真菌-细菌修复石油污染土壤的协同作用机制研究

提出并研究了真菌和细菌协同强化原位修复石油污染土壤.从中原油田石油污染土壤中筛选出刺孢小克银汉霉菌(Cunninghamella echinulata)和阴沟肠杆菌(Enterobacter cloacae),在泥浆体系中考察了Cun.echinulata和E.cloacae的生长及其对石油烃的降解过程.结果表明,混合培养体系中细菌和真菌的数量最高分别为其纯培养体系的3倍和20倍,细胞衰亡则被明显推迟;混合培养体系中石油烃的去除率高于真菌和细菌纯培养体系石油烃去除率的总和;采用多次接种新鲜菌种的培养方式能够强化混合培养体系对石油烃的降解.在石油烃污染土壤中接入由Cun.echinulata和E.Cloacae所组成的真菌-细菌微生物制剂实施原位修复,结果表明,Cun.echinulata和E.Cloacae的生长及其对石油烃的降解不受土著微生物的抑制,最适工艺条件为:水和木屑含量分别为25%和6%(质量分数),Cun.echinulata和E.cloacae接种量分别为2.5×104和2.5 × 107CFU/g.接种上述真菌-细菌40 d后石油烃去除率可达约65%,而土著微生物对石油烃去除率为16.0%.     

葫芦岛锌业股份有限公司汞污染现状调查与防治对策研究

葫芦岛市是辽宁省汞污染最严重的城市,该市汞排放量约占全省汞排放量的90％以上。从多年环境管理掌握情况看,葫芦岛市现仅有葫芦岛锌业股份有限公司（简称葫芦岛锌厂）一家企业有汞污染物排出,为加强葫芦岛市汞污染治理和管理提供科学依据,本论文主要针对葫芦岛锌厂周圉环境汞污染现状调查与防治对策进行研究。     

微宇宙系统中氯苯的生物强化处理

将分离出的一株降解氯苯的高效土著菌Acinetobacter calcoaceticus和自然材料组成微宇宙系统,通过改变系统组成、重金属和营养物添加水平、悬浮物浓度以及温度,研究了系统中氯苯的去除机制.结果表明,微宇宙系统中氯苯的去除主要是加入菌株的降解作用;加入降解菌后,8d内系统中氯苯的去除率可达到98.3%.底泥和光照对微宇宙系统中氯苯的去除具有明显的促进作用(p0.05).悬浮物在实验前期对氯苯的去除产生明显的促进作用.微宇宙系统中氯苯的去除率随着温度的升高而增加,30.0℃条件下培养7d后,氯苯的去除率可达95.4%;10.0℃和15.0℃下培养14d后,氯苯的去除率分别为43.4%和68.5%.营养盐加入比例达1.0%时,可明显促进氯苯的去除.Cd2+和Hg2+浓度达到10.0mg·L-1时,可对系统中氯苯的去除率产生显著(p0.05、p0.01)降低作用.研究结果可为突发性事故造成的氯苯污染水体的微生物修复提供基本的理论和实践依据.     

Control of petroleum-hydrocarbon contaminated groundwater by intrinsic and enhanced bioremediation

In the first phase of this study, the e ectiveness of intrinsic bioremediation on the containment of petroleum hydrocarbons was evaluated at a gasoline spill site. Evidences of the occurrence of intrinsic bioremediation within the BTEX (benzene, toluene, ethylbenzene, and xylenes) plume included (1) decreased BTEX concentrations; (2) depletion of dissolved oxygen (DO), nitrate, and sulfate; (3) production of dissolved ferrous iron, methane, and CO2; (4) deceased pH and redox potential; and (5) increased methanogens, total heterotrophs, and total anaerobes, especially within the highly contaminated areas. In the second phase of this study, enhanced aerobic bioremediation process was applied at site to enhance the BTEX decay rates. Air was injected into the subsurface near the mid-plume area to biostimulate the naturally occurring microorganisms for BTEX biodegradation. Field results showed that enhanced bioremediation process caused the change of BTEX removal mechanisms from anaerobic biodegradation inside the plume to aerobic biodegradation. This variation could be confirmed by the following field observations inside the plume due to the enhanced aerobic bioremediation process: (1) increased in DO, CO2, redox potential, nitrate, and sulfate, (2) decreased in dissolved ferrous iron, sulfide, and methane, (3) increased total heterotrophs and decreased total anaerobes. Field results also showed that the percentage of total BTEX removal increased from 92% to 99%, and the calculated total BTEX first-order natural attenuation rates increased from 0.0092% to 0.0188% per day, respectively, after the application of enhanced bioremediation system from the spill area to the downgradient area (located approximately 300 m from the source area).     

自然循环水处理系统的应用试验

基于对自然循环水处理系统的工艺流程的分析,设置脱氮池、碳氧化池和除磷池,以多种天然材料作为微生物载体,建立小型自然水处理系统,对生活污水进行小型应用试验。结果表明：对于普通的生活污水,该处理系统可以使出水CODcr在30～50mg/L之间,氨氮〈5mg/L,总磷〈1mg/L,接近于中水回用要求,且处理过程剩余污泥少。     

P450酶系对污染物的生物指示和催化降解机制

细胞色素P450酶系是广泛存在于不同生物体内的含有多种超家族CYP450血红素蛋白或相同结构域的一系列酶,是多组分电子传递链的终端氧化还原酶。最新研究发现,利用P450在生物体内的含量/活性与污染物浓度的定量响应关系可实现环境污染的早期预警和诊断,对环境污染的监测和预报具有重要意义。更重要的是,P450酶系被认为是生物对内源或外生污染物代谢途径的启动催化因子。P450的脱卤化、羧基化、脱烷基化、环氧化等催化作用在诱导污染物的分解代谢过程中起核心作用。本文综述了P450酶系的结构、催化过程和诱导抑制机理,分析了其在环境污染物的生物指示和催化降解中的应用进展,以便为利用P450进行环境预警和生物修复提供系统的理论和技术支持。     

β-环糊精强化微生物修复石油烃污染土壤的试验研究

石油烃污染物的生物可利用性是土壤微生物修复的限制因素,为了提高污染物的生物可利用性和降解效率,引入环境友好的β-环糊精作为污染物增溶剂,并与表面活性剂十二烷基硫酸钠(SDS)作对比。结果表明,当β-环糊精的投加浓度为其在水中饱和溶解度的90%、SDS的投加浓度为其临界胶束浓度时,β-环糊精和SDS对土壤中石油烃污染物的增溶效果达到最大,分别为84.42%和89.63%。虽然两者都具有相近的增溶效果,但SDS具有一定的生物毒性,抑制了微生物的生长及其对石油烃污染物的降解,而β-环糊精可以促进微生物生长并有效提高微生物对污染物的去除效率。投加β-环糊精的微生物修复组在15 d内的降解率达到19.5%,比单独微生物修复组的降解率提高了70%以上。     

石油烃-镉污染土壤的生物修复研究

利用微生物菌剂和花卉植物在花盆中对不同浓度的石油烃和重金属镉的复合污染土壤进行了生物修复试验研究。结果表明:种植植物能提高石油烃的降解率,其中种植牵牛花优于紫茉莉;2个月后种植牵牛花的土壤石油烃降解率比对照提高13.0%以上,PAHs降解率提高22.0%以上;紫茉莉和牵牛花均能适应100mg/kg的镉浓度,牵牛花在土壤中镉浓度为100mg/kg时的富集效果是紫茉莉的6倍。     

地下水硝酸盐反硝化修复过程中生物膜抑制缓堵模拟实验研究

为缓解地下水污染原位生物修复过程中生物膜形成造成的多孔介质渗透性损失,采用纳米乳化油为碳源,市售反硝化细菌为菌种,开展静态批实验,模拟地下水硝酸盐氮反硝化修复过程;选取蛋白酶、多糖酶以及群体感应抑制剂香草醛为生物膜抑制剂,分析不同反应体系硝酸盐氮的降解情况,探究3种添加物的不同组合方式对于反硝化细菌生物膜的抑制作用.结果显示,多糖酶、蛋白酶以及香草醛的投加能够有效促进硝酸盐氮的降解和亚硝酸盐氮的还原.4个实验组别的NO₃-N降解速率为0.28～0.30 mg·L^-1·h^-1,约为空白组的2.55～2.73倍,且NO₂-N无明显积累.群体感应抑制剂香草醛与蛋白酶的结合对以假单细胞菌属为主的反硝化细菌生物膜的抑制效果最好.定量评估结果表明,生物膜去除效果依次为香草醛和蛋白酶的混合物（81.3%）>蛋白酶和多糖酶的混合物（68.6%）>蛋白酶（54.1%）>多糖酶（49.1%）,单位质量多糖酶、蛋白酶和香草醛对于胞外聚合物的去除量分别为30.07、65.34 mg·mL^-1     

The Reduction of Stranded Oil by In Situ Shoreline Treatment Options

The Svalbard Shoreline Field Trials quantified the effectiveness of sediment relocation, mixing, bioremediation, bioremediation combined with mixing, and natural attenuation as options for the in situ treatment of oiled mixed-sediment (sand and pebble) shorelines. These treatments were applied to oiled plots located in the upper beach at three experimental sites, each with different sediment character and wave-energy exposure. Systematic monitoring was carried out over a 400-day period to quantify oil removal and to document changes in the physical character of the beach, oil penetration, oil loading, movements of oil to the subtidal environment, biodegradation, toxicity, and to validate oil-mineral aggregate formation.The results of the monitoring confirmed that sediment relocation significantly accelerated the rate of oil removal and reduced oil persistence where oil was stranded on the beach face above the level of normal wave activity. Where the stranded oil was in the zone of wave action, sediment relocation accelerated the short-term (weeks) rate of oil loss from the intertidal sediments.Oil removal rates on a beach treated by mechanical mixing or tilling were not significantly higher than those associated with natural recovery. However there is evidence that mixing/tilling may have enhanced microbial activity for a limited period by increasing the permeability of the sediment.Changes in the chemical composition of the oil demonstrated that biodegradation was significant in this arctic environment and a bioremediation treatment protocol based on nutrient enrichment effectively doubled the rate of biodegradation. However, on an operational scale, the success of this treatment strategy was limited as physical processes were more important in causing oil loss from the beaches than biodegradation, even where this oil loss was stimulated by the bioremediation protocols.