简青霉(Penicillium simplicissimum)对木质纤维素的降解及相关酶活性特征

简青霉[Penicillium simplicissimum(Oudem.)Thom BGA]能分泌木质纤维素降解酶,其中半纤维素酶、纤维素酶、木质素过氧化物酶、锰过氧化酶和漆酶的最大酶活分别为146.82 Iu·g-1、2.78 U·g-1、47.97 U·g-1、34.56 U·g-1和17.94 U·g-1.实验结果和SPSS统计分析表明,简青霉产木质纤维素酶的能力与木质纤维素的结构有很大的关系,其对木质纤维素的降解可能是几种木质纤维素酶之间协同作用的结果.在30 d的固态发酵中,半纤维素含量与发酵天数呈显著负相关(r=-0.946,P<0.01),纤维素与木质素的降解趋势呈显著负相关(r=-0.818,P<0.05).木质素过氧化物酶和锰过氧化物酶在降解木质素的同时对半纤维素和纤维素进行协同降解,是非选择性的木质素降解酶.木质素过氧化物酶、锰过氧化物酶与纤维素酶之间呈显著相关(相关性依次为r=0.922,P<0.01;r=0.807,P<0.05).研究还发现生物吸附在简青霉对液态碱木质素的去除中起到了非常重要的作用.     

浓缩型溢油分散剂的研究

针对海洋石油污染的严峻形势和普通型消油剂的局限性,研制开发了对环境友好的浓缩型溢油分散剂。该溢油分散剂具有乳化性能好、鱼类急性毒性低的特点,且凝固点较低,适宜于低温(高于-20℃)环境条件下使用。惟有生物可降解性指标低于现行国家标准,本文分析了造成其生物降解性差的原因,并提出了新的测定方法-CTAS法。     

Electrocatalytic biofilm reactor for effective and energy-efficient azo dye degradation: the synergistic effect of MnOx/Ti flow-through anode and biofilm on the cathode

● MnO _x /Ti flow-through anode was coupled with the biofilm-attached cathode in ECBR. ● ECBR was able to enhance the azo dye removal and reduce the energy consumption. ● Mn^IV=O generated on the electrified MnO _x /Ti anode catalyzed the azo dye oxidation. ● Aerobic heterotrophic bacteria on the cathode degraded azo dye intermediate products. ● Biodegradation of intermediate products was stimulated under the electric field. Dyeing wastewater treatment remains a challenge. Although effective, the in-series process using electrochemical oxidation as the pre- or post-treatment of biodegradation is long. This study proposes a compact dual-chamber electrocatalytic biofilm reactor (ECBR) to complete azo dye decolorization and mineralization in a single unit via anodic oxidation on a MnO_x/Ti flow-through anode followed by cathodic biodegradation on carbon felts. Compared with the electrocatalytic reactor with a stainless-steel cathode (ECR-SS) and the biofilm reactor (BR), the ECBR increased the chemical oxygen demand (COD) removal efficiency by 24 % and 31 % (600 mg/L Acid Orange 7 as the feed, current of 6 mA), respectively. The COD removal efficiency of the ECBR was even higher than the sum of those of ECR-SS and BR. The ECBR also reduced the energy consumption (3.07 kWh/kg COD) by approximately half compared with ECR-SS. The advantages of the ECBR in azo dye removal were attributed to the synergistic effect of the MnO_x/Ti flow-through anode and cathodic biofilms. Catalyzed by Mn^IV=O generated on the MnO_x/Ti anode under a low applied current, azo dyes were oxidized and decolored. The intermediate products with improved biodegradability were further mineralized by the cathodic aerobic heterotrophic bacteria (non-electrochemically active) under the stimulation of the applied current. Taking advantage of the mutual interactions among the electricity, anode, and bacteria, this study provides a novel and compact process for the effective and energy-efficient treatment of azo dye wastewater.     

斜生栅藻与单甲脒的相互作用

为研究斜生栅藻与单甲脒的相互作用,采用评价化学品对藻类毒性的标准实验方法出了单甲凶制斜生栅藻生长的９６ｈ－ＥＣ５０为６．５ｍｇ／Ｌ。实验结果表明,在单甲脒浓度分别为２,４和８ｍｇ／Ｌ下,斜生栅藻都不具备降解单甲 能力。     

Anaerobic degradation of xenobiotic organic contaminants (XOCs): The role of electron flow and potential enhancing strategies

In groundwater, deep soil layer, sediment, the widespread of xenobiotic organic contaminants (XOCs) have been leading to the concern of human health and eco-environment safety, which calls for a better understanding on the fate and remediation of XOCs in anoxic matrices. In the absence of oxygen, bacteria utilize various oxidized substances, e.g. nitrate, sulphate, metallic (hydr)oxides, humic substance, as terminal electron acceptors (TEAs) to fuel anaerobic XOCs degradation. Although there have been increasing anaerobic biodegradation studies focusing on species identification, degrading pathways, community dynamics, systematic reviews on the underlying mechanism of anaerobic contaminants removal from the perspective of electron flow are limited. In this review, we provide the insight on anaerobic biodegradation from electrons aspect — electron production, transport, and consumption. The mechanism of the coupling between TEAs reduction and pollutants degradation is deconstructed in the level of community, pure culture, and cellular biochemistry. Hereby, relevant strategies to promote anaerobic biodegradation are proposed for guiding to an efficient XOCs bioremediation.     

壬基酚在海河沉积物中的耗氧和厌氧降解

研究了壬基酚（NP）在海河沉积物中的降解.结果表明,NP在沉积物的耗氧降解分为快速和慢速降解阶段,半衰期分别为3.20-9.87d和21.66-385.11d.NP在沉积物中的厌氧降解缓慢,降解半衰期为160.65-203.88d.加入电子受体NaNO3和Na2SO4促进了NP的厌氧降解,并且NaNO3促进作用较大.当沉积物中NP降低到一定浓度以后就很难继续降解,说明沉积物中一些活性吸附点位对NP的锁定作用降低了其生物有效性.盐度不利于NP的耗氧和厌氧降解.     

优势菌降解橡胶工业有机废水的实验研究

用含M盐(2-硫醇基苯并噻唑)的橡胶工业有机废水驯化活性污泥,分离出8株高效优势菌,并初步鉴定到属.对8株菌种降解橡胶工业有机废水的效果进行了对比研究.结果表明:处理6 d后,各单菌株对橡胶工业有机废水的去除率均在55%以上,其中Y8的去除率达到82%.对复合菌降解橡胶工业有机废水的研究结果表明:温度为35 ℃,pH为8是复合菌降解的最佳条件.对废水稀释会导致碳源稀薄,降低降解率.多因素正交实验表明:降解该类废水的最佳条件是ρ(葡萄糖),ρ(尿素),菌量和转速分别为2 g/L,1.0 g/L,20%和80 r/min.      

厌氧混合培养条件下六氯苯生物降解的外加碳源必要性

采用标准血清瓶实验探讨了厌氧污泥对六氯苯(HCB)的降解活性以及各种环境因素的影响.结果表明,经过14d的HCB驯化,厌氧污泥具备了较好的降解HCB能力;反应温度对HCB的降解速率有很大影响,适宜温度为35℃左右;葡萄糖、甲酸、乙酸、丙酸和丁酸等有机碳源的存在明显促进了HCB的厌氧降解,其中甲酸和乙酸的加入极其重要;根据实验结果推测出,产甲烷过程对HCB的生物降解发挥了重要作用.     

含氟有机化合物的生态迁移及转化

含氟有机化合物的众多特性使得其在各方面得到越来越广泛的应用,同时也成为了一种较普遍的环境污染物。本文列举了含氟有机化合物的应用类型及相应的应用特点;指明其污染途径和毒性特征;从含氟有机物的分子结构特征、降解茵的类型、外部因素三方面阐明了其生物降解特性;总结了酶作用于碳氟键使得含氟有机物发生降解的四种作用;并介绍了含氟有机污染物的生物处理和生态修复的一般方法。     

Biodegradation of 2,6-ditert-butylphenol by immobilized microorganism strains

2,6-Ditert-butylphenol （2,6-DTBP） is a major organic contaminant presenting in acrylic fiber manufacturing wastewaters. This compound is of high bio-resistance due to its complex structure which consists of one phenol group and two highly branched tert-butyl groups. This research attempted to improve the biodegradation efficiency of 2,6-DTBP through various strain immobilization methods. The stratified immobilization can settle oxygen transmission in the single microorganism immobilization, and can realize two-process reaction in the single device by choosing two symbiotic microorganisms. Two effective strains, named F-1-4 and F-3-4, which were screened out in our previous work, were used to degrade 2,6-DTBP after being immobilized in calcium alginate gel. Results indicate that the substrate removal efficiency of various immobilization methods follows the order： stratified 〉 single F-3-4 〉 mixed ≈single F-1-4. The immobilized biodegradation capacity was higher than the free one. After an incubation time of 12 d, 91% of 2,6-DTBP could be degraded by the stratified immobilization method, compared to 79% achieved by the mixed immobilization method with an initial 2,6-DTBP concentration of 100 mg/L. The stratified immobilization satisfies the oxygen demand nature of the aerobic F-3-4 and the facultative F-1-4, thus yielding the highest degradation efficiency. Both the outer layer strain F-3-4 and the inner layer strain F-1-4 can grow actively on the substrate of 2,6-DTBP, as illustrated by SEM images. This study shows that the highly bio-refractory compound, 2,6-DTBP, can be effectively degraded using appropriately inunobilized microorganism strains.