用水体中大肠菌群的含量检测水质污染程度

微生物污染是水质污染的主要原因之一,常用某些与病原微生物有密切关系的微生物的含量来反映水体中病原微生物存在的可能性。水体中病原微生物污染主要来自人畜粪便。因而常选用存在于人体和哺乳动物肠道中的微生物如大肠菌群作为水质污染指示菌。利用指示菌反映水质污染状况具有快速、灵敏的优点。测定大肠菌群含量常用多管发酵法和滤膜法。     

替代指示微生物在粪便污染源示踪中的研究现状

传统粪便指示微生物仅能反映出环境中粪便污染情况,不能追踪污染来源以及反映病毒污染情况,并且不同环境条件下病原微生物的生态学特征和存活特性具有差异。通过采用不同的替代指示微生物来监测和评价不同水体水质的污染状况,分析指示微生物和病原体之间的相关性,确定在具体情况下应选择哪种粪便污染的指示微生物,有望更全面地评价粪便污染和疾病风险。现总结替代指示微生物的特征和优缺点及其与病原体的相关性,以期客观、准确地评价这类指示微生物预测粪便指示污染的可信度,并为目前微生物源示踪(MST)方法的应用提供参考。     

黄土塬地区集雨窖水水源地优选

为提高黄土塬地区窖水水质,保证窖水饮用安全,集雨水源地的选择势在必行。本文通过应用主成分分析法,研究了优质集雨水源地和决定水质的控制指标。结果表明,在不同类型集雨水源地中,水泥地面和瓦屋面的综合主成分得分分别为-3.350和-1.945,污染程度分级结果为轻度,是集雨的最佳场地;COD、NH4+-N、TP、SS和粪大肠菌群在主成分中具有高荷载值;集雨水受有机物质、地表尘土、人畜粪便污染明显,与人为活动密切相关。最后,就集雨水源地在政策法规、水质保护技术体系、水质检测和保护等方面提出了改善措施和建议。     

岸滩粪便污染指示菌来源与影响因素研究进展

粪便污染指示菌(Fecal Indicator Bacteria,FIB),如大肠杆菌、肠球菌和耐热大肠菌等是用于指示水体中污染程度的微生物,但近年来的研究表明岸滩逐步成为FIB的重要储存库。微生物源示踪技术(MicrobialSourceTracking,MST)等方法被广泛应用于溯源岸滩FIB污染,但FIB进入岸滩环境后的生消机制尚不明确,因此影响FIB在岸滩上生存、消亡的各类因素仍是目前研究的热点。基于此,本文综述了岸滩生态系统中FIB的来源,同时结合国内外研究进展分析了影响FIB生存的非生物因素、生物因素及间隙流动等其他影响因素,并针对岸滩环境中FIB对人体健康的潜在风险提出相关建议,以期降低游客的患病风险,保障公共健康安全。     

分子标记物在禽类粪便污染溯源中的研究及应用进展

排入环境后的禽类粪便不仅会造成水体和土壤环境污染,且其携带的致病菌对人类健康也存在潜在危害,因此快速准确地识别并控制粪便污染源对环境保护和人类健康至关重要。微生物溯源（Microbial source tracking,MST）技术可以利用分子标记物识别人和不同动物的粪便污染,从而有助于及时发现并控制粪便污染。鉴于禽类粪便对环境和人类健康的危害,越来越多的禽类MST标记物被开发并用于禽类的粪便污染溯源研究。归纳总结了多种禽类（如鸡、鸭、鸽子、海鸥、加拿大雁和沙丘鹤等） MST分子标记物及其敏感性和特异性,重点综述了禽类分子标记物的基因来源,包括细菌16S rRNA基因、线粒体DNA和功能基因等。其中,细菌16S rRNA基因在标记物设计中的应用最为广泛,源指示菌主要包括厚壁菌门（Firmicutes）、拟杆菌目（Bacteroidales）、放线菌门（Actinobacteria）、变形菌门（Proteobacteria）和梭杆菌门（Fusobacteria）及其家族成员;以cytb基因、ND5基因、16S rRNA基因和ND2基因等线粒体DNA （Mitochondrial DNA,mtDNA）为设计来源的禽类MST标记物在溯源研究中指示效果最好,具有很大的应用潜能;使用功能基因作为设计来源的禽类MST标记物种类较少,且均表现出较低的敏感性,但是将功能基因作为MST标记物的思路具有一定的参考价值。通过对多种禽类标记物指示效果的比较,能为科研人员快速选择禽类标记物时提供一定的参考。此外,还对禽类MST技术的现存问题进行了分析总结,并对其在我国的发展进行了展望,以期促进MST技术在我国环境质量监测领域中的发展和应用。     

用污染指示菌评价城市水体污染的研究

选择湖南省常德市江北城区水体为代表开展本项研究。结果表明,水体中污染指示菌,总大肠菌群（ＴＣ）和粪大肠菌群（ＦＣ）密度同ＢＯＤ＿５负荷以及综合污染指数Ｐ呈高度正相关。所以,污染指示菌指标,特别是粪大肠菌群指标足综合评价城市污水,尤其是生活污水污染的一个必不可少的重要参数。对该城区水体细菌污染的评价结果是,生活污水排放愈集中的地区,细菌污染愈严重。其中护城河水的ＴＣ密度超出我国地面水Ⅲ级标准４个数量级;ＦＣ密度超过ＷＨＯ娱乐用水标准３个数量级。护城河是细菌污染最严重水体。包括滨湖公园内湖在内的接纳生活污水多或较多的水体,细菌污好也相当严重。只是远离城区的柳叮湖受污染程度较轻。     

环境条件对猪粪好氧堆肥过程的影响

禽畜粪便的大量排放给环境造成了巨大污染,其中猪场粪便和污水是最主要的污染源。为了实现猪粪的无害化、减量化和资源化,好氧堆肥是目前普遍应用和效果良好的实用技术。为了探明堆肥过程的生物学和化学过程,论本文主要从几个影响因素如温度、调理剂、含水率、通风方式、微生物菌剂等对猪粪好氧堆肥技术方面进行了综述。     

利用拟杆菌分子标记物对粪便污染溯源的研究进展

拟杆菌(Bacteroidales)是粪便污染的主要标志之一,近年来被广泛应用在水体微生物溯源领域,并展现了良好的应用前景.拟杆菌微生物溯源的优势在于不需要纯培养过程,直接根据拟杆菌具有的宿主特异性生物标记引物设计,通过检测水体中拟杆菌生物标记的存在情况来判断粪便污染来源.本文从人、猪、反刍动物等拟杆菌特异性生物标记的发现、引物设计以及其应用综述了拟杆菌在微生物溯源中的研究进展,指出了应用过程中的局限性.本文还对拟杆菌在溯源中的应用进行了展望.提出了寻找新的宿主特异性拟杆菌生物标记是研究的主要方向,在应用研究中应注重与其他溯源方法相结合以使溯源结果更加准确.     

应用定量微生物风险评估海水浴场人体健康风险

【背景】定量微生物风险评估作为定量评估游泳人群暴露于病原微生物后健康风险的方法,在国外已得到广泛应用,但目前国内的应用处于起步阶段且缺乏所需的游泳人群暴露数据。【目的】收集游泳人群暴露数据,并在海水浴场中进行应用,评估粪大肠菌群作为风险评估指标的可行性。【方法】通过对6个典型海水浴场的水质状况、粪大肠菌群浓度与环境因子的相关性进行分析,并发放调查问卷收集国内游泳人群的暴露数据,进而应用定量微生物风险评估方法,得出各个海水浴场的胃肠道疾病患病风险。【结果】6个海水浴场中粪大肠菌群浓度均与水温、气温及总云量具有显著相关性(P<0.01)。位于南方的海水浴场粪便污染情况较北方严重,粪大肠菌群浓度第95百分位数远高于国内“差”类水质标准的阈值。儿童、成年男性、成年女性单次沐浴事件吞下海水的体积分别为35.1 mL (95%置信区间为32.4-37.8,α=0.578,β=0.016),45.0 mL (95%置信区间为31.1-59.3,α=0.532,β=0.012),35.7 mL (95%置信区间为29.7-41.8,α=0.753,β=0.032)。6个海水浴场患胃肠道疾病的风险...     

模拟稳定塘系统对污染指示菌的去除作用

本文研究了模拟稳定塘系统去除污染指示菌如总大肠菌群(TC),粪大肠菌群(FC),粪链球菌(FS)以及异养细菌(HPC)的作用。结果表明,16℃时污水在日进污水10t的模拟稳定塘系统停留9天后,TC与FC的密度下降4个数量级。在日进污水90t,污水理论水力停留时间10天的模拟稳定塘系统进行的全年跟踪监测结果表明,TC与FC密度随各塘依次递减。Ⅳ号塘出水的TC密度下降2.5个数量级,基本上达到了我国GB3838-88中规定的地面水Ⅲ级标准;FC密度下降3个数量级,达到WHO标准的轻污染水平,肯定了稳定塘系统去除污染指示菌的有效性。     

Distribution of genetic marker concentrations for fecal indicator bacteria in sewage and animal feces

Very little is known about the density and distribution of fecal indicator bacteria (FIB) genetic markers measured by quantitative real-time PCR (qPCR) in fecal pollution sources. Before qPCR-based FIB technologies can be applied to waste management and public health risk applications, it is vital to characterize the concentrations of these genetic markers in pollution sources (i.e., untreated wastewater and animal feces). We report the distribution of rRNA genetic markers for several general FIB groups, including Clostridium spp., Escherichia coli, enterococci, and Bacteroidales, as determined by qPCR on reference collections consisting of 54 primary influent sewage samples collected from treatment facilities across the United States and fecal samples representing 20 different animal species. Based on raw sewage sample collection data, individual FIB genetic markers exhibited a remarkable similarity in concentration estimates from locations across the United States ranging from Hawaii to Florida. However, there was no significant correlation between genetic markers for most FIB combinations (P > 0.05). In addition, large differences (up to 5 log(10) copies) in the abundance of FIB genetic markers were observed between animal species, emphasizing the importance of indicator microorganism selection and animal source contribution for future FIB applications.     

Biotic Interactions and Sunlight Affect Persistence of Fecal Indicator Bacteria and Microbial Source Tracking Genetic Markers in the Upper Mississippi River

The sanitary quality of recreational waters that may be impacted by sewage is assessed by enumerating fecal indicator bacteria (FIB) (Escherichia coli and enterococci); these organisms are found in the gastrointestinal tracts of humans and many other animals, and hence their presence provides no information about the pollution source. Microbial source tracking (MST) methods can discriminate between different pollution sources, providing critical information to water quality managers, but relatively little is known about factors influencing the decay of FIB and MST genetic markers following release into aquatic environments. An in situ mesocosm was deployed at a temperate recreational beach in the Mississippi River to evaluate the effects of ambient sunlight and biotic interactions (predation, competition, and viral lysis) on the decay of culture-based FIB, as well as molecularly based FIB (Entero1a and GenBac3) and human-associated MST genetic markers (HF183 and HumM2) measured by quantitative real-time PCR (qPCR). In general, culturable FIB decayed the fastest, while molecularly based FIB and human-associated genetic markers decayed more slowly. There was a strong correlation between the decay of molecularly based FIB and that of human-associated genetic markers (r², 0.96 to 0.98; P < 0.0001) but not between culturable FIB and any qPCR measurement. Overall, exposure to ambient sunlight may be an important factor in the early-stage decay dynamics but generally was not after continued exposure (i.e., after 120 h), when biotic interactions tended to be the only/major influential determinant of persistence.     

Microbial Source Tracking for Identification of Fecal Pollution

Fecal pollution is a serious environmental problem that affects many coastal and inland waters worldwide. Both human and animal fecal pollution impose risks to human health from exposure to pathogenic bacteria, viruses, and protozoa. To assist authorities with the implementation of the changes suggested by more restricted legislation concering water quality in Europe, methods are needed which can identify the sources of fecal pollution. Management of fecal contamination of water would be improved if the origin of the fecal pollution could be correctly identified since remediation efforts could then be allocated in a more effective manner. The concept that the origin of fecal pollution can be traced has been termed microbial source tracking. In microbial source tracking (MST) endogenous markers of fecal sources are used for identification of the fecal pollution in aquatic environments. Chemical MST-methods can be used to trace mainly sewage pollution, but the used chemical targets have no direct relationship with pathogenic bacteria. This is not the case in microbial MST-methods where source-specific bacteria or viruses are cultured to identify fecal pollution sources. However, sometimes these microbial targets can be present in too low numbers to be detected. This is circumvented by using molecular assays for host-specific marker detection. Phenotypic and genotypic library-based methods can be used to discriminate among different fecal sources. However, the isolation step makes this procedure very labour-intensive, and issues as temporal and geographical variability remain unresolved. The underlying assumptions will be discussed and the methods mostly used in microbial source tracking will be described in more detail.     

Persistence and differential survival of fecal indicator bacteria in subtropical waters and sediments

Fecal coliforms and enterococci are indicator organisms used worldwide to monitor water quality. These bacteria are used in microbial source tracking (MST) studies, which attempt to assess the contribution of various host species to fecal pollution in water. Ideally, all strains of a given indicator organism (IO) would experience equal persistence (maintenance of culturable populations) in water; however, some strains may have comparatively extended persistence outside the host, while others may persist very poorly in environmental waters. Assessment of the relative contribution of host species to fecal pollution would be confounded by differential persistence of strains. Here, freshwater and saltwater mesocosms, including sediments, were inoculated with dog feces, sewage, or contaminated soil and were incubated under conditions that included natural stressors such as microbial predators, radiation, and temperature fluctuations. Persistence of IOs was measured by decay rates (change in culturable counts over time). Decay rates were influenced by IO, inoculum, water type, sediment versus water column location, and Escherichia coli strain. Fecal coliform decay rates were significantly lower than those of enterococci in freshwater but were not significantly different in saltwater. IO persistence according to mesocosm treatment followed the trend: contaminated soil > wastewater > dog feces. E. coli ribotyping demonstrated that certain strains were more persistent than others in freshwater mesocosms, and the distribution of ribotypes sampled from mesocosm waters was dissimilar from the distribution in fecal material. These results have implications for the accuracy of MST methods, modeling of microbial populations in water, and efficacy of regulatory standards for protection of water quality.     

Enterococci in the Environment

Summary: Enterococci are common, commensal members of gut communities in mammals and birds, yet they are also opportunistic pathogens that cause millions of human and animal infections annually. Because they are shed in human and animal feces, are readily culturable, and predict human health risks from exposure to polluted recreational waters, they are used as surrogates for waterborne pathogens and as fecal indicator bacteria (FIB) in research and in water quality testing throughout the world. Evidence from several decades of research demonstrates, however, that enterococci may be present in high densities in the absence of obvious fecal sources and that environmental reservoirs of these FIB are important sources and sinks, with the potential to impact water quality. This review focuses on the distribution and microbial ecology of enterococci in environmental (secondary) habitats, including the effect of environmental stressors; an outline of their known and apparent sources, sinks, and fluxes; and an overview of the use of enterococci as FIB. Finally, the significance of emerging methodologies, such as microbial source tracking (MST) and empirical predictive models, as tools in water quality monitoring is addressed. The mounting evidence for widespread extraenteric sources and reservoirs of enterococci demonstrates the versatility of the genus Enterococcus and argues for the necessity of a better understanding of their ecology in natural environments, as well as their roles as opportunistic pathogens and indicators of human pathogens.     

Decay of bacterial pathogens, fecal indicators, and real-time quantitative PCR genetic markers in manure-amended soils

This study examined persistence and decay of bacterial pathogens, fecal indicator bacteria (FIB), and emerging real-time quantitative PCR (qPCR) genetic markers for rapid detection of fecal pollution in manure-amended agricultural soils. Known concentrations of transformed green fluorescent protein-expressing Escherichia coli O157:H7/pZs and red fluorescent protein-expressing Salmonella enterica serovar Typhimurium/pDs were added to laboratory-scale manure-amended soil microcosms with moisture contents of 60% or 80% field capacity and incubated at temperatures of -20°C, 10°C, or 25°C for 120 days. A two-stage first-order decay model was used to determine stage 1 and stage 2 first-order decay rate coefficients and transition times for each organism and qPCR genetic marker in each treatment. Genetic markers for FIB (Enterococcus spp., E. coli, and Bacteroidales) exhibited decay rate coefficients similar to that of E. coli O157:H7/pZs but not of S. enterica serovar Typhimurium/pDs and persisted at detectable levels longer than both pathogens. Concentrations of these two bacterial pathogens, their counterpart qPCR genetic markers (stx1 and ttrRSBCA, respectively), and FIB genetic markers were also correlated (r = 0.528 to 0.745). This suggests that these qPCR genetic markers may be reliable conservative surrogates for monitoring fecal pollution from manure-amended land. Host-associated qPCR genetic markers for microbial source tracking decayed rapidly to nondetectable concentrations, long before FIB, Salmonella enterica serovar Typhimurium/pDs, and E. coli O157:H7/pZs. Although good indicators of point source or recent nonpoint source fecal contamination events, these host-associated qPCR genetic markers may not be reliable indicators of nonpoint source fecal contamination events that occur weeks following manure application on land.     

Seasonal detection of human viruses and coliphage in Newport Bay, California

Recent studies have shown that the fecal indicator bacteria (FIB) currently used to indicate water quality in the coastal environment may be inadequate to reflect human viral contamination. Coliphage was suggested as a better indicator of human viral pollution and was proposed by the U.S. EPA as an alternative indicator for fecal pollution in groundwater. In this study, we investigated the occurrence and distribution of FIB, F+ coliphage, and PCR-detectable human adenovirus and enterovirus for an entire year at 15 locations around the Newport Bay watershed, an important southern California estuary for water recreation and an ecological reserve. Peak concentrations and prevalences of FIB and F+ coliphage were associated with winter storms (wet weather). Human adenoviruses and enteroviruses, however, were detected by PCR in approximately 5% of samples collected in the summer (dry weather) but only once in wet weather. These results demonstrated that FIB and coliphage have similar seasonal and freshwater-to-saltwater distribution patterns, while the detection of human viruses depends on a distribution pattern that is the opposite of that of FIB and coliphage. This research suggested that coliphage and FIB share similar environmental sources, while sources of human viruses in Newport Bay are perhaps different.     

Persistence and Differential Survival of Fecal Indicator Bacteria in Subtropical Waters and Sediments

Fecal coliforms and enterococci are indicator organisms used worldwide to monitor water quality. These bacteria are used in microbial source tracking (MST) studies, which attempt to assess the contribution of various host species to fecal pollution in water. Ideally, all strains of a given indicator organism (IO) would experience equal persistence (maintenance of culturable populations) in water; however, some strains may have comparatively extended persistence outside the host, while others may persist very poorly in environmental waters. Assessment of the relative contribution of host species to fecal pollution would be confounded by differential persistence of strains. Here, freshwater and saltwater mesocosms, including sediments, were inoculated with dog feces, sewage, or contaminated soil and were incubated under conditions that included natural stressors such as microbial predators, radiation, and temperature fluctuations. Persistence of IOs was measured by decay rates (change in culturable counts over time). Decay rates were influenced by IO, inoculum, water type, sediment versus water column location, and Escherichia coli strain. Fecal coliform decay rates were significantly lower than those of enterococci in freshwater but were not significantly different in saltwater. IO persistence according to mesocosm treatment followed the trend: contaminated soil > wastewater > dog feces. E. coli ribotyping demonstrated that certain strains were more persistent than others in freshwater mesocosms, and the distribution of ribotypes sampled from mesocosm waters was dissimilar from the distribution in fecal material. These results have implications for the accuracy of MST methods, modeling of microbial populations in water, and efficacy of regulatory standards for protection of water quality.     

Association of fecal indicator bacteria with human viruses and microbial source tracking markers at coastal beaches impacted by nonpoint source pollution

Water quality was assessed at two marine beaches in California by measuring the concentrations of culturable fecal indicator bacteria (FIB) and by library-independent microbial source tracking (MST) methods targeting markers of human-associated microbes (human polyomavirus [HPyV] PCR and quantitative PCR, Methanobrevibacter smithii PCR, and Bacteroides sp. strain HF183 PCR) and a human pathogen (adenovirus by nested PCR). FIB levels periodically exceeded regulatory thresholds at Doheny and Avalon Beaches for enterococci (28.5% and 31.7% of samples, respectively) and fecal coliforms (20% and 5.8%, respectively). Adenoviruses were detected at four of five sites at Doheny Beach and were correlated with detection of HPyVs and human Bacteroides HF183; however, adenoviruses were not detected at Avalon Beach. The most frequently detected human source marker at both beaches was Bacteroides HF183, which was detected in 27% of samples. Correlations between FIBs and human markers were much more frequent at Doheny Beach than at Avalon Beach; e.g., adenovirus was correlated with HPyVs and HF183. Human sewage markers and adenoviruses were routinely detected in samples meeting FIB regulatory standards. The toolbox approach of FIB measurement coupled with analysis of several MST markers targeting human pathogens used here demonstrated that human sewage is at least partly responsible for the degradation of water quality, particularly at Doheny Beach, and resulted in a more definitive assessment of recreational water quality and human health risk than reliance on FIB concentrations alone could have provided.