Biology Department, University of Massachusetts at Boston, 02125, Boston, Massachusetts, USA.
Microb Ecol. 1989 Sep;18(2):135-46. doi: 10.1007/BF02030122.
The effect of varying salinity on phenanthrene and glutamate mineralization was examined in sediments along a natural salinity gradient in an urban tidal river. Mineralization was measured by trapping(14)CO2 from sediment slurries dosed with trace levels of [(14)C]phenanthrene or [(14)C]glutamate. Sediments from three sites representing three salinity regimes (0, 15, and 30%.) were mixed with filtered column water from each site. Ambient phenanthrene concentrations were also determined to calculate phenanthrene mineralization rates. Rates of phenanthrene mineralization related significantly to increasing salinity along the transect as determined by linear regression analysis. Rates ranged from 1 ng/hour/g dry sediment at the freshwater site to > 16 ng/hour/g dry sediment at the 30‰ salinity site. Glutamate mineralization also increased from the freshwater to the marine site; however, the relationship to salinity was not statistically significant.To examine the effect of salinity on mineralizing activities, individual sediments were mixed with filtered water of the other two sites. Slurries were also made with artificial seawater composed of 0, 15, or 30 g NaCl/ liter to substitute for overlying water. Rates of phenanthrene mineralization in the 0‰ ambient salinity sediments were not affected by higher salinity waters. Activities in the 15 and 30‰ ambient salinity sediments, however, were significantly inhibited by incubation with 0‰ salinity water. The inhibition, in large part, appears to be due to the decreased NaCl concentration of the water phase. Glutamate mineralization was affected in a similar manner, but not as dramatically as phenanthrene mineralization. The results suggest that phenanthrene degraders in low salinity estuarine sediments subject to salt water intrusion are tolerant to a wide range of salinities but phenanthrene degradation in brackish waters is mainly a function of obligate marine microorganisms.
在一条城市潮汐河的自然盐度梯度上,研究了盐度变化对菲和谷氨酸矿化的影响。通过从用痕量 [(14)C]菲或 [(14)C]谷氨酸处理的沉积物悬浮液中捕获 (14)CO2 来测量矿化作用。从代表三个盐度区(0、15 和 30%)的三个地点采集沉积物,并将每个地点的过滤柱水与沉积物混合。还测定了环境中菲的浓度,以计算菲的矿化率。通过线性回归分析,菲的矿化率与沿剖面的盐度呈显著正相关。速率范围从淡水点的 1 ng/小时/克干沉积物到 30‰盐度点的 >16 ng/小时/克干沉积物。谷氨酸矿化也从淡水点到海洋点增加;然而,与盐度的关系没有统计学意义。为了研究盐度对矿化作用的影响,将单独的沉积物与其他两个地点的过滤水混合。还使用由 0、15 或 30 g NaCl/升组成的人工海水制成悬浮液,以替代上层水。在 0‰环境盐度沉积物中,菲的矿化率不受较高盐度水的影响。然而,在 15 和 30‰环境盐度沉积物中的活性,在用 0‰盐度水孵育时受到显著抑制。这种抑制在很大程度上似乎是由于水相中的 NaCl 浓度降低。谷氨酸矿化也受到类似的影响,但不如菲矿化那么显著。结果表明,在受到盐水入侵的低盐度河口沉积物中,菲降解菌对广泛的盐度具有耐受性,但在半咸水中,菲的降解主要是专性海洋微生物的功能。