Microbial regeneration and respiration of Fe(III) outcompetes sulphate respiration in ferruginous, high-sulphate oligotrophic ecosystems

Author(s):  
Ingrid Steenbergen ◽  
Roman Špánek ◽  
Dagmara Sirova ◽  
Jakub Borovec ◽  
Daniel Petrash

<div> </div><div> <p>In anoxic lacustrine systems, at low-sulphate concentrations, sulphidisation acts as a crucial pathway driving the reductive dissolution of amorphous and nanocrystalline Fe-(oxyhydr)oxides in the presence of dissolved organic matter. The cycling of intermediate sulphur through a disproportionation reaction with the available Fe(III) stocks supports a continued intermediate sulphur-based respiration mechanism often referred to as cryptic. The prevalence of the so-called cryptic mechanism in meromictic, low-sulphate lakes could be attributed to the abundance of crystalline as opposed to more reactive amorphous iron (oxyhyd)roxides, which by immobilizing ferric iron also favour microbial sulphate reduction (MSR) promoting the accumulation of solid phase intermediate sulphur and sulphides<sup>[1]</sup>. In a ferruginous, sulphate-rich and oligotrophic post-mining lake (Lake Medard, Czech Republic) we observed a departure from this condition as dissolved sulphide does not accumulate in the bottom water column nor precipitate in the anoxic sediments.<sup>[2]</sup> Analyses of the bacterioplankton abundance in the hypolimnion indicate a marked niche compartmentalization, with Fe(II)-oxidising microbes, such as <em>Gallionella</em> sp., <em>Rhodopseudomonas</em> sp. and <em>Sideroxydans</em> sp., being important at the dysoxic to anoxic (ferruginous) interface where they drive the regeneration of ferric iron. On the other hand, Fe(III)-reducers, such as <em>Geobacter</em> sp. and<em> Rhodoferax</em> sp. are present at the O<sub>2</sub>-depleted monimolimnion and in the uppermost anoxic sediments. Toward the redox interface, the chemolithotrophic community described above allows for Fe-(re)cycling and drives the oxidation and turnover of the scarcely available volatile fatty acids. Sulphate reducers (e.g. Desulfobulbaceae, <em>Chrostridia, Desulfarculus</em>) and microorganisms capable of anammox, such as <em>Nitrosomonas</em>  and <em>Nitrosospira</em> where found below the redoxcline. However, together these obligate anaerobes account for < 4% of the total bacterial OTUs identified in the monimolimnion. Our observations in this purported modern analogue to ferruginous, relatively sulphate-enriched Precambrian coastal zones raise the possibility that limited dissimilatory sulphate reduction in the Earth’s primitive ferruginous oceans was rather linked to the scarcity of suitable organic substrates and high rates of Fe-(re)cycling than to low levels of dissolved sulphate. The co-precipitation of minor amounts of gypsum/anhydrite and siderite, with Fe(II,III)-(oxyhydr)oxides further support a potential link between the deep Lake Medard precipitation environment and certain mid- to Late-Archean marginal settings, where these phases have been described to be primary and/or early diagenetic in origin. </p> </div><div> <p><sup>[1]</sup> Hansel, C.M., Lentini, C.J., Tang, Y., et al. ISME J. 9, 2400–2412 (2015). </p> </div><div> <p><sup>[2]</sup> Petrash, D.A., Jan, J., Sirová, et al. Environ. Sci. Process. Impacts 20, 1414–1426 (2018). </p> </div><div> <p> </p> </div>

2008 ◽  
Vol 1107 ◽  
Author(s):  
J. Tits ◽  
T. Fujita ◽  
M. Tsukamoto ◽  
E. Wieland

AbstractThe immobilization of U(VI) by C-S-H phases under conditions relevant for the cementitious near field of a repository for radioactive waste has been investigated. C-S-H phases have been synthesized using two different procedures: the “direct reaction” method and the “solution reaction” method.The stabilities of alkaline solutions of U(VI) (presence of precipitates or colloidal material) were studied prior to sorption and co-precipitation tests in order to determine the experimental U(VI) solubility limits. These U(VI) solubility limits were compared with the U(VI) solubilities obtained from thermodynamic speciation calculations assuming the presence of combinations of different solid U(VI) phases. The solid phase controlling U(VI) solubility in the present experiments was found to be CaUO4(s).The U(VI) uptake kinetics and sorption isotherms on C-S-H phases with different C:S ratios were determined under various chemical conditions; e.g., sorption and co-precipitation experiments and different pH’s. U(VI) was found to sorb fast and very strongly on C-S-H phases with distribution ratios (Rd values) ranging in value between 103 L kg-1 and 106 L kg-1. Both sorption and co-precipitation experiments resulted in Rd values which were very similar, thus indicating that no additional sorption sites for U(VI) were generated in the co-precipitation process. Furthermore, C-S-H synthesis procedures did not have a significant influence on U(VI) uptake. The U(VI) sorption isotherms were found to be non-linear, and further, increasing Ca concentrations resulted in increasing U(VI) uptake. The latter observation suggests that U(VI) uptake is controlled by a solubility-limiting process, while the former observation further indicates that pure Ca-uranate is not the solubility-limiting phase. It is proposed that a solid solution containing Ca and could control U(VI) uptake by C-S-H phases.


Author(s):  
Laskar ◽  
Awata ◽  
Kasai ◽  
Katayama

Anoxic aquifers suffer from energy limitations due to the unavailability of organic substrates, as dictated by hydrogen (H2) for various electron-accepting processes. This deficiency often results in the accumulation of persistent organic pollutants, where bioremediation using organic compounds often leads to secondary contamination. This study involves the reductive dechlorination of pentachlorophenol (PCP) by dechlorinators that do not use H2 directly, but rather through a reduced state of humin—a solid-phase humic substance—as the extracellular electron donor, which requires an organic donor such as formate, lactate, etc. This shortcoming was addressed by the development of an anaerobic mixed culture that was capable of reductively dechlorinating PCP using humin under autotrophic conditions induced by homoacetogenesis. Here, H2 was used for carbon-dioxide fixation to acetate; the acetate produced was used for the reduction of humin; and consequently used for dechlorination through reduced humin. The 16SrRNA gene sequencing analysis showed Dehalobacter and Dehalobacterium as the possible dechlorinators, while Clostridium and Oxobacter were identified as the homoacetogens. Thus, this work contributes to the development of an anaerobic consortium that balanced H2 dependency, where efficiency of humin reduction extends the applicability of anaerobic microbial remediation in aquifers through autotrophy, syntrophy, and reductive dechlorination.


2004 ◽  
Vol 49 (9) ◽  
pp. 89-98 ◽  
Author(s):  
Y. Huang ◽  
L. Ortiz ◽  
J. García ◽  
P. Aguirre ◽  
R. Mujeriego ◽  
...  

A headspace solid-phase microextraction (HS-SPME) preconcentration method was applied to the analysis of some of the major odorous compounds occurring in wastewater using GC/MS or GC/NPD detection. The detection limit for volatile amines, volatile fatty acids, and volatile alkylsulphides ranged from 3 to 100, 2 to 150, and 0.0006 to 0.035 μg/L, respectively. The SPME method was used to examine the fate of odorous compounds in the subsurface flow constructed wetlands (SFCW) operated under different hydraulic loading rate (HLR), bed aspect ratio, and granular medium size. Among the experimental conditions evaluated in the SFCW beds, HLR was found to be the most important factor influencing the evolution of the studied compounds. There were also significant differences among bed types in the behaviour of ammonia (NH3), acetic acid (Ac), isovaleric acid (IsoA), propionic acid (PrA), and dimethylsulphide. Aspect ratio and medium granular size were minor factors influencing SFCW performance. The major odour compounds by mass in the effluent of SFCW with different operational conditions were NH3 and Ac. Further removal of these two compounds is considered as very important from the viewpoint of chemical composition. On the other hand, Relative Odour Intensity (ROI: ratio between the absolute concentration to the odour threshold concentration) suggested that PrA and IsoA were the two major compounds responsible for odour intensity. Thus, further removal of these two compounds is viewed as very important for the effluent deodorization, especially for PrA. From our results, this compound appears to be produced by processes occurring in the SFCW.


1986 ◽  
Vol 43 (2) ◽  
pp. 183-194 ◽  
Author(s):  
R. J. Dewhurst ◽  
A. J. F. Webster ◽  
F. W. Wainman ◽  
P. J. S. Dewey

ABSTRACTA model has been developed to predict the true metabolizable energy (ME,) concentration in forages given to ruminants.The chemical description of forages is based on the concentrations of ash, crude protein, ether extract, sugars and α-glycans, β-glycans and lignin, volatile fatty acids and lactic acid. The model assumes complete fermentation of sugars, α-glycans and lactic acid. The extent of fermentation of β-glycans and crude protein is determined in part by rumen solid-phase outflow rate, which can itself be predicted from dry-matter intake.The model was tested using 121 graminaceous forages whose chemical composition and concentration of metabolizable energy had been measured in the Feedingstuffs Evaluation Unit at the Rowett Research Institute. The agreement between observed and predicted ME, for all classes of forage was nearly always as good as, or better than, the best prediction from single attributes of food chemistry which could only be determined retrospectively and were not consistent even within classes of forage. The model predicts a decline in ME, with increasing rumen solid-phase outflow rate which is determined mainly by the extent of fermentation of β-glycans.


2013 ◽  
Vol 745-746 ◽  
pp. 512-516
Author(s):  
Qing Wei Wang ◽  
Hong Zhi Wang ◽  
Wei Ning ◽  
Li Da Luo

The Pr2O3 doped SnO2 dense ceramic was prepared by co-precipitation method and further sintering. Through the micrograph of the cross-sectional microstructure of the electrodes, the sintering process was analyzed and discussed. Results showed that the solid phase sintering was exhibited at the early stage; when sintering was kept going on, the instant liquid phase could be emerged due to the rich dopants in the grain boundary. Finally, there would be much secondary phase existe as the concentration of dopants reached to a certain value.


2014 ◽  
Vol 1708 ◽  
Author(s):  
K. Simeonidis ◽  
N. Andritsos ◽  
E. Kaprara ◽  
S. Mourdikoudis ◽  
M. Mitrakas

ABSTRACTMagnetite nanoparticles were produced by the chemical co-precipitation of iron sulfates at alkaline conditions and were tested as a Cr(VI) adsorbent from water. Batch adsorption experiments showed a high removal efficiency, which is maximized at pH values below 6. This behavior was also verified in a continuous flow reactor, where nanoparticles were in contact with the polluted water. In particular, using a particle concentration of 1 g/L in water containing 100 μg Cr(VI)/L, a contact time of at least 2 h was required to achieve complete removal of Cr(VI). The recovery of nanoparticles after their use was accomplished using their magnetic nature. Application of an external magnetic field at the sides of the tube in which the suspension was flowing was sufficient to completely collect the nanoparticles in the outflow of the contact reactor, thus, providing water free of Cr(VI) and a solid phase.


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