Guo Jian-Yang, Wu Feng-Chang, Liao Hai-Qing, Deng Qiu-Jing, Li Wei, Zhang Run-Yu, Zhao Xiao-Li
State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang 550002, China.
Huan Jing Ke Xue. 2010 Jun;31(6):1589-93.
In order to reconstruct the chronology of 2,2-his (4-Chlorophenyl)-1,1,1-trichloroethane (DDT) input into the Hongfeng reservoir and assess the pollution issues, the temporal distribution of DDT in sediment core from Hongfeng reservoir was measured using GC/MS method, and the possible sources and potential risk assessment also had been identified. The DDTs (sum of p,p'- and o,p'-DDT, DDE and DDD) in sediment core were ranged from 7.6 to 23.7 ng/g, and roughly, ever decreased from the bottom to the surface sediment. In detail, a sharp decline of DDTs concentration in sediment was found from 1981 to 1983, followed by a tardy decrease trend to the present. The DDTs in sediment were mainly composed of p,p'-DDTs (sum of p,p'-DDT, DDE and DDD). The ratio of p,p'-DDTs to o,p'-DDTs (sum of o,p'-DDT, DDE and DDD) ranged from 5.1 to 8.4, which suggests that the DDTs in sediment were chiefly originated from the technical DDT. Meanwhile, the DDTs in sediments were dominated by the metabolites of DDT (DDD and DDE) and the ratio of DDT/(DDD + DDE) were between 0.31 and 0.84, indicating the DDTs in sediment were mostly stemmed from the historical usage. Besides, the vertical profile of the ratios of DDT/( DDD + DDE) and DDE/DDD indicate that possible usage of technical DDT still occurred in the drainage area of Hongfeng reservoir around 1990, although the usage of technical DDT in agriculture has been banned in 1983. The residue levels of DDE, DDD, DDT, and DDTs in surface sediment from Hongfeng reservoir were all between ERL and ERM, suggesting potential risk could occur, and the contamination of DDT in Hongfeng reservoir deserving more concerns.
为了重建2,2-双(4-氯苯基)-1,1,1-三氯乙烷(DDT)输入红枫湖水库的时间序列并评估污染问题,采用气相色谱/质谱法测定了红枫湖水库沉积物岩芯中DDT的时间分布,并确定了其可能来源及潜在风险评估。沉积物岩芯中的滴滴涕(p,p'-和o,p'-DDT、DDE和DDD的总和)范围为7.6至23.7 ng/g,大致上从底部到表层沉积物呈下降趋势。具体而言,1981年至1983年沉积物中DDT浓度急剧下降,随后呈缓慢下降趋势直至现在。沉积物中的DDT主要由p,p'-DDTs(p,p'-DDT、DDE和DDD的总和)组成。p,p'-DDTs与o,p'-DDTs(o,p'-DDT、DDE和DDD的总和)的比值在5.1至8.4之间,这表明沉积物中的DDT主要来源于工业DDT。同时,沉积物中的DDT以DDT的代谢产物(DDD和DDE)为主,DDT/(DDD + DDE)的比值在0.31至0.84之间,表明沉积物中的DDT大多源于历史使用。此外,DDT/(DDD + DDE)和DDE/DDD比值的垂直剖面表明,尽管1983年已禁止农业使用工业DDT,但1990年左右红枫湖水库流域仍可能存在工业DDT的使用情况。红枫湖水库表层沉积物中DDE、DDD、DDT和DDTs的残留水平均介于效应浓度低值(ERL)和效应浓度中值(ERM)之间,表明可能存在潜在风险,红枫湖水库中DDT的污染值得更多关注。