镉对鲤鱼磷酸酶活性的影响

研究了重金属镉对鲤鱼明脏，肝胰脏，肠，血液等组织酸性磷酸酶（ACP）和碱性磷酸酶（AKP）活性的影响，结果表明，受水中16mg/L影响，肝胰脏的ACP活性显著升高；肾脏的ACP的活性在32mg/L组显著降低；血液的ACP活性在16mg/L,32mg/L组均显著降低，肠道的ACP活性在8mg/L,16mg/L,32mg/L 3种浓度下影响均不明显，肾脏，肠道的AKP活性在16mg/L组显著降低，在31mg/L组极显著降低，体外试验表明，镉能直接抑制AKP的活性，而对ACP不产生直接影响。     

Quantitative structure activity relationships for carp kidney ATPase endpoint

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低pH对草鱼血液酸碱平衡的影响

研究了低pH(6.0—4.0)对草鱼血液酸碱平衡、p_(o2)及p_(co2)的影响,结果表明,低pH引起草鱼严重的酸血症.亚致死pH(6.0—5.0)时,血液酸碱平衡的影响主要表现为碱贮备[HCO_3]的丧失,血液pH的明显下降经机体缓冲调节可趋于稳定.致死低pH(4.0)时,血液pN和[HCO_3]下降均非常显著,并在96h内随酸化时间延长而日趋严重.仅在pH≤4.0的酸水中草鱼存在低氧症影响问题.草鱼是一种酸敏感性鱼类,为确保成鱼在天然水体的生存和繁育,水质pH至少应维持在6.0以上.     

羟基多溴联苯醚对鲤鱼急性毒性及定量结构活性关系

羟基多溴联苯醚是一类具有环境风险的新兴污染物,它们已经在众多环境介质甚至人体内广泛存在。参照GB/T13267-91标准方法,采用静态生物急性毒性试验,测定了6种羟基多溴联苯醚(2′-OH-BDE7、4′-OH-BDE17、2′-OH-BDE28、2′-OH-BDE68、4′-OH-BDE90和2′-OH-BDE123)对普通鲤鱼的急性毒性96 h-LC50值,分别为697、1 130、854、550、644和522 ng.mL-1。除4′-OH-BDE17为高毒物质外,其他5种OH-PBDEs均为剧毒物质,高溴代的2′-OH-BDE123毒性最大。选用OH-PBDEs的KOW参数及由MOPAC软件PM3算法计算出的16个量子化学参数(EHomo、qBr+、ELumo等)为描述符,运用一元线性回归分析分别研究了96 h-LC50与他们之间的相关关系。结果表明:lgKOW和ELumo与6种羟基多溴联苯醚的96 h-lg LC50表现出较好的相关性,复相关系数均大于0.96,根据方程得到的96 h-lg LC50预测值与实验值基本相同,进一步对环境中广泛检出的其它OH-PBDEs的96 h-LC50值也进行了预测。     

鲢鱼放养控制北京城市河湖水华试验研究

介绍了利用鲢鱼控制北京城市河湖水华的试验研究,通过不同放养密度(0、17、51和103 g/m3)的现场围隔试验,对鲢鱼放养对水体水质和浮游生物的影响进行了分析.研究结果表明,鲢鱼放养使有鱼围隔中浮游生物量极低,从而使浮游植物基本不受浮游动物影响,而直接受鱼类影响;同时,中等密度(51 g/m3)的鲢鱼放养使水华蓝藻和微小藻的生长均得到了有效抑制,使藻类生物量最低.     

重庆境内江河水域渔业环境特点及对船体网箱养鱼的影响

重庆境内河流属长江水系，以长江，嘉陵江，涪江等河流为骨干和主体，水域面积８．２５万ｈａ，占水域总面积的７６．４％，船体网箱养鱼是近年来在该地区兴起并迅速发展的鱼类集约化养殖方式。本文根据船体网箱养鲤试验结果和有关资料，分析了重庆境内江河水温，含氧量，流速，含沙量，浮渣，工业污染特点及对船体网箱养鱼的影响，拟合了养殖舱内，外流速关系及含沙量与透明度关系，并就船体网箱养鱼的进一步发展提出了措施。     

七种染料对鲤鱼肝微粒体芳烃羟化酶的诱导

以鲤鱼肝微粒体为实验体系,研究了七种染料化合物对其芳烃羟化酶（AHH）的诱导,发现七种染料都可诱导AHH的活性,随染料浓度增大AHH的活性升高。七种染料对AHH活性诱导能力大小为：酸性红B＞派拉丁蓝RRN＞普拉红B＞活性艳红K－2BP＞活性艳红K－2G,媒介大红S－80＞分散红E－4B,与其毒性大小相关。     

Effects of synthetic pyrethroids and methidation on activities of some digestive enzymes in carp (Cyprinus carpio L.)

Abstract

The effects of pyrethroid pesticides (deltamethrin, permethrin and cypermethrin) and an organophosphate ester (methidation) on the activities of carp trypsin, α‐chymotrypsin, carboxypeptidase A and lipase were studied. The enzymes were isolated from the gastrointestinal tract and the effects of the pesticides were investigated during incubation for 5 min. The activity of trypsin was influenced only slightly by the presence of deltamethrin and methidation, whereas permethrin and cypermethrin caused significant inhibition. The pyrethroid pesticides at lower concentrations resulted in a slight activation of α‐chymotrypsin. Methidation inhibited the α‐chymotrypsin activity by about 20%. These pesticides modified the lipase activity to a lesser extent; the highest inhibition was measured with cypermethrin. The carboxypeptidase A activity was inhibited by both pyrethroid pesticides and methidation. The results suggest that these pesticides might interact with the active conformation of the studied hydrolytic enzymes, resulting in changes in their activities.     

Evaluation of food chain transfer of the antibiotic oxytetracycline and human risk assessment

There has been recent concern regarding the possibility of antibiotics entering the aquatic food chain and impacting human consumers. This work reports experimental results of the bioconcentration of the antibiotic oxytetracycline (OTC) by the Asian watermeal plant (Wolffia globosa Hartog & Plas) and bioaccumulation of OTC in watermeal and water by the seven-striped carp (Probarbus jullieni). They show, for the first time, the extent to which OTC is able to transfer from water to plant to fish and enter the food chain. The mean bioconcentration factor (dry weight basis) with watermeal was 1.28 × 10³ L kg⁻¹. Separate experiments were undertaken to characterize accumulation of OTC by carp from water and watermeal. These showed the latter pathway to be dominant under the conditions employed. The bioconcentration and biomagnification factors for these processes were 1.75 L kg⁻¹ and 2 × 10⁻⁴ kg g⁻¹ respectively. Using an aqueous concentration range of 0.34–3.0 μg L⁻¹, hazard quotients for human consumption of contaminated fish of 1.3 × 10⁻² to 1.15 × 10⁻¹ were derived.