Dipartimento di Biologia Ambientale, Università di Siena, via P. A. Mattioli, 4, I-53100 Siena, and Laboratorio Chimico d'Igiene e Profilassi, I-19100, La Spezia, Italy.
Appl Environ Microbiol. 1993 Aug;59(8):2479-85. doi: 10.1128/aem.59.8.2479-2485.1993.
Two strains of Desulfovibrio desulfuricans, one known to synthesize monomethylmercury from ionic mercury, were grown to determine methylmercury toxicity and for comparison with an anaerobic strain of Clostridium pasteurianum, a H(2) producer, and with the broad-spectrum mercury-resistant Pseudomonas putida strain FB-1, capable of degrading 1 mug of methylmercury to methane and elemental mercury in 2 h. The CH(3)HgCl resistance of D. desulfuricans strains was 10 times that of P. putida FB-1 and 100 times that of C. pasteurianum. The methylmercury resistance of D. desulfuricans was related to the disappearance of methylmercury from cultures by transformation to dimethylmercury, metacinnabar, methane, and traces of ionic mercury. During a 15-day experiment the kinetics of the two volatile compounds dimethylmercury [(CH(3))(2)Hg] and methane were monitored in the liquid by a specific new technique with purge-and-trap gas chromatography in line with Fourier transform infrared spectroscopy and in the headspace by gas chromatography with flame ionization detection. Insoluble metacinnabar (cubic HgS) of biological origin was detected by X-ray diffractometry in the gray precipitate from the insoluble residue of the pellet of a 1-liter culture spiked with 100 mg of CH(3)HgCl. This was compared with a 1-liter culture of D. desulfuricans LS spiked with 100 mg of HgCl(2). In a further experiment, it was demonstrated that insoluble, decomposable, white dimethylmercury sulfide [(CH(3)Hg)(2)S] formed instantly in the reaction of methylmercury with hydrogen sulfide. This organomercurial was extracted with chloroform and identified by gas chromatography in line with mass spectrometry. The D. desulfuricans strains were resistant to high concentrations of methylmercury because they produced insoluble dimethylmercury sulfide, which slowly decomposed under anaerobic conditions to metacinnabar and volatilized to dimethylmercury and methane between pHs 6.2 and 6.5 for high (4.5-g . liter) or low (0.09-g . liter) sulfate contents. Methane was produced from CH(3)HgCl at a lower rate than by the broad-spectrum Hg-resistant P. putida strain FB-1.
两种脱硫弧菌菌株,一种已知能将离子汞合成为甲基汞,被培养以确定甲基汞的毒性,并与产氢的厌氧梭菌菌株巴氏梭菌(Clostridium pasteurianum)和广谱抗汞假单胞菌 FB-1 进行比较,后者能在 2 小时内将 1 微克甲基汞降解为甲烷和元素汞。脱硫弧菌菌株对 CH3HgCl 的抗性是广谱抗汞假单胞菌 FB-1 的 10 倍,是巴氏梭菌的 100 倍。脱硫弧菌对甲基汞的抗性与甲基汞向二甲基汞、辰砂、甲烷和痕量离子汞转化而从培养物中消失有关。在为期 15 天的实验中,通过一种特殊的新技术,用吹扫捕集气相色谱法与傅里叶变换红外光谱法在线监测了两种挥发性化合物二甲基汞[(CH3)2Hg]和甲烷在液体中的动力学,并用火焰电离检测的气相色谱法监测了顶空的动力学。用 X 射线衍射法在 1 升培养物的不溶性沉淀的灰色沉淀中检测到生物来源的不溶性辰砂(立方 HgS),该培养物中加入了 100 毫克 CH3HgCl。这与 1 升加入了 100 毫克 HgCl2的脱硫弧菌 LS 培养物进行了比较。在进一步的实验中,证明了在甲基汞与硫化氢的反应中,立即形成了不溶性、可分解的白色二甲基汞硫化物[(CH3)2HgS]。这种有机汞通过氯仿提取,并通过气相色谱与质谱联用进行鉴定。脱硫弧菌菌株对高浓度的甲基汞具有抗性,因为它们产生不溶性的二甲基汞硫化物,该硫化物在厌氧条件下缓慢分解为辰砂,并在 pH 值为 6.2 到 6.5 之间挥发为二甲基汞和甲烷,硫酸盐含量高(4.5 克/升)或低(0.09 克/升)。与广谱抗汞假单胞菌 FB-1 相比,CH3HgCl 生成甲烷的速度较慢。