Background: Because of the concern for infection risk, use of sterile water has been recommended in the water bottle for endoscopic equipment, although studies evaluating prevalence of contamination of the water bottle with clinical outcomes have not been performed.
Methods: Over a 12-week period in three endoscopy rooms at a university teaching hospital, the water bottles were filled on a weekly schedule with either sterile (one room) or tap water. The water bottles were sterilized on a weekly basis with an automated endoscope washer. At the end of each week, an aliquot of the remaining water was transferred to a sterile container, and quantitative cultures for aerobic and facultative anaerobic bacteria were performed by use of a 0.01 ml calibrated loop according to standard protocols. Cultures were performed in a blinded fashion without knowledge of the water source. Follow-up was performed on all patients within 2 weeks of the procedure to determine any potential infectious complications.
Results: During the study period, 437 procedures were performed (203 endoscopy, 68 colonoscopy, 38 sigmoidoscopy, 128 endoscopic retrograde cholangiopancreatography). Of a total of 36 cultures (12 sterile), the results of nine (25%) were positive, including three bottles where sterile water was used. Bacterial isolates included five Flavobacterium sp., four Acinetobacter sp., two Pseudomonas sp., and one Stenotrophomonas maltophilia. Colony counts ranged from 900 to more than 10,000 per ml. On follow-up no patient had development of a clinical infection from any of these organisms.
Conclusions: Bacterial growth in the water bottle was infrequent, consisted predominantly of nonpathogenic organisms, and was not associated with clinical complications. Our pilot study suggests that the use of tap water as compared with sterile water may be practical as well as provide cost savings.
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http://dx.doi.org/10.1016/s0196-6553(96)90031-0 | DOI Listing |
Plant Physiol Biochem
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Universidade do Oeste Paulista (UNOESTE), Presidente Prudente, SP, Brazil.
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January 2025
State Key Laboratory of Pollution Control and Resource Reuse, School of Environment, Nanjing University, Nanjing, Jiangsu 210023, China. Electronic address:
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January 2025
State Key Laboratory of Geohazard Prevention and Geoenvironment Protection (Chengdu University of Technology), 1#, Dongsanlu, Erxianqiao, Chengdu 610059, Sichuan, PR China; State Environmental Protection Key Laboratory of Synergetic Control and Joint Remediation for Soil & Water Pollution (Chengdu University of Technology), 1#, Dongsanlu, Erxianqiao, Chengdu 610059, Sichuan, PR China. Electronic address:
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January 2025
State Key Laboratory of Environmental Aquatic Chemistry, Research Center for Eco- Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; University of Chinese Academy of Sciences, Beijing 100049, China. Electronic address:
The flow through the grit chamber is non-biochemically treated wastewater, which contains microorganisms mainly from the source of wastewater generation. There are limited reports on aerosol particles generated by grit chambers compared with those produced by biochemical treatment tanks. This study analyzed the fugitive characteristics of aerosol particles produced in grit chambers at nine wastewater treatment plants in three regions of China.
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Faculty of Geosciences and Civil Engineering, Kanazawa University, Kanazawa 920-1192, Japan; Center for Infectious Disease Education and Research (CiDER), Osaka University, 565-0871, Japan. Electronic address:
Treated effluent of wastewater treatment plants (WWTPs) are major sources of extracellular antimicrobial resistance genes (eARGs) into aquatic environments. This study aimed to clarify the fate and origins of eARGs from influent to treated effluent at a full-scale WWTP. The compositions of eARG and intracellular ARG (iARG) were acquired via shotgun metagenomic sequencing in influent wastewater, activated sludge, and treated effluent of the target WWTP, where identical wastewater was treated by conventional activated sludge (CAS) and membrane bioreactor (MBR) processes.
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