热带海洋环境中BHC和DDT的行为特征研究Ⅰ.中国珠江口区旱季BHC和DDT的含量与分布

本文于1994年11月用气相色谱法研究了旱季珠江口区环境中BHC和DDT的含量与分布。结果表明，表层海水BHC含量为0.187μg/L，DDT为0.080μｇ/L；底层海水BHC为0.117μｇ／L，DDT为0.506μｇ／L。沉积物BHC为11.15×10－9（干），DDT为33.46×10－9（干）。海水中的盐度、DO、C     

白洋淀水体、底泥及鲫鱼体内DDT、BHC污染状况研究

对白洋淀水体、底泥及鲫鱼肌肉中的ＤＤＴ及其衍生物和ＢＨＣ的残留量进行了测定研究，分别给出含量范围．研究表明，鱼体肌肉中ＢＨＣ的４种异构体的含量顺序（δ＞α＞γ＞β）与其在水和底泥中的含量顺序（α＞γ＞δ＞β）略有不同．鱼体肌肉中ＤＤＴ主要以代谢物Ｐ，Ｐ′ＤＤＥ形式存在．两种农药的污染具有明显的地域差异，位于府河入淀口及村庄附近的水体、底泥及鱼体肌肉中ＤＤＴ及其衍生物，ＢＨＣ含量较高，与１９７５—１９７７年检测结果相比，鲫鱼肌肉中ＤＤＴ及其衍生物残留量下降了５４２％，ＢＨＣ下降了８６９％．     

白洋淀几种不同食性鱼类对六六六、DDT的富集

对白洋淀几种不同食性鱼体内六六六和ＤＤＴ残留量分析表明，草食性鱼体内农药残留量最少，六六六含量为５９．３μｇ／ｋｇ，ＤＤＴ含量为２９．６μｇ／ｋｇ；其次是杂食性鱼类，六六六含量为９０．４μｇ／ｋｇ，ＤＤＴ含量为１０８．５μｇ／ｋｇ；肉食性鱼体内农药残留量最高，六六六含量为１１０．７μｇ／ｋｇ，ＤＤＴ含量为１２４．４μｇ／ｋｇ。鱼体对ＤＤＴ的浓缩因子为３１１～１２４４，明显高于六六六的１７７～３６８。鱼体内ＢＨＣ４种异构体的残留顺序为δ＞α＞γ＞β，与其在水体中的比例α＞γ＞δ＞β略有不同。鱼体内ＤＤＴ主要以代谢物ｐ，ｐ＇－ＤＤＥ的形式存在，但个别样品中少量的ｐ，ｐ＇－ＤＤＤ及ｏ，ｐ＇－ＤＤＴ的检出，表明白洋淀水生生态系统最近受到ＤＤＴ的轻度污染。本项研果与１９７５～１９７７年检测结果进行比较；白洋淀鱼体内六六六残留量显著下降，下降率为１５．８％～７９．２％；ＤＤＴ残留量却明显增加（草食性鱼类除外），增加率约为４７．８％～９７．８％。     

白洋淀水生食物链BHC、DDT生物浓缩分析

为了评价ＢＨＣ和ＤＤＴ在水生食物链的生物累积放大效应,对白洋淀地区端村水域生态系统水生生物对六六六、ＤＤＴ的富集沿食物生物营养等级而递增的规律性较强（当年生鲫鱼例外）,水体,底泥水生维管束植物,浮游动物、底栖动物,当年生鲫鱼及２龄乌鳢体内六六六残留量分别为：０．３μｇ／Ｌ,０．７μｇ／ｋｇ,１９．０μｇ／ｋｇ,３０．０μｇ／ｋｇ,６０．９μｇ／ｋｇ,１７．２μｇ／ｋｇ、１１０．７μｇ／ｋｇ,ＤＤＴ     

两种金属和两种农药对草鱼不同发育阶段的毒性效应

进行了金属和农药对草鱼不同发育阶段影响的试验。结果表明,对草鱼胚胎孵化率的影响,96h的EC_(50)值分别为:Cd~(2+)0.078mg/L;Cu~(2+)0.17mg/L;丙体六六六1.0mg/L;对硫磷1.0mg/L。畸形症状呈现出草鱼胚胎卵黄囊水肿,心脏发育受阻而形成管状心脏、胚体弯曲(弯体)等。草鱼的不同发育阶段对金属的敏感性存在着差异:Cd~(2+)96h的LC_(50)值,胚胎为0.1—0.5mg/L;10日龄草鱼苗为0.34mg/L;120日龄草鱼种为8mg/L.Cu~(2+)96h的LC_(50)值,胚胎为0.3—0.5mg/L;10日龄草鱼苗为0.11mg/L;120日龄草鱼种为0.59mg/L.     

黄海江豚体脂中有机氯的含量及与其年龄等相关性的研究

从江苏吕泗采集到18头黄海产江豚,测定了体脂中DDTs和BHCs含量.DDTs浓度范围为2.27—77.69μg/g.BHCs为0.42—7.24μg/g.黄海江豚体脂中DDTs的含量比日本海和长江江豚低,BHCs含量则高许多.在雌性中,四龄前DDTs和BHCs的蓄积浓度随年龄增长而增加,至4龄左右,随年龄的增长而下降.     

Measurement of flow speed in the channels of novel threadlike structures on the surfaces of mammalian organs

There have been several reports on novel threadlike structures (NTSs) on the surfaces of the internal organs of rats and rabbits since their first observation by Bonghan Kim in 1963. To confirm this novel circulatory function, it is necessary to observe the flow of liquid through the NTS as well as the structurally corroborating channels in the NTS. In this article, we report on the measurement of the flow speed of Alcian blue solution in the NTSs on the organ surfaces of rabbits, and we present electron microscopic images depicting the cribrous cross-section with channels. The speed was measured as 0.3 ± 0.1 mm/s, and the flow distance was up to 12 cm. The flow was unidirectional, and the phase contrast microscopic images showed that the NTSs were strongly stained with Alcian blue. The ultrastructure of the NTSs revealed by cryo-scanning electron microscopy and high-voltage electron microscopy showed that (1) there were cell-like bodies and globular clumps of matter inside the sinus of the channel with thin strands of segregated zones which is a microscopic evidence of the liquid flow, (2) the sinuses have wall structures surrounded with extracellular matrices of collagenous fibers, and (3) there exists a cribriform structure of sinuses. To understand the mechanism for the circulation, a quantitative analysis of the flow speed has been undertaken applying a simplified windkessel model. In this analysis, it was shown that the liquid flow through the NTSs could be due to peristaltic motion of the NTS itself. Baeckkyoung Sung and Min Su Kim contributed equally to this work.     

气相色谱法测定人参中BHC残留量

本文研究了一种快速、简便、准确地测定人参中ＢＨＣ残留量的气相色谱法。人参样品经正己烷—丙酮冷浸泡,超声萃取,磺化法处理后,萃取液直接上机测定。本方法对人参中ＢＨＣ各异构体的回收率均在８５％以上。变异系数小于１０％。与其它方法相比,本法耗时少,价格廉,结果准确,适合批量样品测定。     

Impact of some chlorinated pesticides on the haematology of the fish Cyprinus carpio and Puntius ticto

The effects of pesticides on blood characteristics and histological changes in erythrocytes of the fish species Cyprinus carpio and Puntius ticto were studied. The fishes were exposed to sub lethal concentrations of different chlorinated pesticides namely aldrin, dieldrin, DDT, BHC and chlordane for 10, 20 and 30 d in continuous flow-through test. The LCso values were calculated based on acute toxicity tests and the sublethal doses were arrived at for chronic bioassay studies. Results showed an increase in haemoglobin content of both Cyprinus carpio and Puntius ticto in case of aldrin and dieldrin. Haemoglobin content reduced from an initial 13 g/100 ml to 8.07 and 10.15 g/100 ml in case of Cyprinus at the end of ten days exposure to aldrin and dieldrin respectively, and gradually increased to 8.7 g/100 ml and 10.15 g/100 ml after 20 d of exposure. The haemoglobin content after 30 d exposure to aldrin and dieldrin was 10.15 g/100 ml and 11.6 g/100 ml respectively. In case of Puntius ticto, the haemoglobin content in control fishes recorded was 12.8 g/100 ml while in case of fish exposed to aldrin, the haemoglobin content reduced initially on ten days exposure to 10.15 g/100 ml and increased to 11.6 g/100 ml and 13.0 g/100 ml during twenty days and thirty days exposure respectively. This trend was also observed with dieldrin in both the fishes studied. Red blood cells were also counted in case of all the pesticides and exposure periods with respect to Cyprinus carpio and Puntius ticto. Irrespective of the species and pesticide, the RBC counts uniformly showed decreasing trend with the increase in exposure period, while packed cell volume, PCV(%) showed increasing trend with respect to increase in exposure period in case of aldrin and dieldrin in both the fishes. But DDT, BHC and chlordane showed decreasing trend in PCV(%) values with increasing periods of exposure.     

Fate of BHC in the terrestrial ecosystem

The fate of BHC in the terrestrial ecosystem was investigated under both laboratory and field conditions. The uptake, accumulation and degradation of BHC in earthworms and corn plants were studied. Earthworms could absorb and accumulate BHC residues from soil. Statistically, significant correlation existed between the amounts of BHC in soil and in earthworms. Different species of earthworms appeared to concentrate BHC in their bodies to different extents. In a terrestrial ecosystem, the uptake, accumulation of BHC residues by soil animals and plants had an effect on each other.