2013
DOI: 10.1002/jobm.201200394
|View full text |Cite
|
Sign up to set email alerts
|

Potential of the salt‐tolerant laccase‐producing strain Trichoderma viride Pers. NFCCI‐2745 from an estuary in the bioremediation of phenol‐polluted environments

Abstract: Industrialization causes the generation of phenolic pollutants in the environment. The ability of laccases to oxidize phenolic compounds and reduce molecular oxygen to water has led to intensive studies on these enzymes. Although salt-tolerant fungi are potential sources of enzymes for industrial applications, they have been inadequately explored for laccase production. This study describes the isolation of a salt- and phenol-tolerant strain of Trichoderma sp. with the ability to produce laccase, and thus with… Show more

Help me understand this report

Search citation statements

Order By: Relevance

Paper Sections

Select...
2
1
1
1

Citation Types

0
11
0

Year Published

2014
2014
2021
2021

Publication Types

Select...
5
4

Relationship

0
9

Authors

Journals

citations
Cited by 29 publications
(11 citation statements)
references
References 28 publications
0
11
0
Order By: Relevance
“…However, higher phenol concentration did harm to the fungi and the pollutant removal efficiency fluctuated when phenol concentration was up to 1000 mg/L with certain inoculating quantity (data not shown). This might reflect the substrate inhibition of fungal growth due to extension of the lag phase, which was also observed on Trichoderma viride Pers (Divya et al, 2014). The strain reached the highest reduction rate and phenol concentration decreased from the initial 500 mg/L to nearly 0 mg/L by the end of 34 h. During this period, the phenol concentration plunged from 275.5 to 17.3 mg/L in 4 h, which was in accordance with the significant increase of OD 600 between 30 h and 34 h. In contrast, Kobayashi et al (2012) have found that the maximum phenol degradation rate of Acinetobacter sp.…”
Section: Phenol Degradationmentioning
confidence: 70%
“…However, higher phenol concentration did harm to the fungi and the pollutant removal efficiency fluctuated when phenol concentration was up to 1000 mg/L with certain inoculating quantity (data not shown). This might reflect the substrate inhibition of fungal growth due to extension of the lag phase, which was also observed on Trichoderma viride Pers (Divya et al, 2014). The strain reached the highest reduction rate and phenol concentration decreased from the initial 500 mg/L to nearly 0 mg/L by the end of 34 h. During this period, the phenol concentration plunged from 275.5 to 17.3 mg/L in 4 h, which was in accordance with the significant increase of OD 600 between 30 h and 34 h. In contrast, Kobayashi et al (2012) have found that the maximum phenol degradation rate of Acinetobacter sp.…”
Section: Phenol Degradationmentioning
confidence: 70%
“…Several factors have been proposed for enhancing the bioremediation of toxic and persistent organic pollutants by applying fungi. The attribute of marine fungi for producing laccase tolerant to high salinity and phenolics was aptly exploited by Divya et al [38] in case of Trichoderma viride Pers NFCCI-2745 isolated from an estuary polluted with phenolics. Similar applications of enzyme mediated bioremediation was demonstrated for decolorizing Remazol Brilliant Blue-R dye using three basidiomycetes isolated from marine sponges [39], and anthraquinone dye Reactive Blue 4 by C. unicolor, a marine white-rot basidiomycete.…”
Section: Marine Fungimentioning
confidence: 99%
“…They are also recognized for their potential in bio-and phytobioremediation of toxic compounds by degrading pollutants particularly in the soil environment [86][87][88]. The versatility of Trichoderma spp.…”
Section: Introductionmentioning
confidence: 99%