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首页> 外文期刊>Applied and Environmental Microbiology >Aerobic and anaerobic degradation and mineralization of 14C-chitin by water column and sediment inocula of the York River estuary, Virginia.
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Aerobic and anaerobic degradation and mineralization of 14C-chitin by water column and sediment inocula of the York River estuary, Virginia.

机译:弗吉尼亚约克河河口水柱和沉积物接种物对14C-甲壳素的需氧和厌氧降解及矿化作用。

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摘要

Potential rates of chitin degradation (Cd) and mineralization (Cm) by estuarine water and sediment bacteria were measured as a function of inoculum source, temperature, and oxygen condition. In the water column inoculum, 88 to 93% of the particulate chitin was mineralized to CO2 with no apparent lag between degradation and mineralization. No measurable dissolved pool of radiolabel was found in the water column. For the sediment inocula, 70 to 90% of the chitin was degraded while only 55 to 65% was mineralized to CO2. 14C label recoveries in the dissolved pool were 19 to 21% for sand, 17 to 24% in aerobic mud, and 12 to 21% for the anaerobic mud. This uncoupling between degradation and mineralization occurred in all sediment inocula. More than 98% of the initial 14C-chitin was recovered in the three measured fractions. The highest Cd and Cm values, 30 and 27% day-1, occurred in the water column inoculum at 25 degrees C. The lowest Cd and Cm values were found in the aerobic and anaerobic mud inocula incubated at 15 degrees C. Significant differences in Cd and Cm values among water column and sediment inocula as well as between temperature treatments were evident. An increased incubation temperature resulted in shorter lag times before the onset of chitinoclastic bacterial growth, degradation, and mineralization and resulted in apparent Q10 values of 1.1 for water and 1.3 to 2.1 for sediment inocula. It is clear that chitin degradation and mineralization occur rapidly in the estuary and that water column bacteria may be more important in this process than previously acknowledged.
机译:测量了河口水和沉积物细菌的几丁质降解(Cd)和矿化(Cm)的潜在速率与接种源,温度和氧气条件的关系。在水柱接种物中,88%至93%的几丁质颗粒被矿化为CO2,在降解和矿化之间没有明显的滞后。在水柱中未发现可测量的放射性标记物溶解池。对于沉积物接种,几丁质的降解率为70%至90%,而矿物质中只有55%至65%转化为CO2。溶解池中14 C标签的回收率:沙子为19%至21%,好氧泥为17%至24%,厌氧泥为12%至21%。降解和矿化之间的这种解耦发生在所有沉积物接种物中。在三个测得的馏分中回收了超过98%的初始14C-几丁质。第一天的Cd和Cm值最高,分别为30%和27%,出现在25摄氏度的水柱接种物中。最低的Cd和Cm值出现在15摄氏度的需氧和厌氧污泥接种物中。水柱和沉积物接种物之间以及温度处理之间的Cd和Cm值很明显。孵化温度的升高导致甲壳破伤性细菌开始生长,降解和矿化之前的滞后时间缩短,并且水的表观Q10值为1.1,沉积物接种的Q10值为1.3至2.1。显然,甲壳质的降解和矿化作用在河口迅速发生,在这一过程中水柱细菌可能比以前公认的更为重要。

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