Laboratory of Soil Microbiology, Department of Soil, Crop and Atmospheric Sciences, Cornell University, 14853, Ithaca, New York, USA.
Microb Ecol. 1990 Dec;20(1):231-44. doi: 10.1007/BF02543879.
The sizes of the populations of individual bacterial species diminished following their addition to water from lakes with different trophic levels at temperatures of 5, 10, 15, and 30°C. Some species persisted after their initial reduction in cell numbers, but others were undetectable after 3 to 15 days. The decline of these introduced bacteria was not a result of their inoculation at higher densities than are found in nature. The death of most of the test species was not the result of starvation, abiotic factors, bdellovibrios, or bacteriophages. Despite the presence of lytic bacteria, the lake water did not have lytic activity against the test species. Protozoan predation was a significant factor in the fall in bacterial population sizes because protozoa increased in numbers as the bacterial density fell, the suppression of protozoa led to the elimination or delay of the decline of the bacteria, and the addition of protozoa to lake water in which indigenous protozoa were suppressed produced the same pattern of bacterial elimination as in untreated lake water.
在 5、10、15 和 30°C 的温度下,将不同营养水平湖泊水中的单个细菌种群添加到水中后,其种群大小会减小。一些物种在细胞数量最初减少后仍能存活,但其他物种在 3 至 15 天后就无法检测到了。这些引入的细菌的减少并不是由于它们的接种密度高于自然界中发现的密度。大多数测试物种的死亡不是由于饥饿、非生物因素、蛭弧菌或噬菌体造成的。尽管存在裂解细菌,但湖水对测试物种没有裂解活性。原生动物捕食是细菌种群数量下降的一个重要因素,因为随着细菌密度的下降,原生动物数量增加,抑制原生动物会导致细菌的消除或延迟下降,并且向抑制土著原生动物的湖水中添加原生动物会产生与未处理湖水相同的细菌消除模式。