微囊藻毒素-RR对反硝化细菌生长及生理特性的影响

用0.01、5.00 mg/L微囊藻毒素-RR(MC-RR)处理反硝化细菌,研究了MC-RR对反硝化细菌的生长、培养液中NO3--N和NO2--N含量以及细胞内硝酸还原酶活性的影响.结果表明,高浓度MC-RR能显著抑制反硝化细菌的生长,延缓其细胞增殖,抑制培养液中硝酸盐含量的降低和亚硝酸盐含量的升高以及细胞内硝酸还原酶的活性,因而可能抑制或减缓生态系统中氮循环的进程.这表明,微囊藻毒素在一定程度上可能调节水体细菌群落.     

微囊藻毒素的生物降解综述

从微囊藻毒素降解菌、降解途径和影响降解的因素三方面，对国内外微囊藻毒素生物降解的研究现状及发展趋势作一介绍。     

越南伯克霍尔德菌降解水中微囊藻毒素-LR

探讨利用越南伯克霍尔德菌(Burkholderia Vietnamiensis)降解微囊藻毒素-LR(MC-LR)的可能性和降解机理。结果表明,在1 mg/L的MC-LR溶液中投加体积分数为5%菌株,初始pH为5,温度为30℃的好氧条件下,经过48 h培养后对MC-LR的降解效率达到97.6%。首先,降解溶液的液相色谱分析结果发现,MC-LR在238 nm的特征峰消失。其次,动力学研究发现降解过程符合一级动力学反应方程。最后,SEM、FTIR表征技术对菌株降解前后样品进行分析发现微生物形态和降解产物。因此,Burkholderia Vietnamiensis可能将水中的MC-LR作为碳、氮源利用从而将其降解,Burkholderia Vietnamiensis作为生物降解MC-LR的一种途径是有效的。     

天然水华蓝藻中微囊藻毒素的提取和净化研究

利用天然水华蓝藻为原料，通过筛选、比较不同极性提取剂对微囊藻毒素的提取效果，80％甲醇溶液有较高的提取效率，而乙醇溶液可实现无毒提取，优化了提取方法。并通过调节溶液pH为藻胆蛋白等电点的方法去除共提取的大量藻胆蛋白，取得了很好的净化效果，为微囊藻毒素的分离和纯化研究提供了基础。     

微囊藻毒素-LR降解菌的筛选及降解特性研究

从上海市淀山湖表层水体中筛选分离出了1株降解微囊藻毒素-LR(MC-LR)的细菌并研究了其降解特性。根据细胞形态结构、生理生化特征及其16S rDNA基因序列分析,鉴定分离菌株DHU-28(GenBank序列登录号为HM047512)属嗜麦芽寡养单胞菌(Stenotrophomonas maltophilia)。微囊藻毒素降解实验结果表明,该菌株能在以MC-LR为唯一碳源、氮源的无机盐培养基中生长,6 d内可将初始质量浓度为15 mg/L的MC-LR降解为8.12 mg/L,降解效率达到45.9%。菌株DHU-28的最适生长温度是30℃,最适生长pH为7.0。酵母粉、蛋白胨、葡萄糖等营养物质可以明显促进菌株对MC-LR的降解效率,尤其是加入50 mg/L酵母粉后,6 d降解率达到63.2%。     

高效液相色谱法检测水中5种微囊藻毒素

使用Agilent1260型高效液相色谱仪,建立定量测定天然水体中5种微囊藻毒素（MC-RR、YR、LR、LA、LY）的分析方法。比较甲醇/三氟乙酸（TFA）水溶液与甲醇/磷酸两种流动相体系,待测物质的响应程度,结果发现,TFA作为缓冲溶液时,基线较磷酸稳定,因此,选择甲醇/TFA水溶液作为流动相。比较不同TFA体积比例,待测物质的分离程度,结果显示,甲醇/0.02%的TFA水溶液作为流动相时,5种MCs含量的分离度较好。比较等度和梯度洗脱条件,发现,梯度洗脱条件5种MCs的分离度较等度洗脱条件好。该方法 MC-RR、YR、LR、LA、LY的最低检出限（LOD）分别为0.015、0.035、0.018、0.032和0.026μg/L,最低定量限（LOQ）分别是0.049、0.117、0.062、0.106和0.086μg/L。在0.10～1.50μg/mL的线性范围内,相关系数R2≥0.99,实际水样回收率为73.9%～103.3%。     

一株微囊藻毒素降解菌的分离与鉴定

以水华蓝藻细胞中提取的微囊藻毒素为筛选物质,从太湖水华腐烂蓝藻中富集筛选出1株微囊藻毒素降解菌。该菌株革兰氏染色呈阴性,细胞细长杆状,菌落黄色,圆形,不透明,接触酶、氧化酶实验均呈阳性。16S rRNA基因序列的长度为1 416 bp(GenBank登录号为FJ976656)。系统发育树显示,该菌株与微嗜酸寡养单胞菌(Stenotrophomonas acidam-iniphila)的亲缘关系最近。通过菌株形态特征、生理生化特征和16S rRNA基因序列分析,将此菌株鉴定为微嗜酸寡养单胞菌,不同于已报道的微囊藻毒素降解菌属种。微囊藻毒素降解实验表明,该菌株5 d内将15.4 mg/L的微囊藻毒素完全降解,降解能力高于假单胞菌。     

碳源对铜绿微囊藻生理特性及微囊藻毒素产率的影响

为研究水体中不同碳源对铜绿微囊藻生理特性的影响,以Na2CO3与葡萄糖分别作为铜绿微囊藻生长的无机碳源与有机碳源,将铜绿微囊藻于光照下进行培养,并对其一系列的生理特性与微囊藻毒素产率进行检测。实验结果表明,同等碳浓度下,有机碳源更能促进铜绿微囊藻的生长,经过30 d的培养,铜绿微囊藻在有机碳源中的产量为187.55 g,比其在无机碳源中的产量提高了6.06%;微囊藻毒素在有机碳源中的产量为969.00μg/g,而在无机碳源中的产量却升高至1 193.60μg/g。参与藻毒素合成的3种氨基酸在无机碳源中的浓度要比有机碳源中的浓度高,但是其余几种氨基酸的含量与之情况相反。而有机碳源培养的铜绿微囊藻总可溶性蛋白含量为387.00μg/g,比无机碳源培养的铜绿微囊藻的蛋白含量提高了93.60%。     

微囊藻毒素生物降解的研究进展

蓝藻水华污染造成的最主要危害之一是产生和释放以微囊藻毒素(microcystins,MCs)为主的多种藻毒素,其在饮用水中的存在可以导致人类癌症,因此对人们的健康构成了严重威胁.从MCs降解微生物菌种、酶催化降解途径和降解基因3个方面,介绍了近年来国内外MCs生物降解的研究进展.     

臭氧氧化降解烷基多苷的试验研究

分析了碱性介质臭氧降解烷基多苷(APG)的机制,进行了臭氧氧化降解APG的试验研究。结果表明,臭氧对APG有较强的氧化能力;有机质初始浓度高有利于其氧化降解;初始阶段降解速率较快,当COD降解率达80%时,再增加臭氧的通入量,降解变慢;臭氧氧化处理APG过程中泡沫的产生、存在的时间及消除与APG的浓度、氧化降解程度密切相关。     

Degradation of diuron in aqueous solution by ozonation

Degradation of diuron [3-(3,4-dichlorophenyl)-1,1-dimethylurea] in aqueous solution and the proposed degradation mechanism of diuron by ozonation were investigated. The factors that affect the degradation efficiency of diuron were examined. The generated inorganic ions and organic acids during the ozonation process were detected. Total organic carbon removal rate and the amount of the released Cl^? increased with increasing ozonation time, but only 80.0% of the maximum theoretical concentration of Cl^? at total mineralization was detected when initial diuron concentration was 13.8 mg L^?1. For N species, the final concentrations of NO₃ ^? and NH₄ ⁺ after 60 min of reaction time were 0.28 and 0.19 mg L^?1, respectively. The generated acetic acid, formic acid and oxalic acid were detected during the reaction process. The main degradation pathway of diuron by ozonation involved a series of dechlorination-hydroxylation, dealkylation and oxidative opening of the aromatic ring processes, leading to small organic species and inorganic species. The degradation efficiency of diuron increased with decreasing initial diuron concentration. Higher pH value, more ozone dosage, additive Na₂CO₃, additive NaHCO₃ and additive H₂O₂ were all advantageous to improve the degradation efficiency of diuron.     

臭氧对饮用水管网中溶解性有机物的影响

利用生物膜环状反应器模拟配水管网系统,将水厂砂滤池出水经过臭氧氧化后投加氯然后进入该模拟管网,另外把水厂砂滤池出水加氯后通入另一模拟管网作为对照实验。通过对两管网出水余氯、总铁、浊度、溶解性有机物(DOC)、以及消毒副产物三卤甲烷(THMs)、卤乙酸(HAAs)生成情况的测定,研究了饮用水臭氧处理对管网出水水质的影响。单因素方差分析结果表明,两管网出水的余氯、总铁、浊度以及THMs、HAAs含量相差不大,但DOC在臭氧氯管网中消耗较多。同时通过高效凝胶色谱(HPSEC), 红外光谱(FTIR)和三维荧光光谱(EEM)表征了不同管网进出水DOC变化,结果表明,臭氧氧化后的管网出水中溶解性有机物荧光光谱中三区富里酸和五区腐植酸荧光峰值(ФⅢ+Ⅴ,n)减小较多,管网出水消毒副产物稍有增加。     

Influence of alum on cyanobacterial blooms and water quality of earthen fish ponds

Eruption of blue-green algal blooms occurs frequently in eutrophic lakes and fish ponds, with associated unpleasant odor and horrid scums. In the present study, we conducted a pre-test experiment in 3 m³ outdoor concrete ponds to determine the optimum concentration of aluminum sulfate (alum) required for reduction of the cyanobacterial blooms without negative effect on fish growth. As a consequence, 10 mg L^?1 alum was named as the optimum concentration that was applied in 1000 m³ earthen fish ponds. Obtained results showed that Secchi disc values significantly increased from 10 to 24 cm after 14 days of alum application. Alum-treated ponds showed a reduction in total phytoplankton counts by 94 and 96 % compared to the corresponding controls after 10 and 14 days, respectively. Abundance of blue-green algae in the treated ponds was decreased by 98 % compared to the corresponding control after 14 days of alum application. Consequently, dissolved oxygen, pH, total phosphorus, orthophosphate, and chlorophyll “a” content declined significantly. Our study revealed that using 10 mg L^?1 of alum is an effective way to control cyanobacterial blooms in eutrophic waters, especially in fish ponds, without negative effect in water quality.     

臭氧氧化降解给水系统中诺氟沙星的实验研究

采用臭氧氧化技术处理给水系统中难降解的诺氟沙星(NOR),考察了NOR臭氧氧化的影响因素,得出最佳的处理条件:初始pH为8,臭氧投加量为5 mg/L,反应90 min后去除效率达31.02%,较常规处理大大提高,同时还对反应机理进行了初步探索,研究表明,NOR经臭氧氧化后生成多种小分子物质。     

臭氧氧化对ASBR/SBR工艺SBR段污泥和上清液的性质影响

研究了臭氧氧化对ASBR/SBR工艺中SBR段污泥性质和上清液的影响.结果表明,当臭氧投加量为0～0.349 g O3/g MLSS时,随着施加臭氧浓度的不断增加,MLSS、MLVSS和污泥的生物活性明显降低,但污泥的沉淀性却增强了.污泥上清液中,TN、NH4+-N、NO3--N、PO43--P和多糖浓度均随着臭氧投加...     

碳纳米管催化臭氧降解PFOS动力学与过程控制

针对全氟化合物难降解问题,通过碳纳米管（CNT）诱导臭氧高级氧化路径,研究非均相催化体系对高稳性全氟辛烷磺酸（PFOS）的降解效能与机制。结果表明：CNT介质可催化臭氧通过C-F断键对PFOS强制氧化分解,其准一级降解常数（k=0.037 min-1,5 mg·L-1 CNT）均高于碱式臭氧处理（k=0.009 min-1,pH=11）以及高负荷活性炭颗粒（k=0.013 min-1,5 g·L-1 GAC）;溶液pH是控制催化过程的重要因素,酸性或碱性环境由于PFOS吸附阻隔均不利于CNT表面与溶解O3的接触催化反应;结合羟基自由基淬灭实验,推测CNT通过表面石墨层促成·OH大量生成并在固/液界面原位降解PFOS。研究结果可为开发利用CNT介质强化臭氧水处理过程提供科学依据。     

Evaluation of photolysis and hydrolysis of pyraclostrobin in aqueous solutions and its degradation products in paddy water

This study evaluated the hydrolysis and photolysis kinetics of pyraclostrobin in an aqueous solution using ultra-high-performance liquid chromatography–photodiode array detection and identified the resulting metabolites of pyraclostrobin by hydrolysis and photolysis in paddy water using high-resolution mass spectrometry coupled with liquid chromatography. The effect of solution pH, metal ions and surfactants on the hydrolysis of pyraclostrobin was explored. The hydrolysis half-lives of pyraclostrobin were 23.1–115.5?days and were stable in buffer solution at pH 5.0. The degradation rate of pyraclostrobin in an aqueous solution under sunlight was slower than that under UV photolysis reaction. The half-lives of pyraclostrobin in a buffer solution at pH 5.0, 7.0, 9.0 and in paddy water were less than 12?h under the two light irradiation types. The metabolites of the two processes were identified and compared to further understand the mechanisms underlying hydrolysis and photolysis of pyraclostrobin in natural water. The extracted ions obtained from paddy water were automatically annotated by Compound Discoverer software with manual confirmation of their fragments. Two metabolites were detected and identified in the pyraclostrobin hydrolysis, whereas three metabolites were detected and identified in the photolysis in paddy water.     

Utilization of water chestnut for reclamation of water environment and control of cyanobacterial blooms

Overgrowth of water chestnut (Trapa spp.) is a regional problem throughout Asia and North America because of waterway blockage and water fouling upon decomposition. In the present study, we investigated the potential of water chestnut to control cyanobacterial blooms, via a high content of phenolic compounds. In addition, we assessed the impact of biomass harvesting and crude extract application on nutrient balance. We showed that the floating parts of water chestnut contained high concentrations of total phenolics (89.2 mg g^?1 dry weight) and exhibited strong antioxidant activity (1.31 mmol g^?1 dry weight). Methanol-extracted phenolics inhibited growth of Microcystis aeruginosa; the half maximal effective concentration (EC₅₀) of the extracted phenolics was 5.8 mg L^?1, which was obtained from only 103 mg L^?1 of dry biomass (the floating and submerged parts). However, the crude extracts also added important quantities of nitrogen, phosphorus, and potassium (1.49, 1.05, and 16.3 mg g^?1, respectively; extracted dry biomass weight basis); therefore, in practice, nutrient removal before and/or after the extraction is essential. On the other hand, biomass harvesting enables recovery of nitrogen, phosphorus, and potassium from the water environment (23.1, 2.9, and 18.7 mg g^?1, respectively; dry biomass weight basis). Our findings indicate that water chestnut contains high concentrations of phenolics and exhibits strong antioxidant activity. Utilization of these resources, including nutrients, will contribute to reclamation of the water environment, and also to disposal of wet biomass.     

Critical review of actually available chemical compounds for prevention and management of cyanobacterial blooms

Cyanobacteria proliferation is among the most threatening consequences of freshwater pollution. Health risks from human and other-organism exposure to cyanobacteria have led to an effort to find practical methods for cyanobacterial water-bloom reduction. Hence, methods and techniques have been developed in order to reduce the amount of phosphorus or to decrease the abundance of nuisance phytoplankton species directly in the water bodies (in-lake measures). Although these “acute” methods do not solve the problem of catchment area eutrophication, they are cheaper, easier to manage, and for some areas they are the only way to protect human and environmental health against massive cyanobacterial proliferation. This review summarizes the extent of knowledge and published data about the management using metals (Al, Fe, Cu, Ag, Ca), photosensitizers (hydrogen peroxide, phthalocyanines, TiO₂), herbicides and chemicals derived from natural compounds as fast and efficient removal agents of cyanobacteria. This review concludes that some compounds, when non-persistent and ecotoxicologically acceptable may help to manage cyanobacterial blooms in an efficient way compared to previous methods (e.g. copper sulfate).