DDT降解菌株DB-1的分离、系统发育及降解特性

从农药厂下水道污泥中分离、筛选到1株能够在好氧条件下降解DDT的细菌菌株DB-1,根据表型特征、生理生化特性及16SrDNA序列的系统发育分析,将菌株DB-1初步鉴定为鞘氨醇单胞菌属(Sphingomonassp).该菌株能在含酵母膏(40mg/L)的DDT(40mg/L)无机盐液体培养基中降解DDT,10d降解率达到83.6%,菌株DB-1在25～30℃长势较好,最适生长pH值为8.0.     

南海北部陆架海域枪乌贼中的六六六和DDT

初步探讨用鱿鱼作指示生物,监测离岸海域六六六(BHC)和滴滴涕(DDT)的污染。结果显示,南海北部陆架海域枪乌贼中BHC和DDT含量远低于国内外残留限量值,BHC含量为(0．0278-0．200)×10-9(湿重,下同),平均为0．101×10-9,在剑尖枪乌贼和中国枪乌贼中略高于杜氏枪乌贼中,稍显珠江口海域>粤西海域>粤东海域>台湾浅滩的区域分布; DDT含量为(0．193-4．74)×10-9,平均为0．941×10-9,在剑尖枪乌贼和杜氏枪乌贼中略高于中国枪乌贼,略呈珠江口>粤西≈粤东>台湾浅滩的分布。γ-BHC／ΣBHC比值为0％-69．8％,平均为18．6％,远低于其在商品BHC中的比值;DDE／ΣDDT比值为0％-67．7％,平均为28．4％,在个别近岸站的比值很低。推测南海北部陆架海域近年没有BHC类污染物输入,但局部可能有DDT类污染物输入。     

A 50-year record of dichloro-diphenyl-trichloroethanes and hexachloro-cyclohexanes in lake sediments and penguin droppings on King George Island, Maritime Antarctic

Since the ban on the use of organochlorine pesticides （OCPs） such as dichloro-diphenyl-trichloroethane （DDT） and hexachlorocyclohexane（HCH） in agriculture, their levels have generally dropped. In a number of cases, however, the levels of these OCPs were found to be unchanging or even increasing after the ban. With the aim to unveil the possible causes of these exceptions, we collected two lake cores from King George Island, West Antarctica, and determined their accumulation flux profiles and temporal trends of these OCPs. In the lake core sediments with glacier meltwater input, the accumulation flux of DDT shows an abnormal peak around 1980s in addition to the expected one in 1960s. In the lake core sediments without glacier meltwater input, the accumulation flux of DDT shows a gradual decline trend after the peak in 1960s. This striking difference in the DDT flux profiles between the two lake cores is most likely caused by the regional climate warming and the resulted discharge of the DDT stored in the Antarctic ice cap into the lakes in the Antarctic glacier frontier. Furthermore, to investigate the change of OCPs loadings in the Antarctic coastal ecosystem, we reconstructed the HCH and DDT concentration profiles in penguin droppings and observed a gradual increase for the former and a continuous decrease for the latter during the past 50 years. The increase of HCH seems to be due to the regional warming from the early 1970s and the resulted HCH discharge to the coastal ecosystem by glaciers＇ meltwater and the illegal use of HCH in the Southern Hemisphere in the recent decade. The different temporal trends of HCH and DDT accumulation rate in the lake core with glacier meltwater input and the aged penguin droppings can be explained by their different water-soluble property.     

土壤中不同老化时间的DDT对小麦根系的生物有效性

研究了水、正己烷、正己烷/丙酮ASE对土壤中不同老化时间的DDT的逐级提取量的差别及其与小麦根吸收的关系。结果表明,有机氯的水提量随老化时间增加而下降,正己烷提取量随老化时间增加而下降,正己烷/丙酮提取量随老化时间增加而上升。植物根吸收随老化时间增加而下降。根吸收与水提量没有确定关系,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。正己烷提取量可被作为土壤有机氯DDT的有效态部分。     

DDT污染土壤的植物修复技术

本文报道用植草方法研究为DDT及其主要降解产物污染土壤的植物修复技术。在污染物的浓度为 0 .2 15mg/kg的土壤中 ,种植 10种草 3个月后DDT及其主要降解产物的总含量分别降低 19.6 %— 73.0 %。种植不同品种的草对土壤中污染物有不同的去除能力 ,其中以种植丹麦产的Taya草 (Per .ryegrass)与美国产的Titan草 (Tallfescue)为最强。用种植草的方法修复受DDT及其主要降解产物污染的土壤是一项可行的技术。在去除土壤中DDT的作用上 ,草的吸收是轻微的 ,只占原施药量的 0 .13%— 1.0 8% ,土壤中污染物消失的主要因素是土壤中生物降解作用的结果。     

太湖五里湖背角无齿蚌体内滴滴涕和六六六的残留

作为建立淡水"贝类观察"体系的初步尝试,选定2003年3月采自太湖五里湖水域的背角无齿蚌(Anodonta woodiana)为研究对象,测定其体内滴滴涕(DDT)和六六六(HCH)含量.除β型外,α型、γ型和δ型HCH异构体及p,p'-DDE,o,p'-DDT,p,p'-DDD,p,p'-DDT均在蚌样本中明显检出.∑DDTs湿重含量5.86～14.13 ng·g-1[平均(9.27±3.04) ng·g-1],高于∑HCHs湿重含量2.45～6.46 ng·g-1[平均(4.00±1.22) ng·g-1].p,p'-DDE、p,p'-DDD与α型、γ型HCH异构体分别为∑DDTs和∑HCHs的优势组分,说明太湖五里湖水域目前DDT的污染源可能很少,但存在较明显的新输入HCH.各蚌样的残留水平没有超过农业部、美国食品与药品管理局(FDA)和联合国粮农组织(FAO)颁布的最大限量.     

天津地区土壤中DDT的残留分布研究

采集了覆盖整个天津地区的188个土壤表层样品,并分析了样品中p,p′-DDE, p,p′-DDD, p,p′-DDT, o,p′-DDE, o,p′-DDD 和 o,p′-DDT等6种DDT代谢产物.结果表明p,p′-DDT 和 p,p′-DDE是表土中的主要污染物,其平均残留量分别为27 5和 18 8 ng@g -1.不同类型土壤∑DDT差异不显著.污灌区与非污灌区内的样品中 DDT及其代谢产物的差异不显著,但1970-1980年DDT施用量较高的地区如今土壤中的残留量均较高.土壤理化性质如pH以及TOC对DDTs的残留量有较显著的影响.禁用20年以来,DDT的总体残留量水平仍较高,是否依然有间或使用,有待探讨.     

DDT residue contamination in sediments from Lake Sibaya in northern KwaZulu-Natal,South Africa: Implications for conservation in a World Heritage Site

Maputaland in northern KwaZulu-Natal is a biodiversity hotspot and host to a number of ecologically important systems, including Lake Sibaya, southern Africa’s largest natural freshwater lake. The region is malaria endemic and this study reports the presence of DDT and its metabolites in the sediments of Lake Sibaya that have resulted from the widespread and continued use of DDT in the region. DDT residues (p,p′-DDT, p,p′-DDD, and p,p′-DDE) were detected at all 11 sites sampled, with total concentrations ranging from 0.8 to 123 ng g⁻¹. Total DDT concentrations at Lake Sibaya represent some of the highest levels reported in South Africa, with most samples exceeding sediment quality guideline values. The findings from this study raise concerns and indicate that urgent further work is needed to investigate the potential for bioaccumulation, which could adversely affect breeding fish, bird, and crocodile populations in the region. While this study represents the first report on DDT contamination in Lake Sibaya, results have important implications for a number of other aquatic ecosystems within the Maputaland ecoregion, as well as the many local people who depend on them.     

Fenton (H2O2/Fe) reaction involved in Penicillium sp. culture for DDT [1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane)] degradation

The purpose of this work was to demonstrate that a Fenton (H₂O₂/Fe) reaction was involved in DDT [1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane)] degradation in a culture of Penicillium sp. spiked with FeSO₄. A commercial DDT mixture (10% DDE [1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene], 30% o,p-DDT and 60% of p,p′ -DDT) of 10 mg L^{? 1} was used. Hydrogen peroxide (H₂O₂), tartaric acid and oxalic acid were identified at 18 h in culture media, with and without added DDT; this correlated positively with lowering of pH from 5.8 to 2.7. Lower concentrations of oxalic acid and H₂O₂ (7.9 and 52.6 mg L^{? 1}, respectively) occurred in media with DDT at 30 h, in comparison to that one without DDT mixture (27.9 and 65.3 mg L^{? 1}, respectively), at this time there was maximum degradation (87.7, 91.7 and 94.2%) for DDE, o,p-DDT and p,p′-DDT, respectively. We propose that the degradation of the DDT mixture by Penicillium sp. was through a Fenton reaction (H₂O₂/Fe) under acidic conditions produced in situ during the fungal culture amended with FeSO₄.