Komlos John, Kukkadapu Ravi K, Zachara John M, Jaffé Peter R
Department of Civil and Environmental Engineering, Princeton University, Princeton, NJ 08544, USA.
Water Res. 2007 Jul;41(13):2996-3004. doi: 10.1016/j.watres.2007.03.019. Epub 2007 Apr 27.
Sediment containing a mixture of iron (Fe)-phases, including Fe-oxides (mostly Al-goethite) and Fe-silicates (illites and vermiculite) was bioreduced in a long-term flow through column experiment followed by re-oxidation with dissolved oxygen. The objective of this study was (a) to determine the nature of the re-oxidized Fe(III), and (b) to determine how redox cycling of Fe would affect subsequent Fe(III)-bioavailability. In addition, the effect of Mn on Fe(III) reduction was explored.(57)Fe-Mössbauer spectroscopy measurements showed that biostimulation resulted in partial reduction (20%) of silicate Fe(III) to silicate Fe(II) while the reduction of goethite was negligible. Furthermore, the reduction of Fe in the sediment was uniform throughout the column. When, after biostimulation, 3900 pore volumes of a solution containing dissolved oxygen was pumped through the column over a period of 81 days, approximately 46% of the reduced silicate Fe(II) was re-oxidized to silicate Fe(III). The Mössbauer spectra of the re-oxidized sample were similar to that of pristine sediment implying that Fe-mineralogy of the re-oxidized sediment was mineralogically similar to that of the pristine sediment. In accordance to this, batch experiments showed that Fe(III) reduction occurred at a similar rate although time until Fe(II) buildup started was longer in the pristine sediment than re-oxidized sediment under identical seeding conditions. This was attributed to oxidized Mn that acted as a temporary redox buffer in the pristine sediment. The oxidized Mn was transformed to Mn(II) during bioreduction but, unlike silicate Fe(II), was not re-oxidized when exposed to oxygen.
含有铁(Fe)相混合物的沉积物,包括铁氧化物(主要是铝针铁矿)和铁硅酸盐(伊利石和蛭石),在长期的流通柱实验中进行生物还原,随后用溶解氧进行再氧化。本研究的目的是:(a)确定再氧化的Fe(III)的性质,以及(b)确定铁的氧化还原循环如何影响随后的Fe(III)生物有效性。此外,还探讨了锰对Fe(III)还原的影响。(57)Fe-穆斯堡尔光谱测量表明,生物刺激导致硅酸盐Fe(III)部分还原(20%)为硅酸盐Fe(II),而针铁矿的还原可忽略不计。此外,沉积物中铁的还原在整个柱中是均匀的。在生物刺激后,当在81天的时间内将含有溶解氧的溶液的3900个孔隙体积泵入柱中时,大约46%的还原硅酸盐Fe(II)被再氧化为硅酸盐Fe(III)。再氧化样品的穆斯堡尔光谱与原始沉积物的光谱相似,这意味着再氧化沉积物的铁矿物学在矿物学上与原始沉积物相似。据此,批量实验表明,尽管在相同的接种条件下,原始沉积物中开始积累Fe(II)的时间比再氧化沉积物长,但Fe(III)的还原速率相似。这归因于氧化态的锰,它在原始沉积物中充当临时的氧化还原缓冲剂。氧化态的锰在生物还原过程中转化为Mn(II),但与硅酸盐Fe(II)不同,当暴露于氧气时它不会再被氧化。