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1 eatments yielded better control of the total coliforms.
2 total dissolved solids, and total and fecal coliforms.
3 o the inhibition of lactic acid bacteria and coliforms.
4 detecting species of Vibrio, enterococci and coliforms.
5 were taken for the presence of translocated coliforms.
6 her species of Bacteroides and gram-negative coliforms.
7 lly collected grab samples to test for total coliform and E. coli throughout supply cycles at 11 site
9 res of 10 and 20 degrees C overnight for the coliforms and AR bacteria, and buffered peptone water at
11 s study compared the abundance of FIB (Total coliforms and E. coli) and the Bacteroidales (HF183 mark
13 e community of Zambia for detection of total coliforms and Escherichia coli in drinking-water samples
14 sources, monitoring of enterococci and fecal coliform, and measurement of chemical and physical water
15 fter treatment, (2) absence of E. coli/total coliforms, and (3) establishment of a CT-factor sufficie
16 ease of Escherichia coli, enterococci, total coliforms, and dissolved chloride from solid dairy manur
17 scherichia coli accounted for 34.5% of fecal coliforms, and Enterococcus faecalis accounted for 32% o
19 were always present while staphylococci and coliform bacteria disappeared after 30 and 90 days, resp
22 aNDM-1 abundances, other AR genes (ARG), and coliform bacteria in sediments and water column samples
25 lakia (RPMP), a rare disease associated with coliform bacterial infection of the kidney and character
31 m water treatment plants revealed that fecal coliform contamination occurred both before and after tr
33 eriologic standards during harvest and fecal coliform counts in water samples were within acceptable
35 correlations with each other and with total coliforms, E. coli, enterococci, and biochemical oxygen
36 cultured facultative anaerobes such as fecal coliforms, Escherichia coli, or enterococci have been us
39 repeated freezing and thawing, on indigenous coliforms, fecal streptococci, and antibiotic-resistant
44 ssing the association between thermotolerant coliforms in drinking water and diarrhea: an analysis of
45 in India, showed a complete inactivation of coliforms in the discharged effluent (Mean Log removal V
47 eir etiologic agents and a substantial fecal coliform load can enter surface, drinking and recreation
49 , biochemical oxygen demand (BOD), and fecal coliform pollution from human excreta for 108 LMICs.
50 A negative correlation was found between coliform removal and estrogen concentration in nonaugmen
52 range) BOD, nitrogen, phosphorus, and fecal coliforms, respectively, are removed by existing sanitat
53 cent Escherichia coli target, as a surrogate coliform, to catholyte where a rapid kill rate was obser
54 red in seawater (Enterococcus species, fecal coliforms, total coliforms) were strongly associated wit
55 , particularly as measured by thermotolerant coliform (TTC) bacteria, a WHO-approved indicator of dri
56 esence of Escherichia coli or thermotolerant coliforms (TTC) were included provided they associated r
57 rinking water was assayed for thermotolerant coliforms (TTC), an indicator of faecal contamination.
58 at the levels of aerobic plate counts, total coliform, water activity, moisture contents, total volat
60 Enterococcus species, fecal coliforms, total coliforms) were strongly associated with incident illnes
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