武汉市郊农田土壤中有机氯农药的残留分析

通过采集武汉市郊农田表层土壤,用GC-ECD法分析了土壤中HCH(六六六)、DDT(滴滴涕)及其代谢物的残留情况.结果表明:HCH残留低于DDT,∑HCHs介于0.18~18.90 ng.g-1,平均值为1.97 ng.g-1,∑DDTs介于1.82~165.34 ng.g-1,平均值为31.41 ng.g-1;残留水平较高的是p,p′-DDE、p,p′-DDD和p,p′-DDT.部分表层土壤中的∑DDTs超出了中国土壤环境质量标准的自然背景值.初步分析结果表明武汉市郊土壤中HCH及DDT的含量处于低浓度

异育银鲫幼鱼对饲料中赖氨酸的利用及需要量研究

以添加晶体氨基酸的半精制饲料饲喂异育银鲫幼鱼,通过69d的生长实验来确定其赖氨酸需要量。饲料以白鱼粉为主要蛋白源,饲料中的总赖氨酸含量分别为1.82%、2.32%、2.82%、3.32%3、.82%、4.32%和4.82%7个水平。实验在室内循环水养殖系统中进行,每种饲料随机3个重复。实验结果表明,异育银鲫能够利用饲料中的晶体赖氨酸、蛋氨酸。在投喂后3h,其血浆中的游离赖氨酸、蛋氨酸含量最高。当饲料中赖氨酸含量为3.32%时,异育银鲫的终末尾均重、特定生长率和鱼空壳占体重的百分比最高,肝体指数最低。当饲料

嗜水气单胞菌毒力与毒力基因分布的相关性

采用PCR扩增的方法对9株鱼源嗜水气单胞菌AEROM ONAS HYDROPHILA中的气溶素基因(AERA)、溶血素基因(HLYA)和丝氨酸蛋白酶基因(AHPA)进行了扩增。结果表明,6/9的A.HYDROPHILA中存在AERA基因,8/9的A.HYDROPHILA中存在HLYA基因,而在7/9的A.HYDROPHILA中检测到AHPA基因。通过比较基因检测的结果与嗜水气单胞菌对鲫鱼的致病性,发现AHPA阴性菌株是无毒株,强毒株都呈AERA+HLYA+AHPA+基因型。AERA+HLYA+AHPA+基

水生呼肠孤病毒研究进展

<正> 水生呼肠孤病毒为感染水生生物的一类呼肠孤病毒。自Meyers等1979年首次报道水生呼肠孤病毒的分离,迄今已分离鉴定出40余株水生呼肠孤病毒。与哺乳动物呼肠孤病毒一样,水生呼肠孤病毒主要通过呼吸肠道感染宿主,导致出血病及肝脏与胰腺疾病,在全球范围内对水产养殖业造成了严

阿斯旺高坝的生态环境问题

:通过对阿斯旺高坝和尼罗河的实际考察和生态环境监测数据的分析 ,介绍了埃及政府相关管理部门的官员和专家对阿斯旺工程的看法 ,对阿斯旺高坝及其生态环境问题进行了评述。认为阿斯旺工程是一个成功的工程 ,它对埃及发挥的巨大影响和积极作用是有目共睹的。它对生态环境的不利影响 ,确被很多批评者盲目地夸大了 ,其中也包含有政治因素。中国在修建水利工程时 ,要对环境的影响作出客观、科学的评价 ,并采取措施把不利影响减少到最小。阿斯旺高坝运行近 30年 ,在生态环境监测方面积累了丰富的数据 ,这些成果和结论对三峡工程具有

稀有鮈鲫的摄食率、排泄率和排粪率

中国科学院重点科研项目KS85－602;KZ952－S2－121资助

富营养化浅水湖泊沉水水生植被的衰退与恢复

对国外近年来有关富营养化浅水湖泊的退化与恢复方面的研究进展以及生物操纵作用作了述评．对有关富营养化湖泊沉水植被衰退的有代表性的3种假说也作了介绍．根据“八五”期间武汉东湖水生植被重建的研究工作和多年积累的湖泊水生植被调查资料，提出了长江中下游浅湖富营养化过程中沉水植技演替的模式．

鲤体长与体内元素富集数学模型

鲤体长与体内元素富集数学模型王继忠，徐小清（中国科学院水生生物研究所，武汉４３００７２）ＡＭＡＴＨＥＭＡＴＩＸＡＬＭＯＤＥＬＦＯＲＢＯＤＹＬＥＮＧＴＨＡＮＤＥＬＥＭＥＮＴＣＯＮＴＥＮＴＩＮＴＨＥＢＯＤＹＯＦＣＡＲＰ￥ＷａｎｇＪｉｚｈｏｎｇａｎｄＸｕＸ...

六种选矿药剂对藻类的毒性比较

本文评价了六种选矿药剂对藻类的毒性效应,它们对斜生栅藻的毒性大小排列顺序是:二号油>Fu>0145>Yx>MPA>S-808,96h-EC_(50)值分别为41.2,50.1,82.0,177.8,198.2和900ppm。六种选矿药剂对藻类毒性最大的是二号油,毒性最小的是S-808。对藻类细胞形态的观察结果表明,0145对藻类的细胞形态有轻度的致畸效应,在其它五种药剂的培养物中,均未发现畸变细胞。在室温下存放10d后MPA,0145和二号油,毒性明显下降,其下降速率的顺序是:MPA>0145>二号油。藻

Environmental mechanism of change in cyanobacterial species composition in the northeastern part of Lake Dianchi (China)

Environmental mechanism of change in cyanobacterial species composition in the northeastern part of Lake Dianchi (also called Macun Bay and Haidong Bay) was studied using canonical correlation analysis (CCA), but also bottom-up control and top-down control were fully discussed. Results from CCA suggest: (1) the abundance and dominance of Microcystis aeruginosa in Macun Bay and Haidong Bay are influenced by total phosphorus (TP), nitrate (NO3--N), nitrite (NO2--N), dissolved oxygen (DO) and water temperature (WT); (2) water temperature has a positive correlation with the abundance of M. aeruginosa and it also has negative correlations with the abundances of Anabaena flos-aquae and Aphanizomenonon flos-aquae; and (3) abundances of both Anabaena flos-aquae and Aphanizomenon flos-aquae have positive correlations with ammonia-N (NH4+-N). Furthermore, cyanobacterial species composition has no significant correlations with light and size-fractioned iron in this study. Grazers, cyanophages and viruses were able to control cyanobacterial blooms and change the composition of cyanobacterial species. Though we studied physical and chemical factors intensely enough, we still are not able to predict the change in the composition of cyanobacterial blooms, because of plankton system in a chaotic behavior.

Sorption, degradation and mobility of microcystins in Chinese agriculture soils: Risk assessment for groundwater protection

In the present paper, sorption, persistence, and leaching behavior of three microcystin variants in Chinese agriculture soils were examined. Based on this study, the values of capacity factor and slope for three MCs variants in three soils ranged from 0.69 to 6.00, and 1.01 to 1.54, respectively. The adsorption of MCs in the soils decreased in the following order: RR > Dha(7) LR > LR. Furthermore, for each MC variant in the three soils, the adsorption rate in the soils decreased in the following order: soil A > soil C > soil B. The calculated half-time ranged between 7.9 and 17.8 days for MC-RR, 6.0-17.1 days for MC-LR, and 7.1-10.2 days for MC-Dha(7) LR. Results from leaching experiments demonstrated that recoveries of toxins in leachates ranged from 0-16.7% for RR, 73.2-88.9% for LR, and 8.9-73.1% for Dha 7 LR. The GUS value ranged from 1.48 to 2.06 for RR, 1.82-2.88 for LR, and 1.76-2.09 for Dha(7) LR. Results demonstrated the use of cyanobacterial collections as plant fertilizer is likely to be unsafe in soils. (c) 2006 Elsevier Ltd. All rights reserved.

Experimental study on a diode-pumped passively mode-locking Nd : GdVO4/SESAM laser

We demonstrate a low-threshold and efficient diode-pumped passively continuous wave (CW) mode-locked Nd:GdVO4 laser with a reflective semiconductor saturable absorber mirror (SESAM). The threshold for the continuous wave was 0.36 W, and it is the lowest threshold for a continuous wave in a passively mode-locked Nd:GdVO4 laser to our knowledge. The maximum average output power of 1.82 W was obtained at a pump power of 6.65 W with a slope efficiency of about 29%. The CW mode-locked pulse duration was measured to be about 10.5 ps with a 116-MHz repetition rate.

Electroluminescence from Au/(SiO2/Si/SiO2) nanometer double barrier/p-Si structures and its mechanism

SiO2/Si/SiO2 nanometer double barriers (SSSNDB) with Si layers of twenty-seven different thicknesses in a range of 1-5 nm with an interval of 0.2 nm have been deposited on p-Si substrates using two-target alternative magnetron sputtering. Electroluminescence (EL) from the semitransparent Au film/SSSNDB/p-Si diodes and from a control diode without any Si layer have been observed under forward bias. Each EL spectrum of all these diodes can be fitted by two Gaussian bands with peak energies of 1.82 and 2.25 eV, and full widths at half maximum of 0.38 and 0.69 eV, respectively. It is found that the current, EL peak wavelength and intensities of the two Gaussian bands of the Au/SSSNDB/p-Si structure oscillate synchronously with increasing Si layer thickness with a period corresponding to half a de Broglie wavelength of the carriers. The experimental results strongly indicate that the EL originates mainly from two types of luminescence centres with energies of 1.82 and 2.25 eV in the SiO2 barriers, rather than from the nanometer Si well in the SSSNDB. The EL mechanism is discussed in detail.