不同有机质含量的土壤中DDT对小麦根系的生物有效性

对不同有机质含量的土壤中，分别选用水、正己烷、正己烷／丙酮混合溶剂作为DDT的提取剂，用这3种提取剂逐级连续提取，研究了这3级提取剂所提取的DDT量的差别及其与小麦根吸收的关系。结果表明，有机氯的水提取量随土壤D0c的增加而上升，正己烷提取量随土壤TOC的增加而下降，正己烷／丙酮提取量随土壤TOC的增加而上升。根吸收与水提取量没有确定的关系，但与正己烷提取量具正相关关系，与正己烷／丙酮提取量有负相关关系。     

叶类蔬菜有机氯农药残留测定过程中的提取和净化

用柱萃取法提取 ,气相色谱 电子捕获检测器 (GC ECD)测定蔬菜中的多种有机氯农药 .比较了不同提取溶剂对蔬菜中有机氯农药的提取效率 .就回收率而言 ,正己烷和丙酮 (V/V ,4∶1 ) >石油醚和丙酮 (V/V ,4∶1 ) >二氯甲烷和丙酮 (V/V ,4∶1 ) >纯正己烷 .用正己烷和丙酮作提取溶剂时 ,1 2种有机氯农药中有 1 0种的回收率在 80 %以上 ,变异系数在 1 %— 1 5 %之间 .不同固相萃取 (SPE)填料对有机氯农药的纯化效率为 :硅胶对目标物质的净化效率要高于硅藻土和氟罗里硅土 ,硅胶做填料时变异系数在 1 5 %以下 .因此 ,本实验认为用正己烷和丙酮 (V/V ,4∶1 )做提取剂、选择硅胶做填料能够对蔬菜中多种有机氯农药有较好的提取和净化效果 ,是一种较理想的蔬菜中有机氯农药的分析方法 .     

油料作物对土壤老化残留DDT的吸收积累

油料作物对亲脂性DDT的吸收富集能力是否会更强是一个值得研究的问题。采用DDT老化残留土壤,温室盆栽油料作物花生(Arachishypogaea),大豆(Glycinemax)和芝麻(Sesamumindicum)。果实成熟后将植株分成根、茎、果壳和果仁四部分,GC-ECD测定各部位中的DDT浓度。研究了油料作物对土壤老化残留DDT的吸收积累情况,结果表明,∑DDT在三种作物不同部位中的浓度顺序都是:根>茎>果壳>果仁。含油量高的花生果仁和芝麻果仁中∑DDT浓度都明显高于大豆果仁的∑DDT浓度,这种差异有可能是由果仁含油量的差异造成的。单株植物吸收积累∑DDT的总量顺序为:花生>芝麻>大豆。花生、大豆和芝麻三种作物的根和茎的生物富集系数都比较高,特别是花生的,说明这三种油料作物根部从土壤中吸收积累老化残留DDT的能力以及从根部向茎部运输DDT的能力都是相当强的。     

降雪中有机氯农药六六六、DDT残留量调查

本文报告了1978年12月至1979年3月唐山市降雪中有机氯农药六六六、DDT含量为1.57微克/升,其中六六六占总量的92.5%。而DDT仅占7.5％。并发现有机氯农药在降雪中含量随降雪时间的推移而依次降低。还对有机氯农药在环境中存在状态与形式进行了讨论。     

呼和浩特市近郊蔬菜、土壤有机氯(六六六、DDT)农药污染现状调查

本项调查是以呼和浩特市近郊四个主要蔬菜生产乡为重点,对人们日常生活中必不可少的蔬菜种类进行测定和分析。其目的是了解该市郊区蔬菜田间土壤有机氯(六六六、DDT)污染水平和残留农药降解情况,进而对蔬菜可食部分中有机氯农药含量增加或减少规律的调查和分析。调查结果为,蔬菜、土壤中有机氯农药残留水平低于国家规定的食品卫生标准,而且有下降趋势,这说明有机氯污染随时间的推移,逐年递减,但仍应进行长期监测。     

气相色谱法测定土壤中BHCs和DDTs的残留

建立了土壤中六六六 (BHC )和滴滴涕 (DDT )异构体含量的气相色谱分析方法 ,样品以正己烷 丙酮利用超声波提取 ,提取液以层析柱净化 采用HP 1(Methylsiloxane )毛细管色谱柱分离样品 ,GC ECD检测BHC和DDT的残留量 ,方法的最小检测量为 1 5× 10 -13 — 1 6× 10 -12 g ;平均加标回收率为 92 6 %—99 2 % ;RSD为 2 2 %— 6 0 %     

雷州半岛典型区域土壤有机氯农药污染探查研究

在雷州半岛典型区域共采集了74个表层土壤和4个剖面土壤,对土壤中有机氯农药残留及分布状况进行了研究。结果表明:有机氯农药检出率为100%,其中∑HCH(六六六)和∑DDT(滴滴涕)质量分数范围分别在nd～65.93μg·kg-1和0.04～52.00μg·kg-1之间,同国内外同类报道相比处于较低水平;按土壤中有机氯农药17种成分质量分数所占的比重排序,前五名分别为P,P'-DDE、β-HCH、硫丹硫酸盐、硫丹Ⅱ、艾氏剂;按不同利用类型土壤中有机氯残留质量分数由大到小排序为菜地→水田→果园→甘蔗地;有机氯农药残留质量分数随土壤深度的增加呈下降趋势,耕层(0~20cm)的有机氯农药残留质量分数都高于底下层次。     

降雨中有机氯农药土壤-水界面迁移过程的实验模拟

以人工降雨实验模拟的方法,对有机氯农药在降雨过程中非点源污染的产生进行了研究.结果表明,在降雨过程中,表层径流中有机氯农药的输出量高于土壤渗流液.土壤径流中有机氯农药浓度的输出呈现先下降后平缓的趋势.土壤有机质影响着降雨过程中有机氯农药浓度的输出变化趋势.泥炭土径流中有机氯农药的输出量相对较高.有机氯农药残留总量沿土壤剖面的总体变化趋势为随深度增加而下降,其峰值出现在0—5 cm,反映了污染物的转移规律.泥炭土中有机氯农药的残留量最低.泥炭土、黄褐土和风沙土中有机氯农药含量的峰值均出现在第2次和第3次采样时间,但在30 d后有机氯农药的残留量仍较高,表明有机氯农药在土壤中残留时间长,可能存在着一定的生态风险.     

土壤中2,2＇,5,5＇-四氯联苯的锁定效应及其影响因素

以2,2＇,5,5＇-四氯联苯（PCB52）为典型代表,采用微波提取法研究了土壤中多氯联苯的锁定效应及其影响因素.实验表明,老化时间、土壤的有机质含量、含水率、pH值以及老化环境温度都对土壤锁定2,2＇,5,5＇-四氯联苯的效果有显著影响.2,2＇,5,5＇-四氯联苯锁定量随着老化时间的增长而增加,添加20 d后尤为显著,之后变化缓慢,趋于平衡;随着土壤有机质含量的增加而显著增加;随着土壤含水率的增大而下降,且表现出一定的线性相关性;在pH 5.5—10.5范围内,随着土壤pH值的升高而增大;在15℃到40℃范围内随着老化环境温度的升高而降低.此外,多氯联苯自身的性质也会影响土壤对其的锁定效果.     

南京市城郊蔬菜生产基地有机氯农药残留特征

以网格法在南京市无公害蔬菜生产基地八卦洲采集70个土壤样品,用加速溶剂萃取、固相萃取柱净化后GC-μECD测定土壤中有机氯农药(α-HCH,β-HCH,γ-HCH和δ-HCH以及o,p'-DDT,p,p'-DDT,o,p'-DDE,p,p'-DDE 和p,p'-DDD)残留量.结果表明,土壤中有机氯农药残留总量在6.18～84.72 μg·kg-1之间,平均18.63 μg·kg-1.DDT残留量高于HCH,为3.36～74.19 μg·kg-1,平均12.61 μg·kg-1.土壤中HCH残留量为2.48～17.80 μg·kg-1,平均6.02 μg·kg-1.DDT同系物中以p,p'-DDE和p,p'-DDT为主,而HCH中δ-HCH含量较低,其他3种异构体含量水平相当.所有土样中DDT和HCH残留量均远远低于GB/T 18407 无公害蔬菜产地土壤标准限定值500 μg·kg-1,但大多数土样中DDT和HCH残留量远远高于荷兰无污染土壤标准.     

Substitution of toxicologically critical solvents in the residue analysis of acetamiprid: Towards green chemistry

The article presents the reduced use of toxicologically critical solvents for the extraction and clean-up of a neo-nicotinoid pesticide, acetamiprid from vegetables. Acetamiprid was extracted from spiked vegetable samples of cabbage by the use of different techniques like microwave-assisted extraction (MWAE), sonication and by the conventional method of homogenization. The study revealed that though higher percent recoveries of 78–92 were obtained in the blending method, solvent use was high as compared to MWAE. In MWAE, the percent recoveries recorded were in the range of 46–89 depending upon the solvent used and power employed. A mixture of methanol–water and methanol–acetone at 400 W power levels gave percent recoveries of 72 and 82, respectively, as compared to solvent mixtures, namely, acetone–hexane and acetone–hexane–water, which recorded recoveries of 49 and 67%. The study indicates that the choice of solvent and power employed plays a significant role in MWAE for enhanced recoveries.     

水稻中氟虫双酰胺及其代谢产物的超高效液相色谱残留分析方法

采用超高效液相色谱法分析了氟虫双酰胺及其代谢产物在田水、土壤、稻秆、糙米和稻壳中的残留.水样以乙酸乙酯为萃取溶剂,液-液分配净化;土壤样品以丙酮为提取剂,液-液分配净化;水稻样品经乙腈提取,NH2-Carb柱净化.对水稻和环境中的氟虫双酰胺及其代谢产物进行不同水平的添加回收率实验,方法的回收率在78.2%—104.8%之间,相对标准偏差为1.1%—4.4%.氟虫双酰胺及其代谢产物的最小检出量在0.004—0.02 ng,其在稻田水中的最低检测浓度为0.0008—0.0009 mg.L-1,在土壤、稻秆、糙米、稻壳中的最低检测浓度为0.001—0.003 mg.kg-1.     

水体和甘蓝及土壤中毒死蜱残留检测方法

研究运用不同的样品前处理方式,在装配火焰光度检测器的气相色谱(GC-FPD)上检测,建立了有机磷杀虫剂毒死蜱在水样、土壤和甘蓝中的残留测定方法.研究表明,不同样品中的毒死蜱残留采用本文中介绍的前处理方法是可行的,用石油醚盐析提取和净化水样中毒死蜱,采用丙酮振荡提取甘蓝中毒死蜱,选用索氏提取法提取土壤中毒死蜱,并经液液分配净化后,采用OV-101大口径毛细管柱(30 m×0.53 mm×1.0μm),在装配火焰光度检测器(FPD和磷滤光片)的气相色谱上测定.该分析方法下,毒死蜱的保留时间为1.74 min,线性范围在1.0×10-11—1.0×10-8g之间,其线性相关系数为0.9998,最小检出量为2.0×10-12g.在设定的较低添加浓度的条件下,毒死蜱在水样、土壤与甘蓝上的添加回收率为80%—120%,变异系数均小于5%.该分析方法灵敏、准确、操作简便,适合水样、甘蓝和土壤中低浓度毒死蜱的残留检测.     

Adsorption and movement of carbaryl in soils: A verification of cosolvent theory and comparison of batch equilibrium and soil thin layer chromatography results

Batch equilibrium and soil thin layer chromatography (TLC) techniques were used to investigate the influence of different volume fractions of organic cosolvents (acetone and methanol) on the adsorption and movement of carbaryl in four different types of Indian soils. L-shaped isotherms were obtained for both the cosolvent–water mixtures at all f _s values and were in close agreement with the Freundlich equation. Higher adsorption was observed on F.R.I. soil (FSL) followed by Alampur soil (ASL), Kalai soil (KL), and Bhoran soil (BSL) at all f _s values for both the cosolvent systems as was anticipated from the K and K _D values. The K and K _D values also confirmed that carbaryl adsorption was higher in methanol–water mixture than acetone–water mixture and decreased with increasing f _s values. The frontal R _f values obtained from soil TLC studies were inversely proportional to the K and K _D values for both the cosolvent systems. The higher K and K _D values and lower R _f values in methanol–water mixtures relative to acetone–water mixtures for all the soils indicated that acetone had a greater potential for ground water contamination compared to methanol. The adsorption data were used to evaluate the cosolvent theory for describing adsorption of carbaryl in acetone–water and methanol–water mixtures. The aqueous phase partition coefficients, K _DW (mol g^?1), normalized with respect to f _oc for carbaryl was evaluated by extrapolating f _s → 0.     

用黑麦幼苗法测定土壤中污染元素的生物有效性

本文对全国污灌区１２个土样中Ｃｄ形态与生物有效性的试验表明，Ｃｄ的交换态，吸附态，有机结合态均有效，且有机结合态最为有效，对紫阳县富硒土壤的试验表明：黑麦幼苗中的总Ｓｅ量与０．１ｍｏｌ／１ＫＨ２ＰＯ４的浸提量最为相关，从而推荐该法为酸性土壤有效Ｓｅ的浸提方法，对西安污水厂污水污泥在娄土上不同施用量的试验表明：幼苗中Ｎ，Ｐ随施用量增加而增加，Ｎ，Ｐ的有效率分别为５０－７０％及１５－２８％；黑麦幼苗中     

气相色谱／质谱测定电子垃圾拆解区土壤中四溴双酚A的方法

本研究建立气相色谱/质谱来测定电子垃圾拆解区土壤中四溴双酚 A（TBBPA）的方法。该化合物通过超声波辅助萃取,溶剂选择V（丙酮）﹕V（正己烷）=1﹕1或乙酸乙酯;净化柱选择酸化的氟罗里硅土和无水硫酸钠混合物或CleanertC18-SPE进行净化;净化液浓缩后经衍生反应,衍生试剂选用N,O-双（三甲基硅烷基）三氟乙酰胺（BSTFA）和含1%的三甲基氯硅烷（TMCS）。该方法测定电子垃圾拆解区土壤中TBBPA的检出限为（S/N=3）0.1μg·kg^-1加标回收率平均值为92.7%（n=5）,重现性RSD为2.52%（n=5）;线性范围是20～400μg·kg^-1相关系数0.999。该方法用于调查电子垃圾拆解区土壤中四溴双酚A,范围值为5.17～218.00μg·kg^-1其周围农田土壤中四溴双酚A,范围值为0.312～4.170μg·kg^-1     

三种表面活性剂对高浓度DDTs污染土壤的洗脱作用

以高浓度滴滴涕(DDTs)污染场地土壤为研究对象,采用表面活性剂洗脱试验,比较研究了聚氧乙烯山梨糖醇酐单硬脂酸酯(Tween60)、辛基酚聚氧乙烯醚(TritonX 100)、十二烷基硫酸钠(SDS)对污染土壤中DDTs的洗脱效率.试验结果表明,三种表面活性剂对污染土壤中DDTs均具有一定的洗脱作用,去离子水对DDTs几乎没有洗脱效果.随着洗脱液中Tween60和SDS质量浓度的逐渐升高,土壤中DDTs的总洗脱效率逐渐增大,一次性洗脱时最大洗脱效率分别为43.60%和34.62%.随着洗脱液中TritonX 100质量浓度的逐渐升高,土壤中DDTs的总洗脱效率出现先增大后降低再升高的变化现象,最大为15.46%.土壤中六种DDT组分的洗脱效率不完全一样,其中Tween60对2,4'-DDD的洗脱效率可达55.12%,对4,4'-DDD的洗脱效率为54.09%;SDS对2,4'-DDD的洗脱效率为59.99%,对4,4'-DDD的洗脱效率为57.10%.试验结果可为筛选适宜的表面活性剂及质量浓度,研发高浓度DDTs污染场地土壤表面活性剂洗脱修复技术的工程应用提供理论依据.     

Factors affecting HCH and DDT in soils around watersheds of Beijing reservoirs,China

The factors that influence the dynamics of hexachlorocyclohexane (HCH) and dichlorodiphenyltrichloroethane (DDT) in soils around the watersheds of Beijing reservoirs were examined. Compared with other studies on HCH and DDT in soils and established reference values, the concentrations of HCH and DDT in soils around our study area were relatively low. The relationships between HCH and DDT concentrations and land use, soil texture, and soil properties were discussed. HCH and DDT concentrations were higher in arable soils than those in uncultivated fallow soils. Although land use was the most important factor affecting HCH and DDT residues, additional factors such as soil texture and soil total organic carbon were also involved in pesticide retention in soils. The results indicated that the historical agricultural applications of HCH and DDT were the major source of their residues. Atmospheric deposition, as well as long-distance transportation and inputs from surrounding weathered agricultural soils may also serve as important sources of HCH and DDT residues in the watersheds.     

Decolorization of methyl orange in wastewater with in situ electrogenerated oh free radicals

A treatability study was conducted to determine the potential of white rot fungi to remediate soil from a Superfund site that had been contaminated with DDT. A tiered approach was utilized, starting with simple laboratory studies to screen the potential of white rot fungal strains to degrade DDT and culminating with a soil pan study that simulated land farming. Results from early tiers of the study indicated that Phanerochaete sordida had the best potential for remediating the soil. In the soil pan study, the fungus ultimately grew very well after second inoculation. However, the good growth did not translate to higher DDT removal compared to removal in pans that were not inoculated. ¹⁴[DDT] fate studies indicated the small amount of removal that did occur for both fungal inoculated and non‐inoculated conditions could be partially attributed to incorporation into humic material. Addition of a surfactant to the soil enhanced the removal of DDT in both inoculated and non‐inoculated soil. Consequently, under simulated land fanning conditions, this strain of fungus was not successful in remediating this soil.