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Cadmium-induced stress response of Phanerochaete chrysosporium during the biodegradation of 2,2',4,4'-tetrabromodiphenyl ether (BDE-47).

Identifieur interne : 000132 ( Main/Exploration ); précédent : 000131; suivant : 000133

Cadmium-induced stress response of Phanerochaete chrysosporium during the biodegradation of 2,2',4,4'-tetrabromodiphenyl ether (BDE-47).

Auteurs : Mi Feng [République populaire de Chine] ; Hua Yin [République populaire de Chine] ; Yajuan Cao [République populaire de Chine] ; Hui Peng [République populaire de Chine] ; Guining Lu [République populaire de Chine] ; Zehua Liu [République populaire de Chine] ; Zhi Dang [République populaire de Chine]

Source :

RBID : pubmed:29454270

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English descriptors

Abstract

Cd-induced stress response of Phanerochaete chrysosporium during the biodegradation of BDE-47 was investigated in this study, with the goal of elucidating the tolerance behavior and the detoxification mechanisms of P. chrysosporium to resist the Cd stress in the course of BDE-47 biodegradation, which has implications for expanding the application of P. chrysosporium in the bioremediation of Cd and BDE-47 combined pollution. The results suggested that single BDE-47 exposure did not induce obvious oxidative stress in P. chrysosporium, but coexistent Cd significantly triggered ROS generation, both intracellular ROS level and H2O2 content showed positive correlation with Cd concentration. The activities of SOD and CAT were enhanced by low level of Cd (≤ 1 mg/L), but Cd of higher doses (>1 mg/L) depressed the expression of these two antioxidant enzymes at the later exposure period (3-5 days). The intracellular content of GSH along with GSH/GSSG ratio also exhibited a bell-shaped response with a maximum value at Cd of 1 mg/L. Furthermore, Cd-induced ROS generation resulted in the lipid peroxidation, as indicated by a noticeable increment of MDA content found after 3 days. Moreover, the study also indicated that Cd less than 1 mg/L promoted the production of extracellular protein and quickened the decrease of pH value in the medium, while excessive Cd (>1 mg/L) would lead to inhibition. These findings obtained demonstrated that P. chrysosporium had a certain degree of tolerance to Cd within a specific concentration range via regulating the antioxidant levels, inducing the synthesis of extracellular protein as well as stimulating the production of organic acids, and 1 mg/L is suggested to be the tolerance threshold of this strains under Cd stress during BDE-47 biodegradation.

DOI: 10.1016/j.ecoenv.2018.02.018
PubMed: 29454270


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<term>Cadmium (toxicity)</term>
<term>Dose-Response Relationship, Drug (MeSH)</term>
<term>Environmental Pollutants (toxicity)</term>
<term>Halogenated Diphenyl Ethers (toxicity)</term>
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<term>Cadmium (toxicité)</term>
<term>Dépollution biologique de l'environnement (MeSH)</term>
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<div type="abstract" xml:lang="en">Cd-induced stress response of Phanerochaete chrysosporium during the biodegradation of BDE-47 was investigated in this study, with the goal of elucidating the tolerance behavior and the detoxification mechanisms of P. chrysosporium to resist the Cd stress in the course of BDE-47 biodegradation, which has implications for expanding the application of P. chrysosporium in the bioremediation of Cd and BDE-47 combined pollution. The results suggested that single BDE-47 exposure did not induce obvious oxidative stress in P. chrysosporium, but coexistent Cd significantly triggered ROS generation, both intracellular ROS level and H
<sub>2</sub>
O
<sub>2</sub>
content showed positive correlation with Cd concentration. The activities of SOD and CAT were enhanced by low level of Cd (≤ 1 mg/L), but Cd of higher doses (>1 mg/L) depressed the expression of these two antioxidant enzymes at the later exposure period (3-5 days). The intracellular content of GSH along with GSH/GSSG ratio also exhibited a bell-shaped response with a maximum value at Cd of 1 mg/L. Furthermore, Cd-induced ROS generation resulted in the lipid peroxidation, as indicated by a noticeable increment of MDA content found after 3 days. Moreover, the study also indicated that Cd less than 1 mg/L promoted the production of extracellular protein and quickened the decrease of pH value in the medium, while excessive Cd (>1 mg/L) would lead to inhibition. These findings obtained demonstrated that P. chrysosporium had a certain degree of tolerance to Cd within a specific concentration range via regulating the antioxidant levels, inducing the synthesis of extracellular protein as well as stimulating the production of organic acids, and 1 mg/L is suggested to be the tolerance threshold of this strains under Cd stress during BDE-47 biodegradation.</div>
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<sub>2</sub>
O
<sub>2</sub>
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</PublicationTypeList>
<ArticleDate DateType="Electronic">
<Year>2018</Year>
<Month>02</Month>
<Day>22</Day>
</ArticleDate>
</Article>
<MedlineJournalInfo>
<Country>Netherlands</Country>
<MedlineTA>Ecotoxicol Environ Saf</MedlineTA>
<NlmUniqueID>7805381</NlmUniqueID>
<ISSNLinking>0147-6513</ISSNLinking>
</MedlineJournalInfo>
<ChemicalList>
<Chemical>
<RegistryNumber>0</RegistryNumber>
<NameOfSubstance UI="D000975">Antioxidants</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>0</RegistryNumber>
<NameOfSubstance UI="D004785">Environmental Pollutants</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>0</RegistryNumber>
<NameOfSubstance UI="D055768">Halogenated Diphenyl Ethers</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>0</RegistryNumber>
<NameOfSubstance UI="D017382">Reactive Oxygen Species</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>00BH33GNGH</RegistryNumber>
<NameOfSubstance UI="D002104">Cadmium</NameOfSubstance>
</Chemical>
<Chemical>
<RegistryNumber>0N97R5X10X</RegistryNumber>
<NameOfSubstance UI="C511295">2,2',4,4'-tetrabromodiphenyl ether</NameOfSubstance>
</Chemical>
</ChemicalList>
<CitationSubset>IM</CitationSubset>
<MeshHeadingList>
<MeshHeading>
<DescriptorName UI="D000220" MajorTopicYN="N">Adaptation, Biological</DescriptorName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D000975" MajorTopicYN="N">Antioxidants</DescriptorName>
<QualifierName UI="Q000378" MajorTopicYN="Y">metabolism</QualifierName>
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<MeshHeading>
<DescriptorName UI="D001673" MajorTopicYN="N">Biodegradation, Environmental</DescriptorName>
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<MeshHeading>
<DescriptorName UI="D002104" MajorTopicYN="N">Cadmium</DescriptorName>
<QualifierName UI="Q000633" MajorTopicYN="Y">toxicity</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D004305" MajorTopicYN="N">Dose-Response Relationship, Drug</DescriptorName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D004785" MajorTopicYN="N">Environmental Pollutants</DescriptorName>
<QualifierName UI="Q000633" MajorTopicYN="Y">toxicity</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D055768" MajorTopicYN="N">Halogenated Diphenyl Ethers</DescriptorName>
<QualifierName UI="Q000633" MajorTopicYN="Y">toxicity</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D015227" MajorTopicYN="N">Lipid Peroxidation</DescriptorName>
<QualifierName UI="Q000187" MajorTopicYN="N">drug effects</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D018384" MajorTopicYN="N">Oxidative Stress</DescriptorName>
<QualifierName UI="Q000187" MajorTopicYN="Y">drug effects</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D020075" MajorTopicYN="N">Phanerochaete</DescriptorName>
<QualifierName UI="Q000187" MajorTopicYN="Y">drug effects</QualifierName>
<QualifierName UI="Q000201" MajorTopicYN="N">enzymology</QualifierName>
</MeshHeading>
<MeshHeading>
<DescriptorName UI="D017382" MajorTopicYN="N">Reactive Oxygen Species</DescriptorName>
<QualifierName UI="Q000378" MajorTopicYN="N">metabolism</QualifierName>
</MeshHeading>
</MeshHeadingList>
<KeywordList Owner="NOTNLM">
<Keyword MajorTopicYN="N">2,2′,4,4′-tetrabromodiphenyl ether</Keyword>
<Keyword MajorTopicYN="N">Cadmium</Keyword>
<Keyword MajorTopicYN="N">Phanerochaete chrysosporium</Keyword>
<Keyword MajorTopicYN="N">Stress response</Keyword>
</KeywordList>
</MedlineCitation>
<PubmedData>
<History>
<PubMedPubDate PubStatus="received">
<Year>2017</Year>
<Month>11</Month>
<Day>16</Day>
</PubMedPubDate>
<PubMedPubDate PubStatus="revised">
<Year>2018</Year>
<Month>02</Month>
<Day>01</Day>
</PubMedPubDate>
<PubMedPubDate PubStatus="accepted">
<Year>2018</Year>
<Month>02</Month>
<Day>02</Day>
</PubMedPubDate>
<PubMedPubDate PubStatus="pubmed">
<Year>2018</Year>
<Month>2</Month>
<Day>18</Day>
<Hour>6</Hour>
<Minute>0</Minute>
</PubMedPubDate>
<PubMedPubDate PubStatus="medline">
<Year>2018</Year>
<Month>6</Month>
<Day>9</Day>
<Hour>6</Hour>
<Minute>0</Minute>
</PubMedPubDate>
<PubMedPubDate PubStatus="entrez">
<Year>2018</Year>
<Month>2</Month>
<Day>18</Day>
<Hour>6</Hour>
<Minute>0</Minute>
</PubMedPubDate>
</History>
<PublicationStatus>ppublish</PublicationStatus>
<ArticleIdList>
<ArticleId IdType="pubmed">29454270</ArticleId>
<ArticleId IdType="pii">S0147-6513(18)30087-3</ArticleId>
<ArticleId IdType="doi">10.1016/j.ecoenv.2018.02.018</ArticleId>
</ArticleIdList>
</PubmedData>
</pubmed>
<affiliations>
<list>
<country>
<li>République populaire de Chine</li>
</country>
</list>
<tree>
<country name="République populaire de Chine">
<noRegion>
<name sortKey="Feng, Mi" sort="Feng, Mi" uniqKey="Feng M" first="Mi" last="Feng">Mi Feng</name>
</noRegion>
<name sortKey="Cao, Yajuan" sort="Cao, Yajuan" uniqKey="Cao Y" first="Yajuan" last="Cao">Yajuan Cao</name>
<name sortKey="Dang, Zhi" sort="Dang, Zhi" uniqKey="Dang Z" first="Zhi" last="Dang">Zhi Dang</name>
<name sortKey="Liu, Zehua" sort="Liu, Zehua" uniqKey="Liu Z" first="Zehua" last="Liu">Zehua Liu</name>
<name sortKey="Lu, Guining" sort="Lu, Guining" uniqKey="Lu G" first="Guining" last="Lu">Guining Lu</name>
<name sortKey="Peng, Hui" sort="Peng, Hui" uniqKey="Peng H" first="Hui" last="Peng">Hui Peng</name>
<name sortKey="Yin, Hua" sort="Yin, Hua" uniqKey="Yin H" first="Hua" last="Yin">Hua Yin</name>
</country>
</tree>
</affiliations>
</record>

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