粪大肠菌群酶底物法在环境监测中的应用研究

粪大肠菌群作为水体粪便污染的指示菌,对地表水的水质监测评价具有重要作用。采取较为精确、快速的粪大肠菌群检测方法,对控制流行疾病的发生和传播有重要的科学意义。从粪大肠菌群的检测意义、监测方法、标准化应用情况等方面进行归纳分析,提出推广和标准化酶底物法监测粪大肠菌群的迫切性。     

两种酶底物法监测水中(粪)大肠菌群商品化制品的比较

比较了进口colilert试剂和国产colitech试剂及其各自配套制品对水中(粪)大肠菌群的检测,包括总大肠菌群和粪大肠菌群。分别使用同为酶底物法的两种制品检测地表水、地下水、水源水、生活饮用水及污水水样,比较了两种制品用于水中(粪)大肠菌群检测结果的一致性,同时验证了两种制品的无菌性和培养基的选择性。试验结果表明,进口colilert试剂和国产colitech试剂及其各自配套制品于水中(粪)大肠菌群检测结果具有一致性,培养基具有很好的选择性。     

粪大肠菌群酶底物法在环境应急监测中的应用

结合国外粪大肠菌群的酶底物检测方法,针对某次突发环境污染事件,用酶底物法和标准方法多管发酵法同步检测受污染地表水中的粪大肠菌群,讨论酶底物法在应急监测中检测粪大肠菌群的适用性。结果表明,两种方法的测定数据显著相关,没有统计学差异（ P＞0．05）。相对于多管发酵法,酶底物法特异性强,检测时间短,二次污染少,符合应急监测的要求。     

水中粪大肠菌群快速检测方法-固定底物酶底物法与多管发酵法的比较

目的在于比较固定底物酶底物法与多管发酵法用于水中粪大肠菌群(耐热大肠菌群)的检测,使用科立得TM(Colilert(R))试刺和传统方法检测地表水、水源水及污水水样,比较固定底物酶底物法与多管发酵法用于水中粪大肠菌群(耐热大肠菌群)检测结果的一致性.结果表明,固定底物酶底物法与多管发酵法用于水中粪大肠菌群(耐热大肠菌群)检测结果具有一致性,固定底物酶底物法可以用作评价水质微生物污染的标准方法.     

快速测定地表水中粪大肠菌群

地表水中粪大肠菌群是评价水质卫生状况的一项重要指标,一般采用多管发酵标准法测定。该方法工作量大,操作繁琐,周期长。因粪大肠菌群的复发酵试验在44 5℃条件下仍能以产酸产气加以判断,因此,可直接将地表水样接种于EC培养液中,按多管发酵标准法原理计算粪大肠杆菌群数,快速检测。1　材料EC培养液,试管,小倒管等。2　检测方法2 1　操作步骤调节地表水样pH值至中性(7～8),按多管发酵标准法的稀释接种方法对水样作适当稀释,以EC培养液直接接种水样,在44 5℃水浴中培养24h,观察结果。表1　多个样品粪大肠菌群两种测定方法的结果　　L-…     

酶底物法与多管发酵法和纸片法监测环境水样大肠菌群的比较

用标准菌株对比了酶底物法和多管发酵法及快速纸片法,监测分析了分组环境水样中的大肠菌群。结果表明,酶底物法操作快速、简单、结果稳定、无二次污染,能满足水质监测和应急监测的需求。     

兰州市生活饮用水源生物性污染的调查

经过一年时间的调查，查清了兰州市生活饮用水源生物性污染现状，为今后饮用水源的选择与开发提供了科学依据。     

粪大肠菌群快速测定——纸片法的应用

采集苏州具有代表性的地表水水体22个点位的样品,进行粪大肠菌群的测定方法比较,结果表明,《粪大肠菌群快速测定--纸片法》适于测定受粪便污染程度较轻的湖泊水体.但是,该方法的培养时间对阳性管率有明显影响,认为16 h～18 h是比较理想的培养时间.     

水中粪大肠菌群检测方法的比较

采用标准菌株、实际水样和国际标准样品,比较纸片快速法与多管发酵法的一致性。标准菌株试验表明,两种方法在粪大肠菌群的定性检测上没有显著性差异;实际水样试验表明,纸片快速法的检测结果略低于多管发酵法,但两种方法检测结果的回归关系显著;国际标准样品试验表明,两种方法的精密度与准确度均无统计学意义上的显著性差异。     

24孔最大可能数法快速检测水质粪大肠菌群

设计了一种24孔最大可能数法,用玫红酸抑制杂菌,快速检测水质粪大肠菌群。方法能在24 h内检测不同程度污染水样中103L-1~107L-1的粪大肠菌群,回收率为76.1%~108%,批内RSD为24.0%~34.0%。与多管发酵法的比较试验表明,两种方法相关性良好,且在添加玫红酸条件下等效。提出方法还需要更多不同性质及来源水样的检测结果来验证。     

Monitoring E. coli and total coliforms in natural spring water as related to recreational mountain areas

Natural spring water has unique properties, as it is rich in minerals that are considered to be beneficial to human health. A survey of the microbiological quality of natural spring water was conducted to assess possible risks from the consumption of the water by visitors in recreational mountain areas located in Seoul, South Korea. The densities of total coliforms and Escherichia coli were measured during the spring and the summer of 2002 to investigate the presence of coliform bacteria in the drinking spring waters. Total coliforms were detected in all samples and the mean density of total coliforms was up to a maximum of 228 CFU/mL. Detectable E. coli was found in 78% of all samples and the mean densities of E. coli varied from a minimum of 0 CFU/mL to a maximum of 15 CFU/mL in all samples. Malfunctioning septic systems and wildlife population appear to be the main source of E. coli contamination. Presence of E. coli in natural spring water indicates potential adverse health effects for individuals or populations exposed to this water. The fecal contaminated spring water may present an unacceptable risk to humans if it is used as raw drinking water.     

Microbiological water quality of the Mfoundi River watershed at Yaoundé, Cameroon, as inferred from indicator bacteria of fecal contamination

Using the membrane filtration technique to count total coliform (TC), fecal coliform (FC) and fecal streptococci (FS), the microbiological water quality of the Mfoundi River and four of its representative tributaries at Yaoundé, Cameroon, was assessed for human use and contact. Sampling was conducted so as to examine the potential origin of fecal contamination and how rainfall affects the measured concentrations of indicators organisms. Our results revealed that waters were not safe for human use or primary contact according to the standards for water quality established by the Word Health Organization (WHO). Indeed, these waters exhibited high concentrations of TC (Mean ± SD=5.6 × 10⁸ ± 2.5 × 10⁶ CFU/100 ml), FC (Mean ± SD=6.8 × 10⁵ ± 2.4 × 10³ CFU/100 ml) and FS (Mean ± SD=7.3 × 10⁵ ± 2.1 × 10³ CFU/100 ml) that varied with the sampling sites and points. FC/FS ratio suggested that this contamination was more from warm-blooded animals than humans and correlation analysis points to the role of rainfall as a contributing factor, which enhanced the bacterial numbers detected. We conclude that there is a great potential risk of infection for users of waters from the Mfoundi River and its tributaries at Yaoundé.     

荧光法快速测定水中粪大肠菌群

为研究荧光法测定水中粪大肠菌群的适用性,在6家实验室使用荧光法对粪大肠菌群的标准菌株和实际水样进行测定,并与多管发酵法进行比对。结果表明:6家实验室对标准菌株的监测结果均在误差范围内,实验室内相对误差为-2. 75%～1. 71%,准确度较高;对3个不同浓度实际水样进行精密度测定,实验室内相对标准偏差分别为1. 30%～3. 93%、1. 94%～4. 72%、1. 88%～4. 54%,实验室间的相对标准偏差分别为1. 14%、1. 59%、1. 72%,精密度较高;用荧光法与多管发酵法同时测定实际水样,2种方法测试结果线性相关性良好且变化趋势相同,对测试数据进行t检验,2种方法测试结果无显著差异。     

A Regional Survey of the Microbiological Water Quality along the Shoreline of the Southern California Bight

A regional survey of the microbiological water quality along the shoreline of the Southern California Bight (SCB), from Point Conception south to Ensenada, Mexico, was conducted during August, 1998, by 36 agencies under the coordination of the Southern California Coastal Water Research Project (SCCWRP). Microbiological water quality was assessed by calculating the percentage of shoreline-mile-days that exceeded bacterial indicator thresholds for total and fecal coliforms, total/fecal ratios, and enterococci. Sample sites were selected using a stratified random sampling approach, with the SCB recreational shoreline divided into six strata: high- and low-use sandy beaches, high- and low-use rocky shoreline, and perennial and ephemeral freshwater outlets. Samples were collected on a weekly basis at a total of 253 sites, beginning on August 2^nd, 1998 and continuing for five weeks. Samples were analyzed by 22 participating labs using their normal methods (multiple tube fermentation, membrane filtration, Colilert® and/or Enterolert®). All labs met testing criteria established through intercalibration exercises and quality control check samples distributed during the sampling period. Nearly 95% of the shoreline-mile days did not exceed daily and monthly bacterial indicator thresholds, demonstrating good bacteriological water quality along the SCB shoreline. Freshwater outlets, comprised mainly of storm drains, had the poorest water quality with 60% and 40% of the shoreline-miles exceeding monthly and daily thresholds, respectively. Freshwater outlets were also more likely to demonstrate exceedances by multiple indicators at a single site, and repeat exceedances at sites over the five-week period. Compared with the southern California beaches, Mexican beaches had nearly 5 times the number of exceedances for total and fecal coliforms, and nearly 8 times the number of exceedances for total/fecal ratios.     

粪大肠菌群多管发酵测定法的改进研究

对地表水和废水中粪大肠菌群目前通用的多管发酵检测方法进行优化。将水样接种至乳糖蛋白胨培养液后,在44.5℃±0.5℃培养箱中培养24h记录结果,并与优化前的方法进行对比。结果表明,改进后的方法在时间上比改进前节省了约24~48小时,但两者在结果上无统计学意义的差别。多管发酵改进法可以用于地表水和废水中粪大肠菌群的检测。     

Bacteriological Purification of the Finnish River Kymi

With its total drainage basin of 37 107 km2 and mean annual discharge of 307 m3 s-1, the River Kymi is one of the largest in Finland. Presently it receives treated domestic wastewaters of about 160 000 inhabitants through eight treatment plants and treated industrial effluents from four paper mills, two cardboard mills and one pulp mill. In the 1960s all the wastewaters were discharged untreated to the river. However, the construction of domestic wastewater treatment plants began in the 1970s and mechanical wastewater treatment became common in industry. By the end of the 1980s practically all the wastewaters discharged to the river were treated in activated sludge processes. The aim of this paper was to investigate the influence of wastewater purification on the bacteriological quality of the river during these three decades. The bacteriological quality of the river was evaluated on the basis of annual medians of fecal streptococci (FS) calculated for 15 sites on the basis of 4804 FS enumerations from the years 1964-1992. The results show that the bacteriological quality improved steadily as the number of treatment plants increased and wastewater treatment became more effective. In the beginning of the 1960s the annual FS medians in the central part of the river were typically 1000-1500 CFU/100 ml, whereas in the 1990s they had decreased to 30-40 CFU/100 ml (CFU = colony forming units). The results indicate that FS input to the river was mainly of domestic origin.     

上海市水环境中嗜肺军团菌分布状况及影响因素分析

为了解上海市水环境中嗜肺军团菌(Legionella pneumophila)的分布状况及相关影响因素,采用酶底物法于2021年11月至2022年8月对上海市地表水、泵站排水、污水厂进出水进行了嗜肺军团菌监测。结果显示:①酶底物法可作为水体中嗜肺军团菌的有效检测方法,其检测结果准确度和精密度均较好;②上海市水环境中存在不同程度的嗜肺军团菌检出,各水样的阳性检出率及检出浓度排序均为污水厂进水>泵站排水>地表水>污水厂出水;③水中嗜肺军团菌含量主要受水质指标、季节、周边环境因素的影响;④嗜肺军团菌与其他病原微生物指标存在显著相关关系;⑤随着环境水体景观娱乐功能的提升,需进一步关注各类病原微生物的环境风险。     

水质标准中指示微生物的发展及现状

饮用水病原微生物污染是公共卫生面临的主要威胁之一,微生物监测在水质监测中的必要性日益受到人们的认可。在实际工作中,一般是通过检测指示微生物间接反映病原微生物的存在。通过调研国内外各组织、机构颁布的水质标准发现,近年来,我国环境质量标准和污染物排放标准中对于指示微生物的选择有从总大肠菌群向粪大肠菌群和大肠埃希氏菌(E.coli)转变的趋势,而美国环保署、欧盟、世界卫生组织、澳大利亚国家健康与医疗研究委员会等根据最新的流行病学证据,强调了大肠埃希氏菌(E.coli)、肠球菌(Enterococci)与粪便污染的相关性更强,可用于替代大肠菌群。建议我国在后续水质标准中对微生物指标进行增补修订时,参考国外经验,形成集成多种指示微生物与多种特定病原体的监测指标体系,以更好地保护环境功能和民众健康。     

Linking on-farm dairy management practices to storm-flow fecal coliform loading for California coastal watersheds

How and where to improve water quality within an agricultural watershed requires data at a spatial scale that corresponds with individual management decision units on an agricultural operation. This is particularly true in the context of water quality regulations, such as Total Maximum Daily Loads (TMDLs), that identify agriculture as one source of non-point source pollution through larger tributary watershed scale and above and below water quality investigations. We have conducted a systems approach study of 10 coastal dairies and ranches to document fecal coliform concentration and loading to surface waters at the management decision unit scale. Water quality samples were collected on a storm event basis from loading units that included: manure management systems; gutters; storm drains; pastures; and corrals and lots. In addition, in-stream samples were collected above and below the dairy facilities and from a control watershed, managed for light grazing and without a dairy facility or human residence and corresponding septic system. Samples were analyzed for fecal coliform concentration by membrane filtration. Instantaneous discharge was measured for each collected sample. Storm runoff was also calculated using the curve number method (SCS, 1985). Results for a representative dairy as well as the entire 10 dairy data set are presented. Fecal coliform concentrations demonstrate high variability both within and between loading units. Fecal coliform concentrations for pastures range from 206 to 2,288,888 cfu/100 ml and for lots from 1,933 to 166,105,000 cfu/100 ml. Mean concentrations for pastures and lots are 121,298 (SE=62,222) and 3,155,584 (SE=1,902,713) cfu/100 ml, respectively. Fecal coliform load from units of concentrated animals and manure are significantly more than units such as pastures while storm flow amounts were significantly less. Compared with results from earlier tributary scale studies in the watershed, this systems approach has generatedwater quality data that is beneficial for management decisions because of its scale and representation of current management activities. These results are facilitating on-farm changes through the cooperative efforts of dairy managers, regulatory agency staff, and sources of technical and financial assistance.