2018
DOI: 10.1016/j.bej.2018.08.017
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Progressive change from nitrate to nitrite as the electron acceptor for the oxidation of H2S under feedback control in an anoxic biotrickling filter

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Cited by 27 publications
(19 citation statements)
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References 33 publications
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“…Thiohalophilus sp. is an SOB that has been isolated under microoxic conditions and found to be capable of sulfur-driven anaerobic growth with NO [111]. Although the bacteria were not identified, the authors report that the bacterial diversity was reduced during the progressive adaptation from NO 3 − to NO 2 − , however the DGGE banding patterns were similar, indicating that the same bacterial community was involved in sulfur-driven autotrophic denitrification with both electron acceptors.…”
Section: Anoxic Biofiltrationmentioning
confidence: 99%
“…Thiohalophilus sp. is an SOB that has been isolated under microoxic conditions and found to be capable of sulfur-driven anaerobic growth with NO [111]. Although the bacteria were not identified, the authors report that the bacterial diversity was reduced during the progressive adaptation from NO 3 − to NO 2 − , however the DGGE banding patterns were similar, indicating that the same bacterial community was involved in sulfur-driven autotrophic denitrification with both electron acceptors.…”
Section: Anoxic Biofiltrationmentioning
confidence: 99%
“…Combinations of organic and inorganic materials have also been studied, pursuing the addition of the nutritional properties of the organic materials and the mechanical properties of the inorganic compounds [76]. Polymeric materials such as polyethylene [39], polypropylene [23], plastic rings, and polyurethane foam [18] have also been used, offering advantages such as a high specific area and characteristics of hydrophobic afiinity with the attached microorganisms.…”
Section: Anoxic Btf Packing Materials For Biogas Desulphurisationmentioning
confidence: 99%
“…In some cases only H 2 S inlet and outlet concentrations of the biofilter or BTF were reported, without taking into account the type and concentration of microorganisms that performed the degradation, as described in the Table 2, in the research items 8, 9, 13, 14, and 15. For example, Brito et al (2018) evaluated the change of nitrate (NO 3 − ) to nitrite (NO 2 − ) as electron acceptors in BTFs for H 2 S removal, only reporting the outlet H 2 S concentration (15 ppm v ), describing loading rates (LR) from 7-69 g m −3 h −1 . However, it would be more insightful to have a performance comparison on critical and maximal elimination capacities (ECs) and their respective removal efficiencies (REs), specifically if the LRs was given [23].…”
Section: Introductionmentioning
confidence: 99%
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“…A higher TLV level supplies a higher nitrate availability in the biofilm. TLV has usually been kept constant in anoxic BTFs between 10 [22] and 15 [23] m·h −1 , but for a high H 2 S IL it would be interesting to study the effect of this parameter. As in aerobic BTFs, where TLV is a key operational variable, in aerobic BTFs the regulation of TLV improves the oxygen mass transfer along the packed bed [24].…”
Section: Empirical Modelmentioning
confidence: 99%