Wielinga B, Mizuba M M, Hansel C M, Fendorf S
Department of Geological and Environmental Sciences, Stanford University, Stanford, California 94305-2115, USA.
Environ Sci Technol. 2001 Feb 1;35(3):522-7. doi: 10.1021/es001457b.
Chromate is a priority pollutant within the U.S. and many other countries, the hazard of which can be mitigated by reduction to the trivalent form of chromium. Here we elucidate the reduction of Cr(VI) to Cr(III) via a closely coupled, biotic-abiotic reductive pathway under iron-reducing conditions. Injection of chromate into stirred-flow reactors containing Shewanella alga strain BrY and iron (hydr)oxides of varying stabilities results in complete reduction to Cr(III). The maximum sustainable Cr(VI) reduction rate was 5.5 micrograms CrVI.mg-cell-1.h-1 within ferric (hydr)oxide suspensions (surface area 10 m2). In iron limited systems (having HEPES as a buffer), iron was cycled suggesting it acts in a catalytic-type manner for the bacterial reduction of Cr(VI). BrY also reduced Cr(VI) directly; however, the rate of direct (enzymatic) reduction is considerably slower than by Fe(II)(aq) and is inhibited within 20 h due to chromate toxicity. Thus, dissimilatory iron reduction may provide a primary pathway for the sequestration and detoxification of chromate in anaerobic soils and water.
铬酸盐是美国和许多其他国家的优先污染物,通过将其还原为三价铬形式可以减轻其危害。在此,我们阐明了在铁还原条件下,通过紧密耦合的生物 - 非生物还原途径将Cr(VI)还原为Cr(III)的过程。将铬酸盐注入含有希瓦氏菌属藻类菌株BrY和不同稳定性的铁(氢)氧化物的搅拌流反应器中,会导致其完全还原为Cr(III)。在铁(氢)氧化物悬浮液(表面积为10平方米)中,最大可持续Cr(VI)还原速率为5.5微克CrVI·毫克细胞⁻¹·小时⁻¹。在铁受限系统(以HEPES作为缓冲剂)中,铁发生循环,这表明它以催化方式作用于细菌对Cr(VI)的还原。BrY也能直接还原Cr(VI);然而,直接(酶促)还原的速率比通过Fe(II)(aq)还原的速率慢得多,并且由于铬酸盐毒性,在20小时内受到抑制。因此,异化铁还原可能为厌氧土壤和水中铬酸盐的螯合和解毒提供主要途径。