菜)修复、微生物(甲基营养型芽孢杆菌(Bacillus methylotrophicus))修复、表面活性剂(聚氧乙烯山梨醇酐单硬脂酸酯(Tween 60))以及联合修复技术对双对氯苯基三氯乙烷(DDT)污染土壤的DDT去除效果。结果表明:以植物-表面活性剂-微生物共同作用下的DDT去除效果最好,土壤DDT去除率达到52.44%;油菜不仅可有效去除土壤中残留的DDT,同时只在地下部分对DDT进行了微量吸收,但没有进行转运,防止了农药在油菜可食部位的累积,保障了食品与生产安全。     

Bound pesticide residues in soils: a review

This article is a review of the current state of knowledge regarding the formation and biological/environmental significance of bound pesticide residues in soils. We begin by defining various terms used in our discussions and identifying the types/classes of pesticides which may be added to soil and interact with it. We then consider various soil properties and aspects of land management which will influence the nature and degree of the soil-pesticide association and discuss the possible physical and chemical binding mechanisms. We then move on to consider the role of microorganisms and other forms of soil biota in bound residue formation and the bioavailability of soil-borne pesticide residues. The review ends with a consideration of the significance of bound pesticide residues.     

Evaluating environmental hazards of land applying composted diazinon using earthworm bioassays.

Environmental hazards resulting from land application of composted pesticide residue have not been rigorously evaluated. This study was conducted to examine the toxicity of a composted pesticide residue using earthworms (Eisenia foetida Savigny) as a microinvertebrate model in a soil bioassay system. Diazinon, which was used in these experiments as a test pesticide, was removed from simulated rinsate (wastewater) by sorption onto peat moss. Following the rinsate clean-up phase, diazinon-laden peat moss was placed into bioreactors and composted for either 30 or 60 days. Earthworms were then exposed to soil amended with the composted material. Mortality and symptomatic effects characteristic of acetylcholinesterase inhibition, including weight loss, reduced burying ability and curling, occurred in earthworms exposed to soil amended with either uncomposted or 30-day composted diazinon, but not in those exposed to soil amended with 60-day composted diazinon. The amount of solvent-extractable diazinon from compost was not directly related to acute earthworm toxicity based on the selected criteria. These results indicated a reduction in diazinon bioavailability during latter 30 d of composting that did not correspond to a reduction in solvent-extractable diazinon concentrations. Measuring symptomatic effects of xenobiotics as described in this study may increase the sensitivity and diagnostic ability of earthworm bioassays.     

Dissipation of chlorpyrifos in two soil environments of semi-arid India

The dissipation of chlorpyrifos (20 EC) at environment-friendly doses in the sandy loam and loamy sand soils of two semi-arid fields and the presence of pesticide residues in the harvested groundnut seeds, were monitored. The movement of chlorpyrifos through soil and its binding in the loamy sand soil was studied using 14C chlorpyrifos. Chlorpyrifos was moderately stable in both loamy sand and sandy loam soils, with half-life of 12.3 and 16.4 days, respectively. With 20 EC treatments the dissipation was slower for standing crop than seed treatment, indicative of the high degradation rates in the bioactive rhizosphere. In soil, 3,5,6-trichloro-2-pyridinol (TCP) was the principal breakdown product. Presence of 3,5,6-trichloro-2-methoxypyridine (TMP), the secondary metabolite, detected in the rhizospheric samples during this study, has not been reported earlier in field soils. The rapid dissipation of the insecticide from the soil post-application might have resulted from low sorption due to the alkalinity of the soil and its low organic matter content, fast topsoil dissipation possibly by volatilization and photochemical degradation, aided by the low water solubility, limited vertical mobility due to confinement of residues to the upper 15 cm soil layers and microbial mineralization and nucleophilic hydrolysis. Contrary to the reports of relatively greater mobility of its metabolites in temperate soils, TMP and TCP remained confined to the top 15 cm soil. The formation of bound residues (half-life 13.4 days) in the loamy sand soil was little and not "irreversible." A decline in bound residues could be correlated to decreasing TCP concentration. Higher pod yields were obtained from pesticide treated soils in comparison to controls. Post-harvest no pesticide residues were detected in the soils and groundnut seeds.     

Pesticide persistence and bound residues in soil--regulatory significance

The paper discusses key aspects of the European Union (EU) regulatory policy related to the persistence and bound residues of agricultural pesticide active substances in soil. This is examined in the context of the EU Authorisations Directive (91/414/EEC) which will gradually replace existing national systems of agricultural pesticide regulation within EU Member States. Discussion is concentrated on this directive, looking in particular at the Uniform Principles therein and the possible ways that these decision-making guidelines could be developed into a regulatory framework. The aim in this process of negotiated development is to identify any questions or data requirements that will be needed for persistent pesticides or soil bound residues, over and above those generally required for all compounds. The present EU regulatory position on soil non-extractable or bound residues is examined and possible future improvements to the system are described and discussed.     

Experimental approaches and analytical techniques for determining organic compound bound residues in soil and sediment

Research has shown that many chemicals form persistent and permanently bound residues in soils and sediments that play an important role in soil and sediment detoxification processes, long-term compound partitioning behaviour and compound bioavailability and toxicity in soil and sediment. This article reviews the methodological approaches that have been applied to determine the nature of bound residues in soil and sediment, the application of specific analytical techniques, the type of information they generate, and their relative advantages and disadvantages. It begins by defining bound residues and discussing soil-compound interactions. The application of model compound studies for elucidating specific binding interactions is reviewed along with long-term laboratory and field soil incubation experiments. The use of radiolabelled compounds, isotopically labelled compounds and combinations of both in these experiments are outlined by examples from the literature, along with sequential extraction schemes for releasing bound residues from soil, sediment and humic materials. The importance of spectroscopic methods, and particularly nuclear magnetic resonance techniques for characterising the structure of bound residues in soil and sedimentary humic substances is discussed and illustrated by examples from the literature on the subject. The process of bound residue formation is highly complex and requires further research to establish the mechanisms of bound residue formation and their subsequent environmental and toxicological fate. Much of the uncertainty regarding the elucidation of bound residue formation arises from our poor understanding of the structure of soil and sedimentary organic matter. Significant advances in our understanding of the formation and fate of bound residues will be made when we develop a deeper insight into the complex and heterogeneous structure of soil and sedimentary organic matter.     

Residue determination and dissipation of ioxynil octanoate in maize and soil

A simple and efficient residue analysis method for direct determination of ioxynil octanoate in maize and soil was developed and validated with High Performance Liquid Chromatography-Ultra Violet (HPLC-UV). The samples were extracted with mixtures of acetonitrile and deionized water followed by Solid Phase Extraction (SPE) to remove co-extractives prior to analysis by HPLC-UV. The recoveries of ioxynil octanoate extracted from maize and soil samples ranged from 86 %-104 % and 84 %-96 %, respectively, with relative standard deviation (RSD) less than 7.84% and sensitivity of 0.01 mg kg(-1). The method was applied to determine the residue of ioxynil octanoate in maize and soil samples from experimental field. Data had shown that the dissipation rate in soil was described as pseudo-first-order kinetics and the half-life (t(1/2)) was less than 1.78 days. No ioxynil octanoate residue (<0.01 mg kg(-1)) was detected in maize at harvest time withholding period of 60 days after treatments of the pesticide. Direct confirmation of the analytes in field trial samples was realized by Liquid Chromatography-Mass Spectrometry (LC-MS).     

Distribution of pesticide residues in soil and uncertainty of sampling

Pesticide residues were determined in about 120 soil cores taken randomly from the top 15 cm layer of two sunflower fields about 30 days after preemergence herbicide treatments. Samples were extracted with acetone-ethyl acetate mixture and the residues were determined with GC-TSD. Residues of dimethenamid, pendimethalin, and prometryn ranged from 0.005 to 2.97 mg/kg. Their relative standard deviations (CV) were between 0.66 and 1.13. The relative frequency distributions of residues in soil cores were very similar to those observed in root and tuber vegetables grown in pesticide treated soils. Based on all available information, a typical CV of 1.00 was estimated for pesticide residues in primary soil samples (soil cores). The corresponding expectable relative uncertainty of sampling is 20% when composite samples of size 25 are taken. To obtain a reliable estimate of the average residues in the top 15 cm layer of soil of a field up to 8 independent replicate random samples should be taken. To obtain better estimate of the actual residue level of the sampled filed would be marginal if larger number of samples were taken.     

Formation of bound residues by naphthalene and cis-naphthalene-1,2-dihydrodiol

The formation of bound residues by naphthalene and its metabolite, cis-naphthalene-1,2-dihydrodiol, in a sediment (1% OC), a silty loam soil (2.9% OC) and a peat (26% OC) was examined. The experiments were carried out under both sterile and nonsterile conditions for up to 35 days. The samples containing bound contaminant were hydrolyzed at an alkaline pH and fractionated using 3,000 and 500 Da molecular weight cutoff ultrafiltration membranes in series. The results for all the geosorbents examined showed that bound residue formation is low for naphthalene and between 5 and 20 times higher for the metabolite. The amount of bound residues released by hydrolysis was higher for the metabolite than for the parent compound for all the samples. The molecular weight distribution of bound radioactivity after hydrolysis showed binding to the high molecular weight components of the sediment organic matter and to the low molecular weight components for soil and peat organic matter when incubated with cis-naphthalene-1,2-dihydrodiol. Experiments performed with naphthalene-UL-(14)C showed larger amounts of bound residue found than in experiments with naphthalene-1-(14)C.     

Structural characterisation of humic acid-bound PAH residues in soil by 13C-CPMAS-NMR-spectroscopy: evidence of covalent bonds

The fate of 13C-labelled phenanthrene and fluoranthene in different soil systems during biodegradation was studied. The soil humic acid fraction was isolated followed by structural characterisation using 13C-cross polarisation magic angle spinning nuclear magnetic resonance spectroscopy (13C-CPMAS-NMR). It could be demonstrated that especially the ratio between the concentrations of polycyclic aromatic hydrocarbons (PAHs) and soil humus matrix limits the usefulness of this analytical tool. Based on these results a ratio of 13C-activity(PAH)/13C-activity(soil) approximately 1.5/1.0 in the test material was suggested. The chemical transformation of a PAH and its bound residue formation in a soil system detected by changes of chemical shifts in the 13C-NMR spectrum was proven for the first time. Structural information obtained by NMR spectra were verified by alkaline hydrolysis of PAH/humus-associations and following identification of cleavage products. Ester-bound phenanthrene metabolites such as 1-hydroxy-2-naphthoic acid, ortho-phthalic acid and 3,4-dihydroxybenzoic acid were detected. Additional structural assignments indicated the presence of ether-bound phenanthrene derivatives as well. Using isotopic labelling techniques a quantitative evaluation of bound residue distribution was undertaken. Fifty to seventy percent of phenanthrene metabolites which could be related to the added 13C(1)-phenanthrene were ester bound via their carboxyl groups.     

Management-oriented sensitivity analysis for pesticide transport in watershed-scale water quality modeling using SWAT

The Soil and Water Assessment Tool (SWAT) was calibrated for hydrology conditions in an agricultural watershed of Orestimba Creek, California, and applied to simulate fate and transport of two organophosphate pesticides chlorpyrifos and diazinon. The model showed capability in evaluating pesticide fate and transport processes in agricultural fields and instream network. Management-oriented sensitivity analysis was conducted by applied stochastic SWAT simulations for pesticide distribution. Results of sensitivity analysis identified the governing processes in pesticide outputs as surface runoff, soil erosion, and sedimentation in the study area. By incorporating sensitive parameters in pesticide transport simulation, effects of structural best management practices (BMPs) in improving surface water quality were demonstrated by SWAT modeling. This study also recommends conservation practices designed to reduce field yield and in-stream transport capacity of sediment, such as filter strip, grassed waterway, crop residue management, and tailwater pond to be implemented in the Orestimba Creek watershed.