黄鳝血清甲状腺激素的检测与分析

用放射免疫测定法测定了４４ 条不同性别黄鳝（Ｍｏｎｏｐｔｅｒｕｓ ａｌｂｕｓ Ｚｕｉｅｗ ）血清总甲状腺激素Ｔｈｙｒｏｘｉｎｅ Ｔ３,Ｔｒｉｉｏｄｏｔｈｙｒｏｎｉｎｅ Ｔ４）含量。结果表明：（１）５～９ 月雄性Ｔ３ 含量一直较高;雌性５～６ 月Ｔ３含量比雄性和兼性低,７ 月以后升至与兼性持平,８～９ 月达到与雄性持平,高于兼性含量,升幅较大,但差异不显著（Ｐ＞ ０．０５）。（２）５～６ 月雄性Ｔ４ 含量稍高于其它性别,７ 月以后有所降低;雌性与兼性 Ｔ４ 含量与变化趋势基本相同。（３）同性别Ｔ４ 含量比Ｔ３ 含量要低得多。甲状腺激素可能与性逆转关系不大,其作用在于促进代谢与生长。     

石油开发污染物毒性监测的实验生物筛选Ⅰ:钻井泥浆对水生动物的毒性比较

用静水式试验方法评价和比较了两种钻井泥浆的水可溶部份对斑节对虾仔虾、罗氏沼虾仔虾、虾虎鱼和剑尾鱼等4种水生动物的急性毒性。结果表明：泥浆水溶性成分对班节对虾仔虾、罗氏沼虾仔虾、虾虎鱼和剑尾鱼的半数致死浓度均明显大于10000mg／L（1％）,但斑节对虾仔虾对泥浆水可溶性成份的敏感性高于其余3种动物,适于钻井泥浆毒性试验。可以认为在试验条件下两种泥浆是无急性毒性的物质,但由于泥浆组成的复杂性,综合评价泥浆对水环境的影响时,需探讨其对底栖生物的影响。     

氟乐灵对斑节对虾卵和幼体的毒性研究

采用静水生物试验法测定了氟乐灵对斑节对虾卵和幼体的急性毒性。结果表明：氟乐灵对斑节对虾无节幼体、蚤状幼体、糠虾幼体和仔虾的２４ｈＬＣ５０／×１０－６分别是１．６８，０．８３，１．８４和２．０９；４８ｈＬＣ５０／×１０－６分别是０．７６，０．５３，１．０９和１．５１。５．０１×１０－６氟乐灵浸浴受精卵１２ｈ，５０％的受精卵可孵化。第２２天仔虾用１０×１０－６以下浓度的氟乐灵浸浴５ｍｉｎ，对其存活率无影响。     

洪湖微齿眼子菜种群遗传多样性研究

采用RAPD方法研究了洪湖微齿眼子菜种群的遗传多样性,并初步探讨了它的遗传结构及影响因素。在97个RAPD标记中有28条(28.87%)是多态性标记,Shannon信息多样性指数分析表明该种群总的遗传多样性为0.193,说明洪湖微齿眼子菜种群的遗传多样性水平较低。研究发现距离和种群发展历史对洪湖微齿眼子菜种群的遗传结构有重要影响。     

罗非鱼遗传背景的研究进展

研究鱼类的遗传背景 ,保护天然群体的基因库 ,维持生物多样性是物种资源保护开发的重要主题之一。生物多样性包括三个层次 :生态多样性、物种多样性、遗传多样性 ,其中遗传多样性是重要的组成部分 ,它是物种多样性的基础 ,也是评价自然生物资源的重要依据 ,在一定程度上反映该物种在自然或人为条件下对环境改变的适应能力。研究生物的遗传多样性就必须找到特异遗传标记 ,并且应该是随机选取能够稳定遗传下去 ,反映生物个体或群体的遗传学特征 ,代表其遗传组成 ,有足够变异类型的标记组合。用以研究鱼类遗传多样性和遗传标记的方法有很多种 ,…     

兴奋性毒性与神经和精神疾病的关系

根据Ｏｌｎｅｙ及其同事［１］以及更早的Ｌｕｃａｓ、Ｎｅｗｈｏｕｓｅ和其他研究者的工作,Ｏｌｎｅｙ在７０年代提出了兴奋性毒性（ｅｘｃｉｔｏｔｏｘｉｎ）的原始概念及兴奋性毒性这一专门术语。这些工作认为过量的兴奋性氨基酸（ｅｘｃｉｔａｔｏｒｙａｍｉｎｏａｃｉｄ,ＥＡＡ）─—谷氨酸（ｇｌｕｔａｍｉｃａｃｉｄ,ＧＬＵ）、ＧＬＵ的类似物门冬氨酸（ａｓｐａｒｔｉｃａｃｉｄ,ＡＳＰ）等─—能过度兴奋中枢神经系统（ｃｅｎｔｒａｌｎｅｒｖｏｕｓｓｙｓｔｅｍ,ＣＮＳ）内的ＧＬＵ敏感神经元而达到使它们致死的程度。在过去…     

八种硝基苯类化合物对发光菌的联合毒性

以淡水发光菌青海弧菌为指示生物,VeritasTM微孔板光度计为发光强度测试设备,分别测定了8种硝基苯类化合物及其混合物对发光菌的发光抑制毒性.结果表明8种硝基苯类化合物的剂量-效应关系都可用Weibull模型有效描述,从模型估算的单个化合物的半数效应浓度值,可知对发光菌的毒性大小顺序为邻硝基苯胺＞对硝基苯胺＞对硝基苯酚＞对硝基甲苯＞邻硝基苯酚＞间硝基苯酚＞间硝基苯胺＞硝基苯.按等毒性浓度比方法配制混合物进行联合毒性实验,结果表明这8种硝基苯类化合物对发光菌的联合毒性可用独立作用(IA)预测,独立作用(IA)倾向于高估了它们的联合毒性.     

5种除草剂对白鲢鱼种急性毒性试验

以白鲢(Hypophthalmicthysmolitris)为实验材料,研究常用除草剂对鱼类的毒性效应。结果表明:采用直线回归法求得的96hLC50值分别为:2,4_D丁酯0.185mg/L,可信限0.138~0.247mg/L;丁草胺0.080mg/L,可信限0.067~0.097mg/L;使它隆3.80mg/L,可信限2.68~5.40mg/L;艾割18.60mg/L,可信限14.80~23.32mg/L;嗪草酮108.80mg/L,可信限91.46~129.72mg/L。对鱼类安全浓度分别为0.019mg/L,0.38mg/L,0.008mg/L,1.86mg/Land10.88mg/L。     

A Model Describing the Time Course and Variability in Toxicity of Hydrophobic Chemicals to Aquatic Organisms-Toxicity of chlorinated benzenes to marine algae

The growth of Chlorella marine, Nannochloris oculate, Pyramimonaos sp., Platymonas subcordiformis and Phaeodactylum tricornutum exposed to chlorobenzene, 1,2-dichlorobenzene, 1, 2, 3, 4-tetrachlorobenzene and pentachlorobenzene was tested. The Boltzman equation was used to describe organism growth. The time course for uptake of hydrophobic organic chemicals (HOCs) by aquatic organisms was expressed by incorporating growth and, if desired, the effect of metabolism into the HOC bioconcentration process. The probability of any given concentration of HOCs in the organisms causing a specified toxic endpoint was expressed with a modified Weibull distribution function. The combined bioconcentration and probability equations were tested with data for time course of incubation of algae exposed to chlorinated benzenes (CBs). A set of parameters, including the uptake rate constant k1, the elimination rate constant k2 and thereafter the bioconcentration factor on a dry weight basis, BCFD, the critical HOC concentration in the organism resulting in a specified toxic endpoint, C*A, and the spread factor, S, could be obtained by fitting only experimental data for percent growth inhibition(%)-time-CB exposure concentration. The average coefficients of variation within CBs were 15.2% for BCFD, 21.0%for k1, 18.3% for k2, 8.1% for C*A and 9.7% for S. The variability in toxicity (such as EC10, EC50, ECg0) derived from the model equations agreed well with those experimentally observed.     

TOXICITY OF CHLORINATED BENZENES TO MARINE ALGAE

Towhomcorrespondenceshouldbeaddressed.ImODUcr0NMarinealgaearethemosttwortantprimaryproducersandplayanimPortantroleindetenniningthefateofpersistenthydrophobicorganicchdricaIs(HOCs)inthernarineeresySteIn.TheirhydrophobicnatureresultsinanenhanedassociationwithH0Csintheanwatercolurnn(Swackhameretal.,l993).HOCfateisdowhnatalbytwoproanes,verti-caltransporttobottomsedimentSbydeadCellsandtIansportintothefood-webbyrooplanktongraring.TherelativetoortanceofthetwoproassesdependsonprharyproduCtion…     

Toxicity of five phenolic compounds to brine shrimp Artemia sinica (Crustacea: Artemiidae)

The acute toxicity of five phenolic compounds each to 15 d old Artemia sinica was determined in this study. The brine shrimp A. sinica was hatched from the encysted dry eggs(Bohai Bay Brand) produced by Dongying Ocean Artemia Co., Ltd., China at 27℃± 1℃ in pre-filtered(through pores of 0.45 μm in diameter) and autoclaved seawater(salinity 31, pH 7.5–8.0) in a cilindroconical glass beaker(2000 mL in volume) under continuous illumination(provided by a side set 20 W fluorescent lamp) with slight aeration. Ten Artemia individuals from the same batch of the hatched were cultured in 10 mL toxicant solution prepared with seawater(salinity 31, pH 7.5–8.0) at room temperature(about 20℃) to determine 24 h, 48 h and 72 h medium lethal concentration(LC50) of 5 phenolic compounds each. It was found that the toxicity of n-heptylphenol was the highest followed by nonylphenol, t-butylphenol, 2,4-dichlorophenol and bisphenol A in order. The LC50 values of the 5 compounds were calculated with regression analysis. The real concentration(in μg- L1) of 5 phenolic compounds each in toxicant solutions was measured with GC/MS analysis. Significant loss of phenolic compounds caused by either adsorption or desorption was not found. The significant difference of LC50 values was found among the five compounds 3 exposure times each. The range between the highest no-observed-effect concentration(NOEC) and 100% death causing concentration of five phenolic compounds each was determined. The toxicity in term of 24 h LC50 value of n-HP was 9.10 times higher than that of BPA, 1.71 times higher than t-BP, 1.53 times higher than 2,4-DCP and 1.36 times higher than NP, respectively.     

坐标拟合的双向解算与矩阵系数的生成

在地理信息系统、机助制图等应用中,四参数与七参数拟合是坐标转换的重要方法。采取重合点坐标可获得正反算两套拟合参数,从而实现正反算求解。本文阐述了基于四参数与七参数这两种转换模型,通过重组矩阵模型,推求反算数学模型,采用一套拟合参数进行正反算的方法,并给出相应系数矩阵的自动生成程序和解算过程。     

A model describing the time course and variability in toxicity of hydrophobic chemicals to aquatic organisms

The growth of Chlorella marine, Nannochloris oculate, Pyramimonaos sp., Platymonas subcordiformis and Phaeodactylum tricornutum exposed to chlorobenzene, 1,2-dichlorobenzene, 1,2,3,4-tetrachlorobenzene and pentachlorobenzene was tested. The Boltzman equation was used to describe organism growth. The time course for uptake of hydrophobic organic chemicals (HOCs) by aquatic organisms was expressed by incorporating growth and, if desired, the effect of metabolism into the HOC bioconcentration process. The probability of any given concentration of HOCs in the organisms causing a specified toxic endpoint was expressed with a modified Weibull distribution function. The combined bioconcentration and probability equations were tested with data for time course of incubation of algae exposed to chlorinated benzenes (CBs). A set of parameters, including the uptake rate constant k ₁, the elimination rate constant k ₂ and thereafter the bioconcentration factor on a dry weight basis, BCF _D, the critical HOC concentration in the organism resulting in a specified toxic endpoint, C _A ^* , and the spread factor, S, could be obtained by fitting only experimental data for percent growth inhibition(%)-time-CB exposure concentration. The average coefficients of variation within CBs were 15.2% for BCF _D, 21.0% for k ₁, 18.3% for k ₂, 8.1% for C _A ^* and 9.7% for S. The variability in toxicity (such as EC₁₀, EC₅₀, EC₉₀) derived from the model equations agreed well with those experimentally observed.     

Acute Toxicity of Formalin to the Red-tide Dinoflagellate Prorocentrum minimum Schiller (Protozoa, Mastigophora)

1Introduction Red tides occur in recorded history,but in recentyears there is a global increase in the number of theseevents due to coastal pollution and other unclear fac-tors.Some kinds of red tides cause mass deaths of cul-tured animals and thus cause heavy economic losses forcoastwise mariculture(Nakanishi et al.,1996;Changet al.,1998;Zhu et al.,1998;Tada et al.,2001).The investigation on red tide control,however,rem-ains insufficient(Burkholder,1998;Edwards and Clark,1999).Although man…     

5种药物对方斑东风螺面盘幼虫的急性毒性

在水温29.0～29.5℃、盐度28.5条件下,采用静水试验法对5种常用药物对方斑东风螺面盘幼虫的急性毒性进行了研究。结果表明:各种药物的24 hLC50、48 hLC50、96 hLC50和安全浓度分别为:高锰酸钾1.71、1.04、0.55和0.115 mg.L-1,新洁尔灭78.58、28.90、6.06和1.17 mg/L,硫酸锌4.52、2.36、0.62和0.193 mg/L,制霉素2.36×104、1.46×104、0.64×104和0.168×104 U.L-1,甲醛10.9、7.11、3.66和0.908μL.L-1。