二甲基硅油的环境行为与生态效应研究进展

二甲基硅油(polydimethylsiloxane,PDMS)广泛应用于工业产品、医药保健品和个人护理品中.PDMS在污水处理过程中几乎不被生物降解,主要随剩余污泥排放进入环境,仅有少量PDMS吸附在悬浮固体或污泥颗粒表面随污水排放进入水体和沉积物中.现有研究表明,PDMS在沉积物中较难迁移和降解;而在不同类型土壤中均可以降解.PDMS对水生态系统风险较低,对底栖生物的急性毒性也不明显;在土壤环境中,PDMS及其降解产物对土壤微生物、土壤动物及农作物的生长和活动没有显著的影响.根据目前为数不多的研究,PDMS及其降解产物在各种环境中的生态毒性都较小,但随着PDMS产量和使用量的快速增长,其在环境中的含量呈快速上升趋势,有必要进一步明确PDMS对环境的潜在威胁.     

土壤和沉积物中黑碳的环境行为及效应研究进展

土壤和沉积物是全球黑碳排放的主要归宿,土壤和沉积物中黑碳具有复杂的环境行为和环境效应。分析了黑碳的概念,指出应以环境意义为出发点去理解黑碳概念的丰富内涵;描述了黑碳形成过程及其对黑碳理化性质的影响,以及基于此的黑碳分类;总结了黑碳来源辨析的若干种常用方法;讨论了黑碳在土壤/沉积物与其他环境介质之间的迁移循环过程,以及在土壤和沉积物内部的迁移行为;探讨了土壤和沉积物中黑碳的降解行为与稳定性,及其与地-气碳氮温室气体通量、土壤稳定碳库的关系,以及在土壤碳循环模型中的作用;综述了土壤和沉积物中黑碳对有机物、重金属和营养盐的吸附行为及主要机制;提出了今后研究的主要方向,以供相关研究者参考。     

环境介质中的抗生素及其微生物生态效应

环境介质中的抗生素因存在浓度较低被称为微量污染物,其对生态系统和人类健康的影响已逐步得到认知。长期以来,抗生素被用于人和畜禽细菌性感染疾病的治疗。然而,随着集约化养殖业的发展,抗生素被大量添加于饲料中来预防畜禽和鱼虾的养殖疾病。因此,环境介质中抗生素种类和含量随着畜禽和水产养殖业的快速发展逐年增加。本文综述了环境中抗生素的来源、残留浓度及其环境微生物生态学效应。医用、兽用抗生素和人畜粪便的农用是抗生素进入环境的主要来源,其在不同环境介质中残留浓度不一：地表水含量为μg?L-1,土壤含量为?g?kg-1,沉积物含量为μg?kg-1—mg?kg-1之间。抗生素进入土壤、水和沉积物等环境介质,经吸附-解吸、迁移和降解等过程重新分配,其降解方式主要有水解、光解和生物降解。抗生素影响环境介质中微生物的生物量、活性和群落结构,并诱导产生抗性基因,但对生态系统服务及其功能的干扰和影响尚有待进一步研究。     

四环素类抗生素降解途径及其主要降解产物研究进展

四环素类抗生素在生产和贮存过程中会发生一系列非生物降解反应,其中某些代谢及降解产物,与母体相比,虽然其活性降低,但毒性却大大增强.此类抗生素随着畜禽废弃物等途径进入到环境中,随环境条件的不同将发生一种或多种降解反应,其降解方式除了非生物降解外,还包括生物降解.本文综述了四环素类抗生素在不同生态环境中的降解途径以及降解产物,并对今后的研究方向进行了探计,旨在为其生态风险评价提供有价值的参考.     

大亚湾冬季沉积物中叶绿素含量与分布

2012年2月(冬季)对大亚湾海域沉积物叶绿素a (Chl-a)及其降解产物脱镁叶绿酸( Pha-a)的含量与分布进行了研究,并探讨了环境因子(水深、温度、透明度、粒度、营养盐、TOC)对表层沉积物Chl-a含量分布的影响.结果表明:Chl-a和Pha-a是同源的,随沉积物深度增加二者皆呈递减趋势,个别站位Chl-a和Pha-a出现许多小突跃,这可能与生物扰动和环境变化有关;表层(0～l cm)Chl-a和Pha-a的含量变化范围分别为0.98 ～ 1.55μg·g-1和3.97～6.65 μg·g-1,平均含量分别为1.24和5.55 μg ·g-1.Chl-a含量变化是各种环境因子共同作用的结果,其中最主要的影响因素是沉积物底质颗粒的大小,高比例砂含量的底质能为底栖藻类提供更多的生存空间,但不利于沉积物中Pha-a的保存;比较了沉积物与上层水体中平均Chl-a相对含量,并与其他海域相比较,发现该海域沉积物中Chl-a含量较高,与水体Chl-a含量比值为50.28％ ～ 150.79％,近海沉积物中底栖初级生产力不可忽视.     

东海赤潮高发区沉积物中叶绿素的分析

研究分析了2002年8～9月“赤潮973”航次所采集的沉积物中叶绿素a及其降解产物脱镁叶绿酸含量与分布．结果表明。叶绿素a和脱镁叶绿酸是同源的;随深度增加叶绿素a和脱镁叶绿酸的含量呈递减趋势,到一定深度后含量不再变化。个别站位叶绿素a和脱镁叶绿酸的垂直分布出现了许多小突跃,可能是由生物扰动引起;表层沉积物(0～0．5cm)中的叶绿素a和脱镁叶绿酸的变化幅度分别为0．14～1．17和0．83～5．58μg·g-1。平均值分别为0．54和2．45μg·g-1;并初步探讨水深(光强)、盐度、温度、含水量对叶绿素水平分布的影响;脱镁叶绿酸作为叶绿素的主要降解产物,到一定深度后,成为叶绿素的主要存在形式,约占80％～90％;由于水温的不同,夏季沉积物中的叶绿素a和脱镁叶绿酸含量是春季的3倍之多;比较了上层水柱中的叶绿素和沉积物中的叶绿素的相对含量,平均而言,沉积物中叶绿素占上层水柱中叶绿素的31％．     

假单胞菌菌株CTN-3对百菌清污染土壤的生物修复

百菌清被美国环境保护署列为优先控制污染物,利用微生物的降解作用修复被污染的土壤、清除环境中的污染物等具有重要的现实意义.假单胞菌(Pseudomonas sp.)菌株CTN-3是一株从污染土壤中分离得到的百菌清降解菌,考察了其在实验室条件下对百菌清污染土壤的生物修复能力及其影响因素.结果表明:降解菌株在灭菌土壤中的降解效果略好于未灭菌土壤;在外源添加降解菌106 CFU·g-1、温度15 ～ 30℃和pH5.8～8.3条件下,该菌株能有效降解土壤中10 ～200 mg·kg-1的百菌清.菌株CTN-3在百菌清污染土壤的生物修复中具有良好的应用前景.     

土壤活性有机碳

土壤活性有机碳是土壤中活跃的化学组分,能显著影响土壤化学物质的溶解、吸附、解吸、吸收、迁移乃至生物毒性等行为,近年来土壤活性有机碳已成为土壤、环境和生态科学领域所关注的焦点和研究的热点。本文从土壤活性有机碳的来源、组成、含量、影响因素以及环境意义等方面做了简要的论述。一般认为,土壤活性有机碳来源于植物凋落物的分解、根系分泌物、土壤有机质的水解、土壤微生物本身及其代谢产物,因为来源的不同土壤活性有机碳含量也不同;影响土壤活性有机碳的因素有很多,研究表明,土壤活性有机碳随季节和湿度的变化呈现十分强烈的变异趋势;土地利用方式改变对土壤活性有机碳的影响在不同的研究中有不同的结果;土地管理措施如耕作、施有机肥和化肥、改变土壤pH值等对土壤活性有机碳也有很大的影响。土壤活性有机碳的生态环境效应主要表现在它对调节土壤养分流有很大影响,与土壤内在的生产力高度相关;它作为重金属的有机配体,对土壤溶液中的微量重金属的可移动性和迁移过程以及金属复合物的形成过程有着重要作用;它的存在影响农药在土壤中的截留、增加农药的水溶性,并影响农药在土壤中的运动;它对温室气体的排放、水体富营养化、岩石圈溶蚀都有很重要的作用。同时指出了未来的研究方向。     

嗜热微生物及其降解剩余污泥的机理

活性污泥法已经被广泛应用于污水处理中.剩余污泥是此过程的副产物,其处理费用约占污水处理系统总成本的25%～60%,处理不当则会带来严重的二次污染,成为目前污泥处理研究的难点之一.利用嗜热微生物降解污泥操作方便、经济性较好且易于管理,具有良好的应用前景.本文对污泥降解中的嗜热微生物、嗜热微生物污泥降解机理以及污泥降解过程中起重要作用的嗜热蛋白酶和脂肪酶的最新研究进展进行综述,归纳总结了影响嗜热微生物降解污泥的主要影响因素,并对嗜热微生物在污泥消化方面的应用研究进行展望.     

城市污泥中邻苯二甲酸酯(PAEs)的厌氧微生物降解

邻苯二甲酸酯(PAEs)是城市污泥中普遍存在的一类具有内分泌干扰性作用的有机污染物.研究污泥厌氧生物处理过程中PAEs的微生物降解对保障污泥农用的安全性十分必要.本文以污泥中两种主要的PAEs——邻苯二甲酸二丁酯(DBP)和邻苯二甲酸(2-乙基己)酯(DEHP)为研究对象,通过比较PAEs在污泥厌氧消化系统与发酵产氢系统中降解过程的差异及系统污泥特性的变化,分析不同污泥厌氧生物处理系统中影响PAEs降解的可能因素.结果表明: 在污泥厌氧发酵系统中,DBP在6 d内降解率达99.6%, DEHP在整个14 d的培养期间也降解了46.1%;在发酵产氢系统中,在14 d培养过程DBP的降解率仅为19.5%,DEHP则没有明显的降解.与厌氧消化系统相比,PAEs在发酵产氢系统中的降解受到明显抑制,这与发酵产氢过程中微生物量下降、革兰氏阳性菌/革兰氏阴性菌(G⁺/G^-)和真菌/细菌变小及挥发性脂肪酸(包括乙酸、丙酸及丁酸)浓度升高有关.     

The biodegradation of surfactants in the environment

The possible contamination of the environment by surfactants arising from the widespread use of detergent formulations has been reviewed. Two of the major surfactants in current use are the linear alkylbenzene sulphonates (LAS) and the alkyl phenol ethoxylates (APE). These pass into the sewage treatment plants where they are partially aerobically degraded and partially adsorbed to sewage sludge that is applied to land. The biodegradation of these and a range of other surfactants both in wastewater treatment plants and after discharge into natural waters and application to land resulting in sewage sludge amended soils has been considered. Although the application of sewage sludge to soil can result in surfactant levels generally in a range 0 to 3 mg kg(-1), in the aerobic soil environment a surfactant can undergo further degradation so that the risk to the biota in soil is very small, with margins of safety that are often at least 100. In the case of APE, while the surfactants themselves show little toxicity their breakdown products, principally nonyl and octyl phenols adsorb readily to suspended solids and are known to exhibit oestrogen-like properties, possibly linked to a decreasing male sperm count and carcinogenic effects. While there is little serious risk to the environment from commonly used anionic surfactants, cationic surfactants are known to be much more toxic and at present there is a lack of data on the degradation of cationics and their fate in the environment.     

污泥土地利用对农作物及土壤的影响研究

以沈阳北部污水处理厂污泥为研究对象 ,开展了污泥土地利用对农作物及土壤环境影响的研究 .结果表明 ,污泥土地利用可提高土壤中N、P及有机质含量 .污泥用量为 2 2 .5t·hm-2 和 45t·hm-2 时有利于作物生长发育 ,使水稻生物量与对照相比分别增加了 11.48%、11.83%.污泥施用量只要控制在 45t·hm-2以内 ,污泥中的重金属不会对土壤、农产品质量及地下水产生不良的影响 .     

Bacteria-mediated bisphenol A degradation

Bisphenol A (BPA) is an important monomer in the manufacture of polycarbonate plastics, food cans, and other daily used chemicals. Daily and worldwide usage of BPA and BPA-contained products led to its ubiquitous distribution in water, sediment/soil, and atmosphere. Moreover, BPA has been identified as an environmental endocrine disruptor for its estrogenic and genotoxic activity. Thus, BPA contamination in the environment is an increasingly worldwide concern, and methods to efficiently remove BPA from the environment are urgently recommended. Although many factors affect the fate of BPA in the environment, BPA degradation is mainly depended on the metabolism of bacteria. Many BPA-degrading bacteria have been identified from water, sediment/soil, and wastewater treatment plants. Metabolic pathways of BPA degradation in specific bacterial strains were proposed, based on the metabolic intermediates detected during the degradation process. In this review, the BPA-degrading bacteria were summarized, and the (proposed) BPA degradation pathway mediated by bacteria were referred.     

Impacts of anthropogenic activity on the ecology of class 1 integrons and integron-associated genes in the environment

The impact of human activity on the selection for antibiotic resistance in the environment is largely unknown, although considerable amounts of antibiotics are introduced through domestic wastewater and farm animal waste. Selection for resistance may occur by exposure to antibiotic residues or by co-selection for mobile genetic elements (MGEs) which carry genes of varying activity. Class 1 integrons are genetic elements that carry antibiotic and quaternary ammonium compound (QAC) resistance genes that confer resistance to detergents and biocides. This study aimed to investigate the prevalence and diversity of class 1 integron and integron-associated QAC resistance genes in bacteria associated with industrial waste, sewage sludge and pig slurry. We show that prevalence of class 1 integrons is higher in bacteria exposed to detergents and/or antibiotic residues, specifically in sewage sludge and pig slurry compared with agricultural soils to which these waste products are amended. We also show that QAC resistance genes are more prevalent in the presence of detergents. Studies of class 1 integron prevalence in sewage sludge amended soil showed measurable differences compared with controls. Insertion sequence elements were discovered in integrons from QAC contaminated sediment, acting as powerful promoters likely to upregulate cassette gene expression. On the basis of this data, >1 × 10¹⁹ bacteria carrying class 1 integrons enter the United Kingdom environment by disposal of sewage sludge each year.     

Impact of application of organic waste materials on microbial and enzyme activities of mine soils in the Lusatian coal mining region

The objective of the present work was to study the short-term stimulation of microbial and enzyme activity in mine soils by application of organic waste materials in lysimeter and mesocosm studies. The mine soils derived from tertiary and quaternary deposits were ameliorated with brown coal filter ash (tertiary deposits) and lime (quaternary deposits). At the beginning of recultivation the soils were treated with varying amounts of sewage sludge, coal sludge, composted sewage sludge and compost to a depth of 30 cm. In the first 2 years after application of organic waste materials we found a very low level of microbial properties especially in the sandy materials from quaternary deposits but a significant increase in microbial respiration, substrate induced respiration and enzyme activities like invertase and alkaline phosphatase with increasing application rates of sewage sludge, compost and sewage sludge mixed with coal sludge. This can be explained by an increase in organic matter and nutrient content of the soils and an improvement of soil physical properties such as water and nutrient retention capacity. Additionally it can be assumed, that constituents of the coal admixtures of tertiary deposits can be mineralised or converted by the soil microorganisms. In the tertiary materials ameliorated with brown coal ash the highest amounts of microbial and enzyme activities were measured after application of nitrogen-rich sewage sludge or very high amounts of mature compost mainly consisting of green waste. Compared with sewage sludge the stimulating effects of composted sewage sludge were quite lower because of organic matter fragmentation and a reduced energy and nutrient supply to soil microorganisms. This revised version was published online in June 2006 with corrections to the Cover Date.     

Removal of the endocrine disrupter butyl benzyl phthalate from the environment

Butyl benzyl phthalate (BBP), an aryl alkyl ester of 1,2-benzene dicarboxylic acid, is extensively used in vinyl tiles and as a plasticizer in PVC in many commonly used products. BBP, which readily leaches from these products, is one of the most important environmental contaminants, and the increased awareness of its adverse effects on human health has led to a dramatic increase in research aimed at removing BBP from the environment via bioremediation. This review highlights recent progress in the degradation of BBP by pure and mixed bacterial cultures, fungi, and in sludge, sediment, and wastewater. Sonochemical degradation, a unique abiotic remediation technique, and photocatalytic degradation are also discussed. The degradation pathways for BBP are described, and future research directions are considered.     

三氯生的环境残留、降解代谢及其潜在生态风险

三氯生因具有良好的广谱抗菌性能而被广泛应用于各类洗护日化用品中.随着这些日用品被人类不断消耗,三氯生也会通过多种途径进入环境并引发一系列环境问题.环境中残留的三氯生及其代谢产物具有持久性、生物累积性和生态毒性,进而给生态系统带来一定的潜在风险,甚至会对人类健康产生不良影响.基于此,本文总结和分析了三氯生在环境介质中的残留特征及其可能发生的降解代谢过程和产物,并系统地介绍了三氯生及其代谢产物的生物有效性及其对生物体繁殖、遗传和基因等方面的毒性效应,综合分析了三氯生对生态系统和人类健康可能存在的风险,并对有关三氯生后续的研究工作提出了建议和展望.     

表施和混施污泥对团花根系生长的影响

林地利用被认为是污泥资源化利用的重要方式,但施用污泥对林木根系生长的影响报道较少。本研究通过根箱试验,分析表施和混施10%污泥对速生树种团花不同土层根系形态、土壤pH值和电导率动态变化及根系重金属含量的影响,并拟合土壤pH值、电导率和根系重金属含量与根长的关系。结果表明: 与不施污泥(对照)相比,混施污泥显著抑制了团花根长、根表面积和根体积增长,混施污泥120和240 d后,0～20 cm土层总根长分别为不施污泥的76.9%和67.4%;表施污泥对团花根长和根表面积的影响不显著,但显著提高了根体积。混施污泥显著提高了土壤pH值和电导率及根系重金属含量,混施污泥0～20和20～40 cm土层根系镉含量分别是不施污泥的11.5和10.0倍。线性回归拟合分析显示,不同处理0～20 cm土层的电导率与根长均呈显著负相关;表施和混施污泥根系镉含量与根长呈极显著负相关。上述结果表明,混施污泥抑制了团花根系生长,这可能是由于混施污泥提高了土壤电导率和根系镉含量所致,而表施污泥对团花根系生长的作用不明显。     

城市污泥对退化森林生态系统土壤的人工熟化研究

森林退化问题在热带亚热带地区较为严重,在广东鹤山丘陵地区进行的野外试验结果表明,施用城市污水厂污泥可有效地促进树木的生长发育如增加株高和地径,对林中的灌草层植被也有促进和改善;同时可提高林地土壤肥力如土壤有机质和有效养分等,对土壤重金属残留的监测表明,施用污水厂污泥后主要问题是增加了Pb含量,其增加量随污泥用量增加而增加;其它重金属增加不显著。     

Phototransformation of Amlodipine: Degradation Kinetics and Identification of Its Photoproducts

Nowadays, monitoring focuses on the primary compounds and does not include degradation products formed during various biological and chemical processes. Transformation products may have the same effects to human health and the environment or sometimes they can be more toxic than the parent compound. Unfortunately, knowledge about the formation of degradation products is still limited, however, can be very important for the environmental risk assessment. Firstly, the photodegradation kinetic of amlodipine was investigated in two experimental conditions: during the exposure to solar radiation and during the exposure to the light emitted by the xenon lamp. In all cases degradation of amlodipine followed a pseudo-first-order kinetics. In the next step, identification of transformation products of amlodipine formed during the exposure to xenon lamp irradiation was performed using ultra high performance liquid chromatography quadrupole time-of-flight mass spectrometry (UHPLC-QTOF-MS). As a result sixteen photoproducts were identified, their structures were elucidated and ultimately the transformation pathway was proposed. Fifteen compounds (out of 16 photoproducts) were newly identified and reported here for the first time; some of those compounds were formed from the first photoproduct, amlodipine pyridine derivative. Several analytes were formed only in acidic or basic conditions. Furthermore, the occurrence of amlodipine and its identified degradation products was investigated in environmental waters. Only one out of 16 compounds was found in wastewater effluent. The possibility of the sorption of examined analytes to sewage sludge particles was discussed based on QSAR.