Phytoremediation of Weathered p,p′-DDE Residues in Soil

A series of field experiments was established to determine the efficacy of plant-assisted remediation/phytoremediation of weathered (at least 30 years) p,p′-DDE ((2,2-bis(p-chlorophenyl)1, 1-dichloroethylene)) residues in an agricultural soil. Alfalfa, ryegrass, and pole bean were planted in soil containing known amounts of p,p′ -DDE. After approximately 85 d, the crops were harvested and the amount of p,p′-DDE in the bulk soil, near-root zone (soil within area of roots), and rhizosphere was determined. In addition, contaminant levels in the various portions of vegetation were measured. There were statistically significant (p < 0.01) declines in the concentration of p,p′ -DDE in the rhizosphere of alfalfa and ryegrass. The bulk soil concentration of p,p′-DDE ranged from 185 to 230 ng/g soil in the plots containing rye and alfalfa, respectively, whereas the levels in the rhizosphere of these plants at harvest were reduced by up to 39%. Conversely, the concentration of p,p′-DDE in the the bulk soil of pole bean was decreased relative to the amount of contaminant in the rhizosphere: 129 and 191 ng/g soil, respectively. An analysis of the residues of p,p′-DDE in the vegetation shows that no measurable levels of the pesticide were translocated into the shoot system of any of the plants. Concentrations of p,p′-DDE in the roots of the three crops ranged from 25 to 90 ng/g of tissue (oven-dry weight). The data show that highly weathered and recalcitrant residues of p,p′-DDE may be remediated from contaminated soil utilizing these plants under normal growing conditions.     

Effect of Surfactant Tween 80 on the Anaerobic Degradation and Desorption of HCHs and DDX in Aged Soil under Saturated Condition with Low Liquid/Solid Ratio

The application of surfactant Tween 80 was investigated to accelerate the anaerobic degradation of HCHs (α-, β-, γ- and δ-hexachlorocyclohexane) and DDX (p,p′-DDT, o,p′-DDT, p,p′-DDE and p,p′-DDD) in aged soil from a former organochlorine pesticide manufacturing plant under saturated condition with low liquid/solid ratio (liquid/solid ratio = 0.50). The surfactant Tween 80 did not facilitate the degradation of HCHs and DDX in the soil used in this experiment. Subsequent desorption experiment results also showed that the surfactant Tween 80 did not increase the pollutant desorption from the soil. The results in this study are not in accordance with the results reported in previous literature. This difference might be due to the fact that the soils used in this experiment were polluted by HCHs and DDX for more than 20 years, and soil aging reduced the desorption of HCHs and DDX in soil. Furthermore, the surfactants might be adsorbed by soils in low liquid/solid ratio condition.     

Conversion of DDT to DDD in flooded soil

Summary Anaerobic conditions obtained by flooding the soil caused reductive dechlorination of p,p-DDT and its conversion to p,p-DDD was enhanced under water-logged conditions creating or favouring anaerobiosis. The DDT showed recalcitrance in the soil kept at 15% moisture.More o,p-DDT was lost from the flooded soil. Similar amounts of p,p-DDE were detected in all of the three levels of technical DDT treatments and the concentrations were not significantly different under both aerobic and anaerobic conditions.     

Pollution assessment of organochlorine pesticides in urban agricultural soils of Jilin City,China

The content, source, and pollution level of organochlorine pesticides (OCPs) in soils are necessary to assess potential risks to eco-environment and human health, and to target environment-friendly policies. A total of 50 surface soil samples were collected from urban vegetable fields of Jilin City and thirteen OCPs were analyzed. The concentrations were in the ranges of 3.16–48.35 ng·g^?1 for Dichloro-Diphenyl-Tricgloroethanes (DDTs, sum of o, p′-DDT, p, p′-DDT, p, p′-DDD, and p, p′-DDE), 4.37–44.77 ng·g^?1 for Hexachlorocyclohexanes (HCHs, sum of α-HCH, β-HCH, γ-HCH, and δ-HCH), 1.19–13.17 ng·g^?1 for Chlordanes (sum of heptachlor, t-chlordane, and c-chlordane), 0.24–2.60 ng·g^?1 for aldrin, and nd–3.43 ng·g^?1 for dieldrin, respectively. The different compositions indicated that the residues of DDTs and HCHs originated mainly from the historical application, while chlordanes were mostly from recent input. On the basis of soil quality standards of China and the Netherlands, DDTs and chlordanes in this study were categorized as light pollution, and HCHs were classified as no pollution for the majority of soil samples. There are a variety of OCPs residues in urban vegetable soils of Jilin City, but it is still safe and suitable for agricultural production.     

High-performance liquid chromatographic method for determination of DDT and its degradation products in rat plasma, liver and brain: validation and application to a pharmacokinetic study

A sensitive and reliable high-performance liquid chromatographic (HPLC) method, using a solid-phase extraction (SPE), was established and validated for determination of p,p′-DDT [1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane] and its metabolite p,p′-DDE [1,1-(2,2-dichloroethanylidene)-bis(4-chlorobenzene)] in rat plasma, liver and brain. After being diluted with water, plasma, liver and brain samples were applied to a solid-phase extraction C₁₈ cartridge. The extraction containing p,p′-DDT and p,p′-DDE from the cartridge were cleaned-up using a Florisil Sep-Pak cartridge. The samples were analyzed by HPLC using UV detection at 238 nm. The limit of detection for p,p′-DDT and p,p′-DDE was 0.1 mg kg⁻¹ liver or brain and 0.1 mg l⁻¹ plasma. For six replicate samples at 40, 4 and 0.2 mg kg⁻¹, intra-day precision values were within 4.9% for plasma, 6.4% for liver, and 9.7% for brain. Inter-day precision values at 4 mg kg⁻¹ were within 8.2% for plasma and tissues. The method performances were shown to be selective for p,p′-DDT and p,p′-DDE, and linear over the range 0.04–12 mg kg⁻¹ (mg l⁻¹ for plasma). The absolute recoveries of p,p′-DDT and p,p′-DDE in rat plasma and tissues were over 92%. The method was proved to be applicable to the pharmacokinetic study of DDT in rats after a single oral administration.     

The phytoremediation potential of bioenergy crop Ricinus communis for DDTs and cadmium co-contaminated soil

Cadmium (Cd) and dichlorodiphenyltrichloroethane (DDT) or its metabolite residues are frequently detected in agricultural soils and food, posing a threat to human health. The objective of this study was to compare the ability of 23 genotypes of Ricinus communis in mobilizing and uptake of Cd and DDTs (p,p′-DDT, o,p′-DDT, p,p′-DDD and p,p′-DDE) in the co-contaminated soil. The plant genotypes varied largely in the uptake and accumulation of DDTs and Cd, with mean concentrations of 0.37, 0.43 and 70.51 for DDTs, and 1.22, 2.27 and 37.63 mg kg⁻¹ dw for Cd in leaf, stem and root, respectively. The total uptake of DDTs and Cd varied from 83.1 to 267.8 and 66.0 to 155.1 μg per pot, respectively. These results indicate that R. communis has great potential for removing DDTs and Cd from contaminated soils attributed to its fast growth, high biomass, strong absorption and accumulation for both DDTs and Cd.     

An Efficient Extraction Method of Persistent Organic Pesticides in Soil Samples for Their Chromatographic Determination

In order to determine persistent organic pesticides (OPs) and their metabolites in soil samples, an analytical procedure was developed, optimized and validated. It possesses advantages like suitable limits of detection, low solvent volume and time consume, and requires a chromatography detector commonly used in routine laboratories. The method allows the determination of Methoxychlor, p,p’-DDT, Endosulfan sulfate, Endrin aldehyde, p,p’-DDD, Endosulfan II, Endrin, Dieldrin, p,p’-DDE, Endosulfan I, Heptachlor epoxide, Aldrin, Heptachlor, δ-HCH, γ-HCH, β-HCH, α-HCH, Etridiazole, Trifluralin, Hexachlorobencene, Chlorothalonil, Chlorpyrifos, DCPA, γ-Chlordane, α-Chlordane, Clorbenzilate, trans-Permethrin, cis-Permethrin. Linearity is evaluated and the analytical parameters are presented. The average recoveries obtained for each pesticide (28 OPs) by using 3, 15 and 22.5 µg kg^?1 spiked samples ranged between 50 and 97.3%, 57 and 103% and from 60 to 100% for each case. The limits of detection and quantification vary from 0.18 to 1.28 μg kg^?1 and from 0.60 to 4.22 μg kg^?1. The reproducibility obtained as relative standard deviation percentages is less than 7.5, 5.3 and 4.2% for low, middle and high level of concentrations, respectively. The procedure is statistically validated for its application to soil samples and compared with other published methods.     

Tissue Residue Guideline for ∑DDT for Protection of Aquatic Birds in China

DDT (1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane) is a chlorinated hydrocarbon insecticide that has been used worldwide. While the use of DDT has been phased out in many countries, it is still produced in some parts of the world for use to control vectors of malaria. DDE (1,1,-dichloro-2,2-bis(p-chlorophenyl)ethylene) and DDD (1,1-trichloro-2,2-bis(p-chlorophenyl)ethane) are primary metabolites of DDT and have similar chemical and physical properties. DDT and its metabolites (DDE and DDD) are collectively referred to as ∑DDT. The lipophilic nature and persistence of the ∑DDT result in biomagnification in wildlife that feed at higher trophic levels in the food chain. Wildlife in aquatic ecosystems depend on aquatic biota as their primary source of food, which provide the main route of exposure to ∑DDT. Studies about effects of ∑DDT on birds were reviewed. The tissue residue guidelines for DDT (TRGs) for protection of birds in China were derived using species sensitivity distribution (SSD) and toxicity percentile rank method (TPRM) based on the available toxicity data. Risks of ∑DDT to birds were assessed by comparing the TRGs and ∑DDT concentrations in fishes from China. The tissue residue guideline for protection of birds in China is recommended to be 12.0 ng ∑DDT/g food.     

DDT concentrations in surficial sediments of three estuarine systems in Portugal

Levels of p,p-DDT and its metabolites in surficial sediments of Tagus and Sado Estuary and lagoon Ria Formosa varied one or two orders of magnitude. In general, p,-DDE and p,-DDD were the dominant metabolites and p,-DDT was a minor component. While concentrations of p,-DDT, p,-DDD and p,-DDE were hardly related to loss on ignition, concentrations of total DDT (tDDT) in surficial sediments of each studied system were positively correlated to that parameter. Higher contaminated samples were excluded from these relationships: a few sediment samples from the Tagus outlet channel, most of the sediments from the upper Sado Estuary, and some particulate matter samples collected in sediment traps in the adjoining area to the Ria Formosa. Concentration of tDDT appears, thus, to be related to sedimentary organic matter of these estuarine systems except near the actual sources of pollution. On the basis of the relationship slopes, one may conclude that lower Tagus Estuary is more contaminated than Ria Formosa and lower Sado Estuary.     

Heptachlor and o‐p′DDT effects on protein kinase activities associated with human placenta particulate fractions

Organochlorine pesticides have been detected in placenta. The ability of heptachlor (HC) and 1,1,1‐tricholoro‐2‐(2‐chlorophenyl)‐2‐4‐chlorophenyl)ethane (o‐p′DDT) to interfere with protein phosphorylation was evaluated. In vitro incubations of cell‐free placental villi homogenates with a concentration range 1–100 µM were performed. In particulate fractions, total serine/threonine kinase activity was increased by 10 µM HC and o‐p′ DDT (59% and 82%, respectively). Maximum eightfold increase was observed with 10 µM o‐p′ DDT on protein kinase A activity. By contrast, protein kinase C activity was reduced by 10 µM HC and o‐p′ DDT (40% and 52%, respectively). Endogenous substrate phosphorylation studies demonstrated that slight but significant increase in 24‐kDa band labeling was produced in nuclear samples with 1, 10, and 100 µM HC and 100 µM o‐p′ DDT. Exposition to 100 µM HC increased 85‐kDa band labeling. In mitochondrial fractions, 10 µM HC and o‐p′ DDT increased 24‐ and 65‐kDa bands' labeling. These data indicate that both pesticides affect protein kinase activities in particulate fraction. Nuclear compartmentalization of these compounds, insertion in membranes, and chemical stress production may be associated to the observed effects, thus suggesting deleterious consequences in signaling pathways. © 2009 Wiley Periodicals, Inc. J Biochem Mol Toxicol 23:185–192, 2009; Published online in Wiley InterScience ( www.interscience.wiley.com ). DOI 10.1002/jbt.20277     

Elevated Concentrations of Pesticides and PCBs in Soils at the Southern Caspian Sea (Iran) are Related to Land Use

Soil contamination by organochlorine pesticides or PCBs is almost undocumented for Iran. Here we report a soil survey in Mazandaran and Guilan provinces that hold >30% of the agricultural areas of Iran where pesticide use is widespread. Concentration of DDTs, HCHs, cyclodienes, and PCBs were measured in 45 soil samples from different agricultural land uses and forest land. The average concentrations of ∑DDT (37 μg kg^?1) and ∑HCH (21 μg kg^?1) in agricultural soils are among the largest ever reported and exceed international soil screening standards. All residues were larger in agricultural than in forest soil. Within agricultural land, ∑DDT were largest for tea gardens, lindane was largest in rice fields, and cyclodiens largest in citrus orchards. The ratio of (DDD + DDE)/DDT is an index of the extent of DDT degradation in soil and was lower in tea gardens than in other soils (0.7 versus 2–5), indicating either ongoing DDT input or lower degradation rate in the tea gardens that are more acid than the other soils (pH 4.5 versus 6.5–7.0). The o,p′–DDT/p,p′–DDT ratio was about 3 in forest soils, suggesting that DDT is derived from dicofol application and not from technical DDT as in agricultural soils. The PCB 28, 180, and 138 showed the highest mean concentration compared with other PCB congeners in all land uses. This survey is the first of this kind for Iran and illustrates that concentrations of organochlorine pesticide in soil are relatively large.     

Persistent organic pollutants (POPs) in fresh water farm fish species from Punjab (India) and evaluation of their dietary intake for human risk assessment

In India, persistent organic pollutants (POPs) have been used extensively in both agricultural and industrial sectors, resulting in deterioration of terrestrial and aquatic environment. In the present study, analysis of POPs in fresh water ecosystem comprising samples of fish, sediments, and water was done from fish farms in Punjab, India. POP residues comprising lindane, p,p’-DDE, p,p’-DDD, endosulfan sulfate, and polychlorinated biphenyl (PCB) congeners (PCB-28, PCB-138, PCB-180) were detected in fish samples. Residues of p,p’ DDE and p,p’ DDD were recorded utmost in fish flesh with mean levels of 13.8 and 5.8 ng g^?1, respectively. PCB residues were estimated in 20 fish samples with values in the range ND–46.3 ng g^?1. The mean residue levels detected in this study were lower than the recommended maximum residue limits (MRLs) described by EU-MRLs, Italian-MRLs, FDA-2001, and FAO-1983. At the current levels of POP residues in fish flesh, the human health risk assessment based on both deterministic (mean residue levels) and probabilistic (95th percentile upper bound limit) approaches, reflected that cancer and non-cancer risks were within United States Environmental Protection Agency (USEPA) prescribed limits. The presence of POP residues in fish farm sediments and water elucidated the relationship between occurrence of POP residues in fish and its aquatic environment.     

Occurrence of organochlorine contaminants in tissues of the coelacanth Latimeria chalumnae

Synopsis Gas chromatography coupled with electrolytic conductivity detection and electron capture negative chemical ionization mass spectrometry have been used to identify and quantify organochlorine xenobiotics in tissues from two specimens of the living coelacanth Latimeria chalumnae. Compounds identified include polychlorinated biphenyls (PCB), 4,4-DDT and its metabolites 4,4-DDD and 4,4-DDE. Levels of these compounds in the specimens were observed to be generally related to tissue lipid content. Highest concentrations of the xenobiotics were present in the lipid-rich swim bladder, followed by adipose tissue and liver. Levels ranged from 89 to 510 g kg^–1 for PCB and 210 to 840 g kg^–1 for -DDT (including DDD and DDE) on a wet-weight basis. Organochlorine concentrations in relatively lipid-poor tissues, i.e. muscle and kidney, were lower. Parent DDT contributed significantly to the -DDT burden. PCB congeners containing five to seven chlorines were most prevalent. Component distributions did not match those present in common commercial PCB formulations. However, major congeners observed were similar to those reported for other fishes.     

Organochlorine pesticides in Cyprinus carpio from Sidi Salem Dam,north-western Tunisia

Cyprinus carpio (Linnaeus, 1758) caught in Sidi Salem Dam in 2011 were analysed for the levels of organochlorine pesticides (OCPs), including hexachlorobenzene (HCB), aldrin, heptachlor, lindane, dieldrin, endrin, and pp′-DDT and its two main metabolites pp′-DDD and pp′-DDE, in order to evaluate the extent of contamination of the dam. Fish were sampled monthly within the dam during 2011. Muscle, liver and gill tissues were analysed by gas chromatography for the determination of OCPs. Samples had variable concentrations of OCPs, ranging from 2.26 to 17.93 ng g?1, 0.59 to 42.67 ng g?1 and 3.30 to 84.27 ng g?1, which were isolated from gills, muscle and liver, respectively. The organochlorine pesticide levels found posed no threat to human health. The highest OCP levels were found in the liver tissues. The pp′-DDE concentrations and their ratios to ΣDDTs indicate aged DDT pollution and suggests that there has been no recent input of technical DDT from the agricultural areas into Sidi Salem Dam.     

Burkholderia xenovorans LB400联苯双加氧酶及突变体对DDTs的降解

DDTs（dichlorodiphenyltrichloroethane,1,1,1-三氯-2,2-双氯苯基乙烷）是一种典型的持久性有机污染物,曾在疟疾防治和农业除虫方面被广泛应用。虽然包括我国在内的很多国家已经禁止使用DDTs,但目前对环境中DDTs的检测发现它仍然广泛存在且具有新的输入源。DDTs的持续存在对近海生态系统和人类健康具有一定危害,因此它所造成的环境污染问题仍然值得关注。由于Rieske型芳香羟化双加氧酶能够起始多种持久性污染物的降解,过去的几十年里一直是芳香化合物降解领域的焦点。[目的] 为探讨联苯双加氧酶对DDTs的降解特性及机制,本研究选取了食异生素伯克霍尔德氏菌LB400（Burkholderia xenovorans）联苯双加氧酶及突变体对p,p''-DDT和o,p''-DDT的降解过程进行研究。[方法] 以BphAE_LB400为亲本,通过两步定点突变将283位的丝氨酸突变为蛋氨酸,获得突变体BphAE_S283M。通过比较亲本酶与突变体对DDTs的催化性能,模拟突变蛋白结构和分子对接等方法,探究其降解特性及机制。[结果] BphAE_LB400和突变体BphAE_S283M都无法降解对位的p,p''-DDT,但突变体BphAE_S283M可以代谢o,p''-DDT并产生2个立体异构体。对接p,p''-DDT的BphAE_LB400和BphAE_S283M的结构分析表明,BphAE_LB400和BphAE_S283M中p,p''-DDT的反应环均不与原晶体结构中的联苯反应环重合。而对接o,p''-DDT的BphAE_S283M的结构分析表明o,p''-DDT的反应环与晶体结构中的联苯反应环距离很近,且2、3位的碳原子与单核铁原子催化中心的距离在0.5 nm以内,此外,BphAE_S283M的催化腔表面积和体积比BphAE_LB400更大,这很可能有助于BphAE_S283M与o,p''-DDT的结合。[结论] 283位氨基酸是影响BphAE_LB400对DDTs的催化代谢能力的关键氨基酸残基,它可以通过调节反应碳原子与催化中心的距离以及催化腔的大小来影响底物特异性。本次研究进一步阐明了283位氨基酸残基的影响机理,为更有效修复DDTs污染提供理论依据和技术支持。     

Identification and Distribution of m- and p-Hydroxyphenylacetic Acids in the Brain of the Rat

The m and p isomers of hydroxyphenylacetic acid have been identified and quantitated in whole rat brain and in several regions using a capillary column high resolution gas chromatography–mass spectrometry procedure. Their concentrations were: for m-hydroxyphenylacetic acid (mean ± S.E., number of determinations in parentheses)—whole brain, 2.3 ± 0.3 ng/g (7); hypothalamus, 1.2 ± 0.3 ng/g (5); caudate nucleus, 5.5 ± 0.6 ng/g (5); brain stem, 1.8 ± 0.1 ngig (5); cerebellum, 1.2 ± 0.1 ng/g (5) and the “rest,” 1.7 ± 0.1 ng/g (5); and for p-hydroxyphenylacetic acid–whole brain, 10.6 ± 0.7 ng/g (7); hypothalamus, 4.5 ± 0.1 ng/g (4); caudate nucleus, 28.3 ±1.6 ng/g (5); brain stem, 8.6 ± 0.6 ng/g (5); cerebellum, 8.1 ± 0.4 ng/g (9, and the “rest,” 5.3 ± 0.5 ng/g (5). This heterogeneous distribution parallels closely that exhibited by their respective precursor amines, m- and p-tyramine.     

Mineral composition variation in the shells of freshwater mussel Anodonta woodiana at different growth stages

The levels of mineral element Na, Mg, K, Ca, Cr, Mn, Fe, Co, Ni, Cu, Zn, Se, Mo, Al, As, Ag, Cd, and Tl were quantified in the whole shells of the freshwater bivalve Anodonta woodiana at three different growth stages (i.e. J1 juveniles of 1 month old, J2 juveniles of 3.5 months old, and adults of 36 months old). The concentrations of Na and Al were different between different growth stages (p < 0.05). The highest Na concentrations (2715 ± 86 μg/g dry weight) were found in J2 juveniles. The highest Al concentrations (303.9 ± 5.95 μg/g dry weight) were found in J1 juveniles. Manganese concentrations (517.0 ± 47.98 μg/g dry weight) were significantly higher in J2 juveniles than in J1 juveniles (432.3 ± 9.87 μg/g dry weight) (p < 0.05). Copper concentrations (27.32 ± 0.15 μg/g dry weight) were significantly higher in J1 juveniles than in J2 juveniles (26.21 ± 0.86 μg/g dry weight) and adults (24.74 ± 1.43 μg/g dry weight) (p < 0.05). Burdens of Na, Ca, Mn, Fe, Co, Cu, Mo, Ag, and Tl were positively correlated with the shell length (p < 0.05). These findings can possibly contribute to an understanding of elemental requirements for shell growth and, hence, facilitate improvement of survival and growth rates during artificial mussel culture.     

Inheritance Profile of Weathered Chlordane and P,P′-DDTs Accumulation by cucurbita pepo hybrids

Cucurbita pepo ssp pepo (zucchini) accumulates significant levels of persistent organic pollutants in its roots, followed by unexpectedly high contaminant translocation to the stems. Most other plant species, including the closely related C. pepo ssp ovifera (squash), do not have this ability. To investigate the mechanism of contaminant accumulation, two cultivars each of parental zucchini and squash, as well as previously created first filial (F1) hybrids and F1 backcrosses (BC) of those parental cultivars, were grown under field conditions in a soil contaminated with weathered chlordane (2.29 μg/g) and DDX residues (0.30 μg/g; sum of DDT, DDE, DDD). The parental zucchini had stem-to-soil bioconcentration factors (BCF, contaminant ratio of stem to soil) for chlordane and DDX of 6.23 and 3.10; these values were 2.2 and 3.7 times greater than the squash, respectively. Chlordane and DDX translocation factors, the ratio of contaminant content in the stems to that in the root, were 2.1 and 3.2 times greater for zucchini than for squash. The parental zucchini and squash also differed significantly in chlordane component ratios (relative amounts of trans-nonachlor [TN], cis-chlordane [CC], trans-chlordane [TC]) and enantiomer fractions for the chiral CC and TC. Hybridization of the parental squash and zucchini resulted in significant differences in contaminant uptake. For both the three separate component ratios (CR) and two sets of enantiomer fraction (EF) values, subspecies specific differences in the parental generation became statistically equivalent in the F1 hybrid zucchini and squash. When backcrossed (BC) with the original parental plants, the zucchini and squash F1 BC cultivars reverted to the statistically distinct CR and EF patterns. This pattern of trait segregation upon hybridization suggests either single gene or single locus control for persistent organic pollutant (POP) uptake ability by C. pepo ssp pepo.     

The Systematic Separation and Identification of Pesticides in the First Division

The systematic identification and determination of many kinds of pesticides were tried by a combination of column, thin-layer and gas chromatography. Pesticides in the first division,¹⁾ e.g., aldrin, DMC ethylene, CPAS, DDDS, o,p′-DDT, p,p′-DDT, heptachlor, quintozene, Telodrin and tetrasul, were separated from pesticides in the second division,¹⁾ e.g., α-BHC, β-BHC, γ-BHC, trifluralin, CPA, CNP, nitrofen, endrin, dieldrin, dicofol, etc. by column chromatography. Further, pesticides in the first division were separated from each other and determined approximately by thin-layer and gas chromatography.

The recoveries of these pesticides, except for aldrin and CPAS, were about 100%. The recoveries of aldrin and CPAS were about 70 %, due to decomposition during the procedures, or to adsorption on the adsorbent during the column chromatography. It was presumed from GC-MS data that CPAS was decomposed to DDDS, tetrasul and other compounds during the procedures.