2017
DOI: 10.1016/j.chemosphere.2016.10.082
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Impact of estuarine gradients on reductive dechlorination of 1,2,3,4-tetrachlorodibenzo-p-dioxin in river sediment enrichment cultures

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Cited by 10 publications
(16 citation statements)
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“…Obtaining genomes of rare microorganisms through culture-independent methods requires either extensive sampling over a long period of time to capture the moment when rare species become dominant or very deep sequencing, if at all possible ( Hugenholtz et al, 1998 ; Köpke et al, 2005 ). Some species with unique, important, and rate-limiting biological functions (such as nitrification, methane and methanol oxidation, or respiratory dehalogenation) are however permanently found at low abundance in the environment ( Griffiths et al, 2004 ; Dam and Häggblom, 2017 ; Pratscher et al, 2018 ). Nevertheless, those rare microorganisms play important ecological roles and contribute to biodiversity and ecological cycles more than previously known ( Jousset et al, 2017 ).…”
Section: Discussionmentioning
confidence: 99%
“…Obtaining genomes of rare microorganisms through culture-independent methods requires either extensive sampling over a long period of time to capture the moment when rare species become dominant or very deep sequencing, if at all possible ( Hugenholtz et al, 1998 ; Köpke et al, 2005 ). Some species with unique, important, and rate-limiting biological functions (such as nitrification, methane and methanol oxidation, or respiratory dehalogenation) are however permanently found at low abundance in the environment ( Griffiths et al, 2004 ; Dam and Häggblom, 2017 ; Pratscher et al, 2018 ). Nevertheless, those rare microorganisms play important ecological roles and contribute to biodiversity and ecological cycles more than previously known ( Jousset et al, 2017 ).…”
Section: Discussionmentioning
confidence: 99%
“…This was expected, since previous work demonstrated microbial dechlorination of 1,2,3,4-TeCDD in both the Passaic 21 and Hackensack rivers. 33 The fact that set 4, created with the original river sediment, showed the least amount of dechlorination supports the notion that cultures enriched on the alternate, more soluble organohalides would be able to more rapidly dechlorinate PCDDs than unenriched cultures. This same pathway of 1,2,3,4-TeCDD dechlorination (Figure S3) was proposed by Bunge et al, 41 Ahn et al, 23 and Dam et al, 33 but not Fennell et al, 14 TrCDD by strain 195.…”
Section: ■ Resultsmentioning
confidence: 69%
“…In the current study, it is unclear if slightly different sets of dehalogenases are operating in the different treatment sets (e.g., set 7 has a high ratio of 2,3-to 1,3-DiCDD, while set 10 and 13 have more 1,3-than 2,3-DiCDD) since they are all at vastly different dechlorination stages. We also do not know if 1,3-DiCDD is a product of both 1,2,3-and 1,2,4-TrCDD dechlorination as is the case for strain CBDB1, 15 or if it comes exclusively from one of the TrCDD congeners as observed with the H1 Hackensack River enrichment culture described by Dam et al 33 Interestingly, Ahn et al 23 reported that the ratio of 1,3-DiCDD: 2,3-DiCDD in 1,2,3,4-TeCDD-amended microcosms was greater with the hydrophobic tetrachlorobenzene cosubstrate rather than the hydrophilic chlorophenol cosubstrate. 23 We also saw a greater ratio of 1,3-DiCDD: The fact that set 13, the culture enriched with DCB, proved most capable of 1,2,3,4-TeCDD dechlorination indicates that DCB was a more suitable substrate for growing PCDDdechlorinating OHRB than TCE in this system.…”
Section: ■ Resultsmentioning
confidence: 91%
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