用14C示踪技术研究摇蚊幼虫对农药的富集作用

摇蚊幼虫是淡水湖泊中分布广泛、数量极大的底栖动物。它们生活在底泥中,位移能力很小,个体又较大,被认为是水质监测和生态毒理学研究的理想生物。底栖动物能大量富集水中微量的有毒物质,这已有许多报道,而有关摇蚊幼虫富集底泥中的有毒物质的报道甚少,国内至今尚未见报道。摇蚊幼虫富集毒物与其它底栖动物比较,其生态学意义更大,因为摇蚊幼虫除了作为鱼饵通过水生食物链浓缩和转移毒物外,大量的幼虫终将羽化为成虫,一批批飞离水体,有毒物质有可能较快地被消除掉。     

二种除草剂遗传毒性的研究

以黄鳝为试验材料,研究了艾割和使它隆二种除草剂对鱼类的致突变性。对经腹腔注射染毒上述二种除草剂的受试黄鳝,通过对其活体肾细胞染色体数目和形态的观察,分析其突变率。研究结果(经t检验)显示:艾割和使它隆二种除草剂分别在其试验最低受试剂量50mg/kg和8.0mg/kg即可引起黄鳝的染色体畸变。采用SOS/Umu显色试验研究,在SOS/Umu试验中,使它隆和艾割2个受试除草剂可以诱发SOS阳性反应,且呈明显的剂量-效应关系。试验表明这二种除草剂具有遗传毒性,应对这二种除草剂严加管控,避免其对环境的影响。     

降解除草剂阿特拉津的藤黄微球菌AD3菌株的分离、鉴定和降解特性研究

用富集培养法从农药厂的工业废水和污泥的混合物中分离到能够降解除草剂阿特拉津的AD3菌株,通过16SrRNA基因序列分析和Biolog细菌自动鉴定仪微量平板测定,该菌株被鉴定为藤黄微球菌(Micrococcusluteus).在以阿特拉津为唯一氮源(500μg·mL-1)的基本培养基中,AD3菌株能在48h内使阿特拉津降解97%以上.对AD3菌株和Pseudomonassp.ADP菌株的阿特拉津氯水解酶基因中间区的核苷酸序列和对应氨基酸序列进行比对结果表明,它们的核苷酸序列和氨基酸序列分别有5个位点和4个位点不同,核苷酸序列和氨基酸序列的类似性分别为99.1%和97.7%.     

用键合硅柱和色谱技术分析水中快杀稗残留

本文提供了两种简便、快速、灵敏、经济的快杀稗残留分析方法。用C_8键合硅柱萃取、富集水中的快杀稗,与MTBSTFA衍生,用GC-FID测定。添加回收率为90—108％,检测极限为1ppb。HPLC法,水样不必净化可直接测定,检测极限为20ppb。水样浓度过低时,需用C_8键合硅柱萃取,富集后用HPLC测定,20ppb的添加回收率为101.3％,可检测到2ppb。     

转bar及NIa基因白菜的田间生物学及经济性状调查

对转入除草剂抗性基因bar及来自病毒TuMV的／VIa基因的不结球白菜纯合株系二代进行了田问生物学性状调查,结果表明，转基因白菜的植物学性状与其未转基因对照材料相比，无明显差别；但在涉及其生存竞争力的一些生物学性状，如发芽势、花粉活力、种子库存力等方面，比对照材料弱，其经济性状也比对照稍差．获得的转基因性状——除草剂抗性，能稳定遗传，并在田间很好表达；NIa基因介导的TuMV抗性在露地开放栽培条件下，不能很好表达，转基因株染病较重．对产生以上现象的原因进行了分析讨论．图3表5参16     

阿特拉津对不同肥力土壤磷酸酶的影响

通过室内恒温培养法，研究除草剂阿特拉津对4种长期定位施肥处理下的土壤的磷酸酶活性的影响。试验结果表明，在阿特拉津质量分数不同和处理时间长短不同的情况下，阿特拉津对土壤磷酸酶的活性既有激活作用又有抑制作用。在试验过程中，4种不同肥力的土壤其磷酸酶活性随着处理时间的延续而呈现出“降低→升高→降低→升高”的消长趋势。不同阿特拉津质量分数对磷酸酶的影响没有规律，同一质量分数处理既有激活作用，也有抑制作用。在4种不同肥力的土壤中，磷酸酶活性最高的是以氮、磷、钾无机肥配合有机肥施用的土壤。     

Rapid assays for environmental and biological monitoring

Abstract

Rapid, inexpensive, sensitive, and selective enzyme‐linked immunosorbent assays (ELISAs) now are utilized in environmental science. In this laboratory, many ELISAs have been developed for pesticides and other toxic substances and also for their metabolites. Compounds for which ELISAs have recently been devised include insecticides (organophosphates, carbaryl, pyrethroids, and fenoxycarb), herbicides (s‐triazines, arylureas, triclopyr, and bromacil), fungicides (myclobutanil), TCDD, and metabolites of naphthalene and toluene. New rapid assays have been developed for mercury.     

Population dynamics in Daphnia Magna as modified by chronic tetradifon stress

Abstract

Two Daphnia magna offsprings (animals from the first and third brood) whose parentals (F₀‐generation) were exposed during 21 days to different tetradifon (4‐chlorophenyl 2,4,5‐trichlophenyl sulfone) concentrations, were transferred to a pesticide free medium during 21 days (recovery period). The algae Nannochloris oculata (5x10⁵ cells/mL) was used as food. In this recovery study, survival, growth and reproduction (mean total young per female, mean brood size, onset of reproduction and mean number broods per female) were assessed as individual parameters and the intrinsic rate of natural increase (r) as population parameter, for F₁ generation (1st and 3rd broods). Reproduction was still reduced in F₁ (1st and 3rd broods) generation daphnids from parentals (F₀) exposed to 0.18 mg/L tetradifon and higher concentrations even after 21 days in clean water. However, survival was not significantly different (p>0.05) in those F1 offsprings from parentals pre‐exposed to the acaricide. Growth was still reduced in F1 daphnids from parentals pre‐exposed to 0.10–0.44 mg/L tetradifon. The intrinsic rate of natural increase (r) was still affected in Fl generation daphnids, specially in those from the third brood. Therefore, Fl generation D. magna offsprings from a parental generation (F0) previously exposed to the acaricide tetradifon were not able to recuperate completely when a recovery period of 21 days was allowed.     

Aged and bound herbicide residues in soil and their bioavailability part 2: Uptake of aged and non‐extractable (bound) [carbonyl‐14C] methabenzthiazuron residues by maize

Abstract

[Carbonyl‐ C]methabenzthiazuron (MBT) was applied to growing winter wheat in an outdoor lysimeter. The amount applied corresponded to 4 kg Tribunil/ha. 140 days after application the 0–2,5 cm soil layer was removed from the lysimeter. This soil contained about 40 % of the applied radioactivity. Using 0,01 M CaCl₂ solution or organic solvents, the extractable residues were removed from the soil. The bioavailability of the non‐extractable as well as aged residues remaining in the soil was investigated in standardized microecosystems containing 1.5 kg of dry soil. During a 4 weeks period the total uptake (4 maize plants/pot) amounted up to 3,6; 2,2; and 0,9 % of the radioactivity from soils containing aged MBT residues, MBT residues non‐extractable‐with 0,01 MCaCl₂ or MBT residues non‐extractable with organic solvents, respectively. About 20 % of the radioactivity found in maize leaves represented chromatographically characterized parent compound. At the end of the plant experiment the soil was extracted again with 0,01 M CaCl₂ and with organic solvents. The soil extracts and also the organic phases obtained from the aqueous fulvic acid solution contained unchanged parent compound.     

EFFECTS OF DIPOTASSIUM ENDOTHALL ON ROOTED AQUATICS AND ADULT AND FIRST GENERATION BLUEGILLS1

ABSTRACT: A 0.31-ha pond was treated with 5.0 mg/l dipotassium endothall on May 31, 1973, and the effects of this treatment on the rooted aquatics, on bluegill reproduction, survival, and growth, and on the buildup of endothall residues in bluegill flesh was investigated. The treatment eliminated Myriophyllum exalbescens, Ceratophyllum demersum, Potamogeton crispus, and Anacharis canadenis during the first season, however, all but C. demersum became reestablished the following year. Little endothall was incorporated into edible bluegill flesh. The dipotassium endothall did not affect the number of young-of-the-year (YOY) bluegills produced by the original adult stocking during the year of treatment and the year following treatment and did not affect the reproduction of first generation bluegills. The survival of adult and first generation bluegills was not affected by the herbicide. Bluegills were slower growing in the treatment than the control pond, when similar densities were present in each pond. It is not known whether this was due to some unknown effect of the dipotassium endothall or to other factors.