微生物对地下水及土壤中阿特拉津降解的研究

从吉林市农药厂采集的污泥样品中筛选出降解阿特拉津（AT）能力较高的菌－JLNY01，JLNY02，通过条件实验表明，JLNY01在pH=6左右，此菌在10℃条件下，一定时间内驯化降解率可达83．6％，30℃时，6天内可达到对AT的完全降解，证明温度越高降解效果越好，JLNY02可直接在低温条件下进行降解，其降解率可达81．8％，而在高温条件下降解率仅达31．4％，证明此菌是一种嗜冷菌。     

农药杀螟硫磷酶促降解的研究

从长期受农药杀螟硫磷污染的土壤中分离到一株高效降解菌株,研究了其最适产酶条件:培养温度为30℃,培养液起始pH为7.0,培养时间为30 h.从该降解菌中提取的粗酶液在pH 7.5和30℃时显示最大的降解活性,其米氏常数Km为2.92×10-4mol/L,最大降解速率为2 422.79 nmolm in-1mg-1.图7参15     

接种降解菌对土壤中邻苯二甲酸二异辛酯降解的影响

邻苯二甲酸二异辛酯〔Di-(2-Ethylhexyl)phthalate,DEHP〕是农田土壤中常被检出的有毒有机污染物,在土壤中有较长的持留性,微生物降解是其从土壤中消失的主要途径.本文采用温室盆栽试验研究了接种两株从污水处理厂活性污泥中分离得到的高效DEHP降解菌及其混合菌悬液降解土壤中DEHP污染的效果,以及土壤中添加葡萄糖和种植作物对其降解效率的影响.结果表明,在土壤初始DEHP浓度为100mg kg-1的条件下,接种两种降解菌及其混合菌悬液都可显著提高土壤中DEHP消失的速率,其残留半衰期比不接种对照缩短了32~48d,但在相同条件下接种不同降解菌的处理之间没有显著差异.土壤中添加0.6%的葡萄糖虽然可以强烈地促进土壤微生物的整体活性,但并没有提高修复效率,反而在短期内延缓了降解菌对DEHP的降解,延长了DEHP在土壤中持留的半衰期;植物生长可显著提高降解菌的降解效率,降低土壤中DEHP的残留浓度.研究结果同时也表明,只添加葡萄糖或只种植植物对土壤中DEHP的降解并没有显著的影响.图3表4参14     

三相内循环流化床光催化反应器及其性能

依据流态化原理,设计出一种三相内循环流化床光催化反应器,对反应器的水力特性做了推算,确定了反应器的操作影响因素.对罗丹明B的降解实验结果显示出优越的性能,依据催化剂投加量及初始光强的不同,反应半衰期在4-10.5min之间.     

臭氧降解乐果机理探讨

研究了臭氧对乐果的降解效果及其影响因素。试验结果表明,当初始臭氧浓度为10mg·L-1时,5min内可使乐果降解80%左右,延长反应时间,乐果降解率无明显增加。同时,通过在乐果和臭氧的反应液中再分别添加重碳酸盐与叔丁醇,探讨臭氧降解乐果的反应机理,结果表明臭氧降解乐果是分子反应。GC-MS检测经臭氧处理的水样发现有氧化乐果存在,表明若臭氧处理不完全,水样中可产生毒副产物。     

水溶液中硝基苯的超声微电场降解

研究了超声微电场中硝基苯的降解过程，并探讨了降解机理及反应历程。结果表明，硝基苯的降解符合拟一级反应，超声与微电场的耦合协同作用大大提高了硝基苯的降解效率，在槽电压10V条件下，协同作用的降解速率比简单加和作用的速率高一倍以上，经过30min协同处理后可以获得93．8％的去除率，而溶液中饱和气体种类等对降民产生一定的影响，经紫外和SMPE－GC－MS分析，推断硝基苯在电超声场作用下存在氧化还原反应与热解、自由基作用等协同作用。主要中间降解产物为苯胺、偶氮苯、1－氧，2－苯基－二氮烯、1，2－苯二甲酸二丁酯、1，2－苯二甲酸丁酯异丁酯等，最终产物为CO2、水及无机盐类。     

黄孢原毛平革菌对固体介质中染料的降解反应

用黄孢原毛平革菌(Phanerochaetechrysosporium)3品系在固体介质中建立染料的降解反应体系,分光光度法测定染料的脱色降解率。黄孢原毛平革菌在琼脂、沙子及土壤等固体介质中均能有效地降解偶氮染料、蒽醌染料及聚合染料;植物材料玉米芯和木屑可作为共代谢碳源被该菌利用;BKM F 1767菌种降解能力最强,对活性艳蓝KN R的进攻性优于对PolyR 478和比布列希猩红。     

环戊酮和环己酮的微生物降解途径、相关酶和基因研究进展

简略介绍了环戊酮和环己酮的应用及危害,综述了目前国内外在环戊酮和环己酮微生物降解方面的研究进展.具体介绍了环戊酮和环己酮降解代谢的过程及其相关的酶类和编码这些酶的基因,重点阐述了环戊酮1,2-单加氧酶和环己酮1,2-单加氧酶及其编码基因.图4参19     

Degradation of Starch–Calcium Carbonate Disposable Packaging in a Solid Waste Composting Facility

The compostability of starch–CaCO₃ disposable packaging was examined in a source-separated municipal solid waste (MSW) composting facility located in East Hampton, NY. Source-separated MSW:starch–CaCO₃ container mixtures of 0 (control), 5, and 20% (by volume) were prepared as feedstock for composting. Compost samples were collected weekly or biweekly during the composting process and examined for fragments of the starch–CaCO₃ containers. Changes in compost quality due to the presence of starch–CaCO₃ containers were assessed by measuring the nutrient and metal content of the three resultant MSW:starch–CaCO₃ composts. Finally, plant growth studies were conducted to examine the composts for possible plant growth inhibition due to the deterioration of the starch–CaCO₃ containers. Results showed that portions of the starch–CaCO₃ containers were not identified in any of the 5 and 20% sieved and characterized compost fractions > 1.3 cm following 1–3 weeks of composting. Mechanical agitation of the waste along with optimum composting conditions were sufficient to initiate the rapid degradation of the starch–CaCO₃ composites. Degradation of starch–CaCO₃ containers did not affect compost nutrient and trace element content. Grass biomass measurements were performed once weekly over 28 days for grass grown in control (0%), 5%, and 20% starch–CaCO₃-containing compost:soil mixtures. Significant differences in grass biomass for these compost:soil mixtures were measured only for the 0 and 20% starch–CaCO₃-containing compost:soil mixtures at 28 days (9.07 vs 11.05 g, respectively; P = 0.046).     

Distribution of Poly(β-propiolactone) Aerobic Degrading Microorganisms in Different Environments

The distribution of degading microorganisms of high molecular weight poly(-propiolactone) (PPL), whose individual structural units are similar to those of poly(-hydroxybutyrate) (PHB) and poly(€-caprolactone) (PCL), was examined. Despite the fact that PPL is a chemosynthetic polymer, many kinds of PPL-degrading microorganisms were found to be distributed as resident populations widely in natural environments. A total of 77 strains of PPL-degrading microorganisms was isolated. From standard physiological and biochemical tests, at least 41 strains were referred to as Bacillus species. Microbial degradation of fibrous PPL proceeded rapidly in some enrichment cultures but was not as complete as that of PHB. Most of the isolated PPL-degrading microorganisms were determined to be PCL degraders and/or PHB degraders. Therefore, it can be assumed that mostly PPL is recognized by the microorganisms as PHB or another natural substrate of the same type as which PCL is regarded. Microbial degradation of PPL was confirmed by some Bacillus strains from type culture collections. The similarity of microbial degradation between PPL and PCL was found to be very close.