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      Urbanization Impacts the Physicochemical Characteristics and Abundance of Fecal Markers and Bacterial Pathogens in Surface Water

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          Abstract

          Urbanization is increasing worldwide and is happening at a rapid rate in China in line with economic development. Urbanization can lead to major changes in freshwater environments through multiple chemical and microbial contaminants. We assessed the impact of urbanization on physicochemical characteristics and microbial loading in canals in Suzhou, a city that has experienced rapid urbanization in recent decades. Nine sampling locations covering three urban intensity classes (high, medium and low) in Suzhou were selected for field studies and three locations in Huangshan (natural reserve) were included as pristine control locations. Water samples were collected for physicochemical, microbiological and molecular analyses. Compared to medium and low urbanization sites, there were statistically significant higher levels of nutrients and total and thermotolerant coliforms (or fecal coliforms) in highly urbanized locations. The effect of urbanization was also apparent in the abundances of human-associated fecal markers and bacterial pathogens in water samples from highly urbanized locations. These results correlated well with land use types and anthropogenic activities at the sampling sites. The overall results indicate that urbanization negatively impacts water quality, providing high levels of nutrients and a microbial load that includes fecal markers and pathogens.

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          A new medium for the enumeration and subculture of bacteria from potable water.

          Plate count agar is presently the recommended medium for the standard bacterial plate count (35 degrees C, 48-h incubation) of water and wastewater. However, plate count agar does not permit the growth of many bacteria that may be present in treated potable water supplies. A new medium was developed for use in heterotrophic plate count analyses and for subculture of bacteria isolated from potable water samples. The new medium, designated R2A, contains 0.5 g of yeast extract, 0.5 g of Difco Proteose Peptone no. 3 (Difco Laboratories), 0.5 g of Casamino Acids (Difco), 0.5 g of glucose, 0.5 g of soluble starch, 0.3 g of K2HPO4, 0.05 g of MgSO4 X 7H2O, 0.3 g of sodium pyruvate, and 15 g of agar per liter of laboratory quality water. Adjust the pH to 7.2 with crystalline K2HPO4 or KH2PO4 and sterilize at 121 degrees C for 15 min. Results from parallel studies with spread, membrane filter, and pour plate procedures showed that R2A medium yielded significantly higher bacterial counts than did plate count agar. Studies of the effect of incubation temperature showed that the magnitude of the count was inversely proportional to the incubation temperature. Longer incubation time, up to 14 days, yielded higher counts and increased detection of pigmented bacteria. Maximal bacterial counts were obtained after incubation at 20 degrees C for 14 days. As a tool to monitor heterotrophic bacterial populations in water treatment processes and in treated distribution water, R2A spread or membrane filter plates incubated at 28 degrees C for 5 to 7 days is recommended.(ABSTRACT TRUNCATED AT 250 WORDS)
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            City clusters in China: air and surface water pollution

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                Author and article information

                Journal
                Int J Environ Res Public Health
                Int J Environ Res Public Health
                ijerph
                International Journal of Environmental Research and Public Health
                MDPI
                1661-7827
                1660-4601
                16 May 2019
                May 2019
                : 16
                : 10
                : 1739
                Affiliations
                [1 ]Department of Biological Sciences, Xi’an Jiaotong-Liverpool University, Suzhou 215123, China; Tianma.Yuan@ 123456xjtlu.edu.cn (T.Y.); Kumar.Kiran@ 123456xjtlu.edu.cn (K.K.V.)
                [2 ]School of Biological Sciences, University of Canterbury, Christchurch 8140, New Zealand; jdtonkin@ 123456gmail.com
                [3 ]Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China; jjwang@ 123456niglas.ac.cn
                [4 ]Futurepolis LLC, Suzhou 215021, China; jinglu.lyu@ 123456gmail.com
                [5 ]Institute of Integrative Biology, University of Liverpool, Liverpool L69 3BX, UK; zimeng.zhang@ 123456liverpool.ac.uk
                [6 ]Department of Health and Environmental Sciences, Xi’an Jiaotong-Liverpool University, Suzhou 215123, China; Yixin.Zhang@ 123456xjtlu.edu.cn
                [7 ]Microbiology Research Group, Institute of Integrative Biology, University of Liverpool, Liverpool L69 7ZB, UK; aj55m@ 123456liverpool.ac.uk
                Author notes
                [* ]Correspondence: Sekar.Raju@ 123456xjtlu.edu.cn ; Tel.: +86-512-8816-1656
                Author information
                https://orcid.org/0000-0002-6053-291X
                https://orcid.org/0000-0003-1546-4150
                https://orcid.org/0000-0002-1182-9004
                Article
                ijerph-16-01739
                10.3390/ijerph16101739
                6572354
                31100947
                bf40f801-16e5-45d0-a98f-a8a44e57e419
                © 2019 by the authors.

                Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license ( http://creativecommons.org/licenses/by/4.0/).

                History
                : 02 April 2019
                : 10 May 2019
                Categories
                Article

                Public health
                urbanization,water quality,nutrients,microbial contaminations,fecal markers,pathogens,suzhou canals

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