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本文引用的文献

1
Modification of membrane diffusion chambers for deep-water studies.深水研究用膜扩散室的改良。
Appl Environ Microbiol. 1977 Jan;33(1):207-10. doi: 10.1128/aem.33.1.207-210.1977.
2
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Appl Environ Microbiol. 1977 Jan;33(1):114-22. doi: 10.1128/aem.33.1.114-122.1977.
3
Replica plating and indirect selection of bacterial mutants.细菌突变体的影印培养和间接筛选
J Bacteriol. 1952 Mar;63(3):399-406. doi: 10.1128/jb.63.3.399-406.1952.
4
Survival of coliform bacteria in natural waters: field and laboratory studies with membrane-filter chambers.天然水体中大肠菌群细菌的存活:使用膜滤室的现场和实验室研究。
Appl Microbiol. 1972 Nov;24(5):805-11. doi: 10.1128/am.24.5.805-811.1972.
5
Plasmid-associated enterotoxin production in a strain of Escherichia coli isolated from humans.从人类分离出的一株大肠杆菌中质粒相关肠毒素的产生
Infect Immun. 1972 Apr;5(4):622-4. doi: 10.1128/iai.5.4.622-624.1972.
6
Effect of physical parameters on the in situ survival of Escherichia coli MC-6 in an estuarine environment.物理参数对河口环境中大肠杆菌MC-6原位存活的影响。
Appl Microbiol. 1975 Nov;30(5):800-6. doi: 10.1128/am.30.5.800-806.1975.
7
Recalibrated linkage map of Escherichia coli K-12.大肠杆菌K-12的重新校准连锁图谱。
Bacteriol Rev. 1976 Mar;40(1):116-67. doi: 10.1128/br.40.1.116-167.1976.
8
Reduced synthesis of beta-galactosidase in Escherichia coli infected with phage phi X 174.感染噬菌体φX 174的大肠杆菌中β-半乳糖苷酶合成减少。
Can J Microbiol. 1977 Aug;23(8):1069-77. doi: 10.1139/m77-160.
9
Survival of human enteric and other sewage microorganisms under simulated deep-sea conditions.人类肠道及其他污水微生物在模拟深海条件下的存活情况。
Appl Microbiol. 1975 Aug;30(2):309-18. doi: 10.1128/am.30.2.309-318.1975.

热应激反应器流出水中大肠杆菌的乳糖变异性

Lactose variability of Escherichia coli in thermally stressed reactor effluent waters.

作者信息

Kasweck K L, Fliermans C B

出版信息

Appl Environ Microbiol. 1978 Nov;36(5):739-46. doi: 10.1128/aem.36.5.739-746.1978.

DOI:10.1128/aem.36.5.739-746.1978
PMID:365111
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC243131/
Abstract

Lactose-utilizing and nalidixic acid-resistant populations of Escherichia coli, having an optimum growth temperature of 37 degrees C, were placed in modified diffusion chambers. The chambers were submerged in the epilimnion and hypolimnion of a 1,100-hectare lake (Par Pond) which receives cooling water from a nuclear production reactor. Control chambers were placed in a deep-water reservoir and a Flowing-Streams Laboratory, both of which had comparable temperatures to Par Pond. The populations of E. coli were sampled regularly for up to 3 weeks. Viability of the bacteria was determined by dilution plating to nutrient agar followed by replicate plating onto selective medium to determine lactose utilization and nalidixic acid sensitivity. Initial populations of E. coli were lactose positive but changed to lactose negative in Par Pond when the reactor was operating (i.e., cooling water from the heat exchangers was being discharged to the lake). This alteration occurred most rapidly in the chambers closest to the cooling-water discharge point. Such changes did not occur in a deep-water reservoir, in Par Pond when the reactor was not operating, or in the Flowing-Streams Laboratory. The nalidixic acid-resistant characteristic remained stable regardless of the chambers' placement or reactor operations. Although the reasons for such alterations are unclear, it appears that lactose-negative populations of E. coli are selected for in these reactor effluent waters. The loss of the lactose characteristic prevents the recognition and identification of E. coli in this cooling lake (when the reactor is operating) and may prevent the assessment of water quality based on coliform recognition.

摘要

将最适生长温度为37摄氏度的利用乳糖且耐萘啶酸的大肠杆菌菌群置于改良的扩散室中。这些扩散室被浸没在一个1100公顷湖泊(帕尔池塘)的上层湖温水层和下层湖冷水层中,该湖泊接收来自一座核生产反应堆的冷却水。对照扩散室被放置在一个深水水库和一个流水实验室中,这两个地方的温度都与帕尔池塘相当。对大肠杆菌菌群进行了长达3周的定期采样。通过将细菌稀释接种到营养琼脂上,然后再重复接种到选择性培养基上来测定乳糖利用情况和萘啶酸敏感性,从而确定细菌的活力。大肠杆菌的初始菌群是乳糖阳性的,但当反应堆运行时(即热交换器的冷却水排入湖泊),在帕尔池塘中变为乳糖阴性。这种变化在最靠近冷却水排放点的扩散室中发生得最快。在深水水库中、反应堆不运行时的帕尔池塘中以及流水实验室中都没有发生这种变化。无论扩散室的放置位置或反应堆的运行情况如何,耐萘啶酸特性都保持稳定。尽管这种变化的原因尚不清楚,但似乎在这些反应堆废水水域中选择了乳糖阴性的大肠杆菌菌群。乳糖特性的丧失妨碍了在这个冷却湖(反应堆运行时)中对大肠杆菌的识别和鉴定,并且可能妨碍基于大肠菌群识别的水质评估。