水产养殖环境微生物研究进展

近年来,水产养殖产业的迅猛发展在带来巨大经济效益的同时,也使周边水质持续恶化。在水产养殖中,微生物在生态平衡和环境保护方面的作用日益明显。着重介绍了养殖水域菌落结构的持续性变化、微生物在水产养殖中的作用以及水产养殖水域微生物群系组成变化的原因,并阐述了改善养殖水环境的生物修复技术,旨在为水产养殖环境微生物的相关研究及其管理提供参考依据。     

多氯联苯的环境毒理研究动态

本文综述了当前国内外对多氯联苯这种持留性有机污染物环境生态毒理的研究现状,详细论述了多氯联苯的来源、分布、迁移变化等环境行为,特别强调了多氯联苯这种持留性有机污染物在生态系统中因食物网营养关系产生的积累、富集、放大进而影响人类健康的可能性,并对多氯联苯对生物影响的早期预警研究作了展望。     

海水养殖环境生物修复研究进展

着重分析了微生物,大型藻类及其他生物在海水养殖环境中的生物修复作用,原理,国内外最新研究进展,存在问题以及发展前景。     

水产养殖对水域环境的影响研究

近年由于水产养殖行业发展迅猛,规模的逐渐扩大,方式的各种各样,已遍布在全国各地,由此也带来了因为水产养殖而不容小觑的环境问题。本文从多方面综合阐述了现阶段水产养殖的状况、养殖造成的污染对水域环境的影响及一系列的解决措施,为提高对水体重复利用率,了解生态环境自我修复的周期,开发环保养殖新模式,创造和谐的生态环境提供依据。     

水产养殖中益生菌研究进展

益生菌在水产养殖中能够净化水质、预防疾病、促进生长且安全、环保、无抗性,是抗生素的理想替代品,具有重要的研究价值和广阔的应用前景。本文主要从益生菌制剂的定义概述、作用机理及特性进行阐述,分析益生菌制剂存在的问题,探讨水产养殖用益生菌制剂的研究方向。     

厦门海域贝类养殖环境中有机氯农药的积累和降解

利用气相色谱法(GC-ECD)对厦门海域贝类养殖环境(海水、底质和养殖贝类)中有机氯农药六六六(HCH)和滴滴涕(DDT)的含量进行了调查分析,初步探讨了贝类养殖环境中HCH和DDT的积累和降解规律.结果表明:厦门海域不同种贝类养殖环境中HCH和DDT的积累和降解存在明显差异,主要与各种贝类的栖息环境和生理生活习性有关.贝类养殖环境中处于积累状态(Rx＞1)的主要为p-HCH、δ-HCH和γ-HCH;处于降解状态(Rx＜1)的主要为α-HCH.α-HCH/γ-HCH的比值≤1.0,贝类养殖环境中的HCH来源于工业品HCH和林丹,大部分HCH为长时间残留,但尚有少量林丹输入.贝类养殖区海水中DDT主要为好氧降解,底质中主要为厌氧降解.海水中的降解产物主要为DDE,(DDD+ DDE )/DDTs(p,p-DDE+p,p-DDD+o,p-DDT+p,p-DDT)的比值＜0.5;底质和养殖贝类体中的降解产物主要为DDD,(DDD+DDE)/DDTs的比值＞0.5,贝类养殖区底质和养殖贝类体中的DDT大部分已降解为DDD和DDE,海水中尚有少量新的DDT输入.贝类养殖环境中HCH异构体降解率的高低顺序存在一定差异,其在贝类养殖生态系中的迁移、转化过程发生了构象变化.     

在水产养殖中作为生物防治因素的益生菌制剂（节译）

水产养殖 (鱼、甲壳动物、软体动物、藻类植物 )是发展最为迅速的行业之一 ,其产量在 1984～ 1995年间 ,每年以近10 %的速度增长 ,与之相比 ,畜牧业和捕捞业的产量每年仅以 3%和 1.6 %的速度增长 (Rana,K.J.1997)。疾病的爆发抑制了水产养殖产量的增长和水产贸易的发展 ,甚至影响了一些国家水产行业的发展。如在虾类养殖业中 ,疾病已成为产量增加的限制因素。到目前为止 ,应用常规办法 ,如使用消毒剂和抗菌剂对预防和治疗水产疾病的效果并不理想 ,并且在水产养殖业中也存在着类似在人类用药和农业中抗菌剂过量使用问题 ,这已经引起人们的…     

现代微生物识别技术在水产养殖环境研究中的应用

养殖环境的恶化已成为制约水产业健康发展的瓶颈。鉴于微生物在养殖水体中的重要作用,本文从技术角度对近年来发展起来的现代微生物分子识别技术进行了概括介绍,并综述了以核酸为靶分子和以微生物表面抗原为靶分子的两类微生物识别技术在水产养殖中的应用进展,为水产养殖环境的改善及其病害防治提供参考。     

微生物降解多氯联苯的研究进展

多氯联苯是一种持续性有机污染物,在自然环境中很难降解。在目前研究的降解方法中,微生物降解最具潜力。本文对多氯联苯微生物降解的研究进展进行了综述,包括厌氧还原脱氯,好氧氧化以及生物表面活性剂的作用,介绍了几种降解方法耦合应用的现状和前景,指出了应用中存在的问题和今后的发展方向。     

光合细菌对水产养殖水质和水生生物的影响

研究光合细菌对水产养殖水体的水质,如化学需氧量(COD)、氨氮(NH₄⁺-N)、溶解氧(DO)、pH等指标,及对水生生物,如藻类植物和细菌的种群组成的影响。结果表明:鲤鱼养殖水中投放一定量的光合细菌,能明显去除水中有机物和NH₄⁺-N,增加DO的含量,稳定pH值。光合细菌对水中藻类也有明显影响,0.50%、1%剂量组中藻类明显增加,其中硅藻在所有藻类中所占比例可达26%以上,绿藻所占比例达60%左右,而以蓝藻为主的杂藻则下降到10%左右。光合细菌对有害菌有一定的抑制作用,使得弧菌属、气单胞菌属等致病菌所占比例显著降低。     

Potential importance of protozoan grazing on the accumulation of polychlorinated biphenyls (PCBs) in the pelagic food web

Experiments were conducted to study the distribution of three selectedpolychlorinated biphenyl (PCB) congeners within the microbial food web attwo different nutrient levels; control and nutrient enriched. The objectivewas to quantify the uptake of PCBs through grazing by protozoa. The¹⁴C-PCBs tested were 4-chlorobiphenyl (IUPAC # 3),2,2,5,5-tetrachlorobiphenyl (IUPAC # 52), and2,2,4,4,5,5-hexachlorobiphenyl (IUPAC # 153). EachPCB was incubated in triplicate seawater samples at 20 idref;Cover one week. Daily, samples were separated into four fractions; <0.2µm (dissolved), 0.2-2 µm (bacteria), 2-10 µm(flagellate), and > 10 µm (microplankton; phytoplankton andprotozoa) by selective filtration. Of the PCB fraction that initiallyadsorbed to particles, 60–100% was associated to the bacterialfraction and 0–5% to the microplankton fraction. The totaluptake was highest in the nutrient enriched samples, but when normalized tothe carbon biomass the concentration was lower or equal to the control inall particle fractions. The recovery of the PCBs in the particulatefractions depended on the degree of chlorination, as the highest values wereobserved for the 2,2,4,4,5,5-hexachlorobiphenyl and thelowest for the 4-chlorobiphenyl. The concentrations in the bacterial andflagellate fractions decreased over the first 48–96 hours whilst theconcentration increased in the highest trophic level (>10 µmfraction). Approximately 75% of the increase in concentration of the2,2,4,4,5,5-hexachlorobiphenyl in the > 10 µmfraction was estimated to be the result of bacterivory. Our results indicatethe microbial food web can contribute to a rapid uptake of higherchlorinated PCBs, particularly in oligotrophic ecosystems where thebacterial biomass dominates.     

On the inhibition of microsomal drug metabolism by polychlorinated biphenyls (PCB) and related phenolic compounds.

The in vitro metabolism of p-nitroanisole, aminopyrine, and aniline by rat liver microsomal monoxygenases were studied in the presence of different polychlorinated biphenyl (PCB) mixtures and some related hydroxybiphenyls. The tested PCB mixtures contained preferably dichloro- (di-CB), tetrachloro- (tetra-CB), or hexachlorobiphenyls (hexa-CB). All PCB were competitive inhibitors of only aminopyrine demethylation by normal microsomes (Ki 22-39 micron). In microsomes of PCB-pretreated rats the aminopyrine demethylation was inhibited noncompetitively by di-CB and hexa-CB whereas tetra-CB remained a competitive inhibitor (Ki 12 micron). Moreover, after PCB pretreatment all PCB were competitive inhibitors of p-nitroanisole demethylation. 2-OH-biphenyl and 4-OH-biphenyl caused competitive inhibition of aminopyrine demethylation and aniline hydroxylation but failed to inhibit p-nitroanisole metabolism by normal microsomes. Chlorinated 4-hydroxybiphenyls inhibited competitively the metabolism of both type I and type II substrates. However, after PCB pretreatment all phenolic compounds caused uncompetitive inhibition of aniline hydroxylation.     

The reductive dechlorination of 2,3,4,5-tetrachlorobiphenyl in three different sediment cultures: evidence for the involvement of phylogenetically similar Dehalococcoides-like bacterial populations

Anaerobic cultures capable of reductively dechlorinating 2,3,4,5-tetrachlorobiphenyl (CB) were enriched from three different sediments, one estuarine, one marine and one riverine. Two different electron donors were used in enrichments with the estuarine sediment (elemental iron or a mixture of fatty acids). The removal of doubly flanked meta and para chlorines to form 2,3,5-CB and 2,4,5-CB was observed in all cultures. Bacterial community analysis of PCR-amplified 16S rRNA gene fragments revealed different communities in these cultures, with the exception of one common population that showed a high phylogentic relatedness to Dehalococcoides species. No Dehalococcoides-like populations were ever detected in control cultures to which no PCBs were added. In addition, the dynamics of this Dehalococcoides-like population were strongly correlated with dechlorination. Subcultures of the estuarine sediment culture demonstrated that the Dehalococcoides-like population disappeared when dechlorination was inhibited with 2-bromoethanesulfonate or when 2,3,4,5-CB had been consumed. These results provide evidence that Dehalococcoides-like populations were involved in the removal of doubly flanked chlorines from 2,3,4,5-CB. Furthermore, the successful enrichment of these populations from geographically distant and geochemically distinct environments indicates the widespread presence of these PCB-dechlorinating, Dehalococcoides-like organisms.     

零价金属降解多氯联苯(PCBs)

多氯联苯(polychlorinated biphenyls,简称PCBs)是一类对环境有不利影响的有毒有机物,它在环境中广泛而大量分布。许多科学家都在致力于有效处理PCBs污染介质(包括水、油、沉积物和土壤)的修复技术的研究。本文综述了国内外在零价金属还原脱氯降解PCBs领域的研究状况。在高温等特殊条件下或有钯、铂、镍和铜等催化剂存在的条件下,零价金属能有效促进PCBs还原脱氯。讨论了零价铁还原脱氯的3个可能的途径:金属直接反应,将零价铁表面的电子转移到有机氯化物使之脱氯;铁腐蚀的直接产物Fe2 具有还原能力,它可使得一部分氯代烃脱氯;铁反应产生的氢气可使有机氯化物还原。评述了零价金属还原脱氯PCBs具有有效、廉价和易得的特点。展望了零价金属还原脱氯降解PCBs研究领域的发展前景。     

一株PCBs降解菌株分离鉴定及其酶学性质

从废旧变压器周围采取的土样中分离出一株多氯联苯降解菌,实验证明该菌株能以联苯作为唯一的碳源生长,经分子生物学鉴定,确定为枯草杆菌,编号为WF1。分别研究温度、pH值、底物浓度等因素对2,3’,4’,5—四氯联苯降解率的影响,确定其最佳产酶条件为发酵温度35℃、pH值7.0、装液量100 mL以下、接种量4%、PCBs起始浓度0.2 mg/L,250 mL三角烧瓶中150 r/min下振荡培养3 d。酶促反应的最适反应温度为35℃,最适pH值7.5。     

An Integrated Surfactant Solubilization and PCB Bioremediation Process for Soils

Two decades after the manufacture and use of polychlorinated biphenyls (PCBs) were banned, PCB contamination remains widespread in the environment. Technologies available for PCB remediation are limited and often impractical for soils with dispersed PCB contamination. In this study, two remediation processes have been integrated for use on PCB-contaminated soils. This remediation strategy links in situ surfactant washing of PCBs from soil with aerobic biodegradation of the resulting surfactant-PCB solution by two field application vectors (F A Vs), Pseudomonas putida IFL5::TnPCB and Ralstonia eutropha B30F4::TnPCB, which utilize surfac-tants as growth substrates and cometabolize PCBs. A bench-scale demonstration of this process was performed using PCB-contaminated soils from an electric power substation site. In a 2-day recycling wash using a 1% (wt/vol) surfactant solution, greater than 70% of the PCBs were removed from the soil. In the biodegradation phase, greater than 90% of the surfactant and 35% of the PCBs were biodegraded in 12 days. The residual PCBs were partitioned onto a solid carrier resulting in greater than 90% removal of PCBs from the bioreactor effluent and a 50-fold reduction in the amount of PCB-contaminated material.     

Polychlorinated biphenyls in alfalfa: Accumulation,sorption and speciation in different plant parts

The accumulation, chemical speciation and distribution of polychlorinated biphenyls (PCBs) were investigated in various parts of alfalfa. Moreover, the adsorption characteristics for PCB 28 by alfalfa and the influencing factors of the adsorption characteristics were studied. There were different degrees of PCB accumulation in alfalfa roots, root nodules and shoots. The decreasing order of the accumulation of PCBs in plant tissues was root nodules > roots > shoots, and the decreasing order of the total PCB contents was roots > shoots > root nodules, indicating that the roots were the main sink for PCB accumulation. There were three modes of PCB speciation in alfalfa roots and root nodules, comprising strong sorption (78%) and weak sorption (19%) on tissue surfaces and absorption within tissues (2%). The adsorption isotherms of PCB 28 indicate that the adsorption capacities of root nodules and shoots were both significantly higher than that of the roots. Both lipids and carbohydrates, and especially lipids, affected the PCB adsorption capacities of the tissues. These results may help in the elucidation of the mechanisms of sorption and accumulation of PCBs in the plants and their main influencing factors and thus contribute to the development of phytoremediation technologies for PCB-contaminated soils.