Luli G W, Talnagi J W, Strohl W R, Pfister R M
Appl Environ Microbiol. 1983 Oct;46(4):846-54. doi: 10.1128/aem.46.4.846-854.1983.
Hexavalent chromium [Cr(VI)] is a known carcinogen and mutagen; however, the actual mechanisms of Cr toxicity are unknown. Two approaches were used to isolate Cr(VI)-resistant bacteria from metal-contaminated river sediments. Diluted sediments were plated directly onto a peptone-yeast extract (PYE) medium containing 0 to 100 micrograms of Cr(VI) ml-1. Approximately 8.4 x 10(5) CFU g-1 were recovered on 0 microgram of Cr(VI) ml-1, whereas 4.0 x 10(2) CFU g-1 were recovered on PYE plus 100 micrograms of Cr(VI) ml-1. Alternatively, continuous culture enrichment techniques were employed using PYE and 100 micrograms Cr(VI) ml-1 input at dilution rates of 0.02 and 0.10 h-1. After six residence periods, 10(9) CFU were recovered on PYE agar containing 0 microgram of Cr(VI) ml-1 and 10(7) CFU on PYE agar plus 100 micrograms of Cr(VI) ml-1. Of 89 isolates obtained by direct plating onto PYE, 47% were resistant to 100 micrograms of Cr(VI) ml-1, and 29% were resistant to 250 micrograms of Cr(VI) ml-1. When the same isolates were plated onto PYE containing Cr(III), 88% were resistant to 100 micrograms ml-1 but only 2% were resistant to 250 micrograms ml-1. Cr, Co, Sb, and Zn were found in significantly higher concentrations at an industry-related contaminated site than at a site 11 km downstream. Total Cr in the sediments at the contaminated site averaged 586 micrograms (dry weight) g-1, and the downstream site averaged 71 micrograms (dry weight) g-1. The Cr recovered from acid-digested Ottawa River sediment samples was predominantly hexavalent. Five acid digestion procedures followed by atomic absorption spectroscopy were compared and found to be 30 to 70% efficient for recovery of Cr relative to neutron activation analysis. A population of aerobic, heterotrophic bacteria was recovered from sediments containing elevated levels of Cr.(ABSTRACT TRUNCATED AT 250 WORDS)
六价铬[Cr(VI)]是一种已知的致癌物和诱变剂;然而,铬毒性的实际机制尚不清楚。采用两种方法从受金属污染的河流沉积物中分离出抗Cr(VI)细菌。将稀释后的沉积物直接接种到含有0至100微克Cr(VI)/毫升的蛋白胨酵母提取物(PYE)培养基上。在0微克Cr(VI)/毫升的培养基上回收了约8.4×10⁵CFU/克,而在添加100微克Cr(VI)/毫升的PYE培养基上回收了4.0×10²CFU/克。或者,采用连续培养富集技术,使用PYE和100微克Cr(VI)/毫升的输入量,稀释率分别为0.02和0.10小时⁻¹。经过六个停留期后,在含有0微克Cr(VI)/毫升的PYE琼脂上回收了10⁹CFU,在添加100微克Cr(VI)/毫升的PYE琼脂上回收了10⁷CFU。在直接接种到PYE上获得的89株分离物中,47%对100微克Cr(VI)/毫升有抗性,29%对250微克Cr(VI)/毫升有抗性。当将相同的分离物接种到含有Cr(III)的PYE上时,88%对100微克/毫升有抗性,但只有2%对250微克/毫升有抗性。在一个与工业相关的污染场地中,发现铬、钴、锑和锌的浓度明显高于下游11公里处的场地。污染场地沉积物中的总铬平均为586微克(干重)/克,下游场地平均为71微克(干重)/克。从渥太华河沉积物酸消解样品中回收的铬主要是六价的。比较了五种酸消解程序并结合原子吸收光谱法,发现相对于中子活化分析,铬的回收率为30%至70%。从铬含量较高的沉积物中回收了一群需氧异养细菌。(摘要截于250字)