Characterization of Cu(II) and Cd(II) resistance mechanisms in Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH and their potential application in the bioremediation of heavy metal-phenanthrene co-contaminated sites

Soil that is co-contaminated with heavy metals (HMs) and polycyclic aromatic hydrocarbons (PAHs) is difficult to bioremediate due to the ability of toxic metals to inhibit PAH degradation by bacteria. We demonstrated the resistance mechanisms to Cu(II) and Cd(II) of two newly isolated strains of Sph...

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Veröffentlicht in:Environmental science and pollution research international 2016-04, Vol.23 (7), p.6861-6872
Hauptverfasser: Chen, Chen, Lei, Wenrui, Lu, Min, Zhang, Jianan, Zhang, Zhou, Luo, Chunling, Chen, Yahua, Hong, Qing, Shen, Zhenguo
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container_end_page 6872
container_issue 7
container_start_page 6861
container_title Environmental science and pollution research international
container_volume 23
creator Chen, Chen
Lei, Wenrui
Lu, Min
Zhang, Jianan
Zhang, Zhou
Luo, Chunling
Chen, Yahua
Hong, Qing
Shen, Zhenguo
description Soil that is co-contaminated with heavy metals (HMs) and polycyclic aromatic hydrocarbons (PAHs) is difficult to bioremediate due to the ability of toxic metals to inhibit PAH degradation by bacteria. We demonstrated the resistance mechanisms to Cu(II) and Cd(II) of two newly isolated strains of Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH and further tested their potential application in the bioremediation of HM-phenanthrene (PhA) co-contaminated sites. The PHE-SPH and PHE-OCH strains tolerated 4.63 and 4.34 mM Cu(II) and also showed tolerance to 0.48 and 1.52 mM Cd(II), respectively. Diverse resistance patterns were detected between the two strains. In PHE-OCH cells, the maximum accumulation of Cu(II) occurred in the cell wall, while the maximum accumulation was in the cytoplasm of PHE-SPH cells. This resulted in a sudden suppression of growth in PHE-OCH and a gradual inhibition in PHE-SPH as the concentration of Cu(II) increased. Organic acid production was markedly higher in PHE-OCH than in PHE-SPH, which may also have a role in the resistance mechanisms, and contributes to the higher Cd(II) tolerance of PHE-OCH. The factors involved in the absorption of Cu(II) or Cd(II) in PHE-SPH and PHE-OCH were identified as proteins and carbohydrates by Fourier transform infrared (FT-IR) spectroscopy. Furthermore, both strains showed the ability to efficiently degrade PhA and maintained this high degradation efficiency under HM stress. The high tolerance to HMs and the PhA degradation capacity make Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH excellent candidate organisms for the bioremediation of HM-PhA co-contaminated sites.
doi_str_mv 10.1007/s11356-015-5926-0
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PHE-SPH and Ochrobactrum sp. PHE-OCH and their potential application in the bioremediation of heavy metal-phenanthrene co-contaminated sites</title><source>MEDLINE</source><source>SpringerLink Journals - AutoHoldings</source><creator>Chen, Chen ; Lei, Wenrui ; Lu, Min ; Zhang, Jianan ; Zhang, Zhou ; Luo, Chunling ; Chen, Yahua ; Hong, Qing ; Shen, Zhenguo</creator><creatorcontrib>Chen, Chen ; Lei, Wenrui ; Lu, Min ; Zhang, Jianan ; Zhang, Zhou ; Luo, Chunling ; Chen, Yahua ; Hong, Qing ; Shen, Zhenguo</creatorcontrib><description>Soil that is co-contaminated with heavy metals (HMs) and polycyclic aromatic hydrocarbons (PAHs) is difficult to bioremediate due to the ability of toxic metals to inhibit PAH degradation by bacteria. We demonstrated the resistance mechanisms to Cu(II) and Cd(II) of two newly isolated strains of Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH and further tested their potential application in the bioremediation of HM-phenanthrene (PhA) co-contaminated sites. The PHE-SPH and PHE-OCH strains tolerated 4.63 and 4.34 mM Cu(II) and also showed tolerance to 0.48 and 1.52 mM Cd(II), respectively. Diverse resistance patterns were detected between the two strains. In PHE-OCH cells, the maximum accumulation of Cu(II) occurred in the cell wall, while the maximum accumulation was in the cytoplasm of PHE-SPH cells. This resulted in a sudden suppression of growth in PHE-OCH and a gradual inhibition in PHE-SPH as the concentration of Cu(II) increased. Organic acid production was markedly higher in PHE-OCH than in PHE-SPH, which may also have a role in the resistance mechanisms, and contributes to the higher Cd(II) tolerance of PHE-OCH. The factors involved in the absorption of Cu(II) or Cd(II) in PHE-SPH and PHE-OCH were identified as proteins and carbohydrates by Fourier transform infrared (FT-IR) spectroscopy. Furthermore, both strains showed the ability to efficiently degrade PhA and maintained this high degradation efficiency under HM stress. The high tolerance to HMs and the PhA degradation capacity make Sphingobium sp. PHE-SPH and Ochrobactrum sp. 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PHE-SPH and Ochrobactrum sp. PHE-OCH and their potential application in the bioremediation of heavy metal-phenanthrene co-contaminated sites</title><title>Environmental science and pollution research international</title><addtitle>Environ Sci Pollut Res</addtitle><addtitle>Environ Sci Pollut Res Int</addtitle><description>Soil that is co-contaminated with heavy metals (HMs) and polycyclic aromatic hydrocarbons (PAHs) is difficult to bioremediate due to the ability of toxic metals to inhibit PAH degradation by bacteria. We demonstrated the resistance mechanisms to Cu(II) and Cd(II) of two newly isolated strains of Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH and further tested their potential application in the bioremediation of HM-phenanthrene (PhA) co-contaminated sites. The PHE-SPH and PHE-OCH strains tolerated 4.63 and 4.34 mM Cu(II) and also showed tolerance to 0.48 and 1.52 mM Cd(II), respectively. Diverse resistance patterns were detected between the two strains. In PHE-OCH cells, the maximum accumulation of Cu(II) occurred in the cell wall, while the maximum accumulation was in the cytoplasm of PHE-SPH cells. This resulted in a sudden suppression of growth in PHE-OCH and a gradual inhibition in PHE-SPH as the concentration of Cu(II) increased. Organic acid production was markedly higher in PHE-OCH than in PHE-SPH, which may also have a role in the resistance mechanisms, and contributes to the higher Cd(II) tolerance of PHE-OCH. The factors involved in the absorption of Cu(II) or Cd(II) in PHE-SPH and PHE-OCH were identified as proteins and carbohydrates by Fourier transform infrared (FT-IR) spectroscopy. Furthermore, both strains showed the ability to efficiently degrade PhA and maintained this high degradation efficiency under HM stress. The high tolerance to HMs and the PhA degradation capacity make Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH excellent candidate organisms for the bioremediation of HM-PhA co-contaminated sites.</description><subject>absorption</subject><subject>Acid production</subject><subject>Anti-Bacterial Agents - pharmacology</subject><subject>Aquatic Pollution</subject><subject>Atmospheric Protection/Air Quality Control/Air Pollution</subject><subject>bacteria</subject><subject>Biodegradation, Environmental</subject><subject>Bioremediation</subject><subject>Cadmium</subject><subject>Cadmium - analysis</subject><subject>Cadmium - chemistry</subject><subject>Cadmium - pharmacology</subject><subject>Carbohydrates</subject><subject>cell walls</subject><subject>Copper</subject><subject>Copper - analysis</subject><subject>Copper - chemistry</subject><subject>Copper - pharmacology</subject><subject>cytoplasm</subject><subject>Drug Resistance, Bacterial</subject><subject>Earth and Environmental Science</subject><subject>Ecotoxicology</subject><subject>Environment</subject><subject>Environmental Chemistry</subject><subject>Environmental Health</subject><subject>Environmental science</subject><subject>Experiments</subject><subject>Fourier transform infrared spectroscopy</subject><subject>Fourier transforms</subject><subject>Geochemistry</subject><subject>Heavy metals</subject><subject>Lethal Dose 50</subject><subject>Metals</subject><subject>Microbial Sensitivity Tests</subject><subject>Microorganisms</subject><subject>Ochrobactrum</subject><subject>Ochrobactrum - drug effects</subject><subject>Ochrobactrum - metabolism</subject><subject>Organic acids</subject><subject>Phenanthrene</subject><subject>Phenanthrenes - analysis</subject><subject>Phenanthrenes - chemistry</subject><subject>Phenanthrenes - pharmacology</subject><subject>Polycyclic aromatic hydrocarbons</subject><subject>proteins</subject><subject>Research Article</subject><subject>resistance mechanisms</subject><subject>soil</subject><subject>Soil - chemistry</subject><subject>Soil contamination</subject><subject>Soil Microbiology</subject><subject>Soil Pollutants - analysis</subject><subject>Soil Pollutants - chemistry</subject><subject>Soil Pollutants - pharmacology</subject><subject>Sphingobacterium - drug effects</subject><subject>Sphingobacterium - metabolism</subject><subject>Sphingobium</subject><subject>Sphingomonas</subject><subject>Studies</subject><subject>toxicity</subject><subject>Waste Water Technology</subject><subject>Water Management</subject><subject>Water Pollution Control</subject><issn>0944-1344</issn><issn>1614-7499</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2016</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>BENPR</sourceid><recordid>eNqNksFu1DAQhiMEokvhAbiAJS7lkGI7Xjs-oqiwK1VqpS1ny3FmN64SO9gOUnlVXgZvU6qKA-Lksf5vfo9Hf1G8JficYCw-RUKqNS8xWZdrSXPxrFgRTlgpmJTPixWWjJWkYuykeBXjLcYUSypeFieUc5Fv9ar41fQ6aJMg2J86We-Q36NmPttuPyLtOtR092WAaGPSzgAawfTa2ThGZB3aTb11B9_aeURxOkfXm4tyd725770yffBtNg9PxKtmEVMPNqDJJ3DJ6gHpaRqsWUbIvllGrfUBRujs42A96B93eYKkh3LqwWmX-gAOkPGl8S7p0TqdoEPRJoivixd7PUR483CeFjdfLm6aTXl59XXbfL4sDeM8lQC4EpR0sOcgtcCEY76Wa0IrTUzLa9MaBh0DziTUlZB5qUSwuhOUZ5lVp8XZYjsF_32GmNRoo4Fh0A78HBUREkuBa0r-AxX1kRQyox_-Qm_9HFz-R6bqmmNWsSNFFsoEH2OAvZqCHXW4UwSrY0bUkhGVM6KOGVE497x7cJ7bvN3Hjj-hyABdgJgld4Dw5Ol_uL5fmvbaK30INqpvO3pcJiYVZZJUvwH_5dDK</recordid><startdate>20160401</startdate><enddate>20160401</enddate><creator>Chen, Chen</creator><creator>Lei, Wenrui</creator><creator>Lu, Min</creator><creator>Zhang, Jianan</creator><creator>Zhang, Zhou</creator><creator>Luo, Chunling</creator><creator>Chen, Yahua</creator><creator>Hong, Qing</creator><creator>Shen, Zhenguo</creator><general>Springer Berlin Heidelberg</general><general>Springer Nature B.V</general><scope>FBQ</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7QL</scope><scope>7SN</scope><scope>7T7</scope><scope>7TV</scope><scope>7U7</scope><scope>7WY</scope><scope>7WZ</scope><scope>7X7</scope><scope>7XB</scope><scope>87Z</scope><scope>88E</scope><scope>88I</scope><scope>8AO</scope><scope>8C1</scope><scope>8FD</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8FL</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BEZIV</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FRNLG</scope><scope>FYUFA</scope><scope>F~G</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>K60</scope><scope>K6~</scope><scope>K9.</scope><scope>L.-</scope><scope>M0C</scope><scope>M0S</scope><scope>M1P</scope><scope>M2P</scope><scope>M7N</scope><scope>P64</scope><scope>PATMY</scope><scope>PQBIZ</scope><scope>PQBZA</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>7X8</scope><scope>7ST</scope><scope>SOI</scope></search><sort><creationdate>20160401</creationdate><title>Characterization of Cu(II) and Cd(II) resistance mechanisms in Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH and their potential application in the bioremediation of heavy metal-phenanthrene co-contaminated sites</title><author>Chen, Chen ; Lei, Wenrui ; Lu, Min ; Zhang, Jianan ; Zhang, Zhou ; Luo, Chunling ; Chen, Yahua ; Hong, Qing ; Shen, Zhenguo</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c466t-ee03721def6e9a701606595123a1cb68cbc4ed4e649e83799441748d726cb643</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2016</creationdate><topic>absorption</topic><topic>Acid production</topic><topic>Anti-Bacterial Agents - pharmacology</topic><topic>Aquatic Pollution</topic><topic>Atmospheric Protection/Air Quality Control/Air Pollution</topic><topic>bacteria</topic><topic>Biodegradation, Environmental</topic><topic>Bioremediation</topic><topic>Cadmium</topic><topic>Cadmium - analysis</topic><topic>Cadmium - chemistry</topic><topic>Cadmium - pharmacology</topic><topic>Carbohydrates</topic><topic>cell walls</topic><topic>Copper</topic><topic>Copper - analysis</topic><topic>Copper - chemistry</topic><topic>Copper - pharmacology</topic><topic>cytoplasm</topic><topic>Drug Resistance, Bacterial</topic><topic>Earth and Environmental Science</topic><topic>Ecotoxicology</topic><topic>Environment</topic><topic>Environmental Chemistry</topic><topic>Environmental Health</topic><topic>Environmental science</topic><topic>Experiments</topic><topic>Fourier transform infrared spectroscopy</topic><topic>Fourier transforms</topic><topic>Geochemistry</topic><topic>Heavy metals</topic><topic>Lethal Dose 50</topic><topic>Metals</topic><topic>Microbial Sensitivity Tests</topic><topic>Microorganisms</topic><topic>Ochrobactrum</topic><topic>Ochrobactrum - drug effects</topic><topic>Ochrobactrum - metabolism</topic><topic>Organic acids</topic><topic>Phenanthrene</topic><topic>Phenanthrenes - analysis</topic><topic>Phenanthrenes - chemistry</topic><topic>Phenanthrenes - pharmacology</topic><topic>Polycyclic aromatic hydrocarbons</topic><topic>proteins</topic><topic>Research Article</topic><topic>resistance mechanisms</topic><topic>soil</topic><topic>Soil - chemistry</topic><topic>Soil contamination</topic><topic>Soil Microbiology</topic><topic>Soil Pollutants - analysis</topic><topic>Soil Pollutants - chemistry</topic><topic>Soil Pollutants - pharmacology</topic><topic>Sphingobacterium - drug effects</topic><topic>Sphingobacterium - metabolism</topic><topic>Sphingobium</topic><topic>Sphingomonas</topic><topic>Studies</topic><topic>toxicity</topic><topic>Waste Water Technology</topic><topic>Water Management</topic><topic>Water Pollution Control</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Chen, Chen</creatorcontrib><creatorcontrib>Lei, Wenrui</creatorcontrib><creatorcontrib>Lu, Min</creatorcontrib><creatorcontrib>Zhang, Jianan</creatorcontrib><creatorcontrib>Zhang, Zhou</creatorcontrib><creatorcontrib>Luo, Chunling</creatorcontrib><creatorcontrib>Chen, Yahua</creatorcontrib><creatorcontrib>Hong, Qing</creatorcontrib><creatorcontrib>Shen, Zhenguo</creatorcontrib><collection>AGRIS</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Ecology Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>ABI/INFORM Collection</collection><collection>ABI/INFORM Global (PDF only)</collection><collection>Health &amp; 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PHE-SPH and Ochrobactrum sp. PHE-OCH and their potential application in the bioremediation of heavy metal-phenanthrene co-contaminated sites</atitle><jtitle>Environmental science and pollution research international</jtitle><stitle>Environ Sci Pollut Res</stitle><addtitle>Environ Sci Pollut Res Int</addtitle><date>2016-04-01</date><risdate>2016</risdate><volume>23</volume><issue>7</issue><spage>6861</spage><epage>6872</epage><pages>6861-6872</pages><issn>0944-1344</issn><eissn>1614-7499</eissn><abstract>Soil that is co-contaminated with heavy metals (HMs) and polycyclic aromatic hydrocarbons (PAHs) is difficult to bioremediate due to the ability of toxic metals to inhibit PAH degradation by bacteria. We demonstrated the resistance mechanisms to Cu(II) and Cd(II) of two newly isolated strains of Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH and further tested their potential application in the bioremediation of HM-phenanthrene (PhA) co-contaminated sites. The PHE-SPH and PHE-OCH strains tolerated 4.63 and 4.34 mM Cu(II) and also showed tolerance to 0.48 and 1.52 mM Cd(II), respectively. Diverse resistance patterns were detected between the two strains. In PHE-OCH cells, the maximum accumulation of Cu(II) occurred in the cell wall, while the maximum accumulation was in the cytoplasm of PHE-SPH cells. This resulted in a sudden suppression of growth in PHE-OCH and a gradual inhibition in PHE-SPH as the concentration of Cu(II) increased. Organic acid production was markedly higher in PHE-OCH than in PHE-SPH, which may also have a role in the resistance mechanisms, and contributes to the higher Cd(II) tolerance of PHE-OCH. The factors involved in the absorption of Cu(II) or Cd(II) in PHE-SPH and PHE-OCH were identified as proteins and carbohydrates by Fourier transform infrared (FT-IR) spectroscopy. Furthermore, both strains showed the ability to efficiently degrade PhA and maintained this high degradation efficiency under HM stress. The high tolerance to HMs and the PhA degradation capacity make Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH excellent candidate organisms for the bioremediation of HM-PhA co-contaminated sites.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><pmid>26670028</pmid><doi>10.1007/s11356-015-5926-0</doi><tpages>12</tpages></addata></record>
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ispartof Environmental science and pollution research international, 2016-04, Vol.23 (7), p.6861-6872
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source MEDLINE; SpringerLink Journals - AutoHoldings
subjects absorption
Acid production
Anti-Bacterial Agents - pharmacology
Aquatic Pollution
Atmospheric Protection/Air Quality Control/Air Pollution
bacteria
Biodegradation, Environmental
Bioremediation
Cadmium
Cadmium - analysis
Cadmium - chemistry
Cadmium - pharmacology
Carbohydrates
cell walls
Copper
Copper - analysis
Copper - chemistry
Copper - pharmacology
cytoplasm
Drug Resistance, Bacterial
Earth and Environmental Science
Ecotoxicology
Environment
Environmental Chemistry
Environmental Health
Environmental science
Experiments
Fourier transform infrared spectroscopy
Fourier transforms
Geochemistry
Heavy metals
Lethal Dose 50
Metals
Microbial Sensitivity Tests
Microorganisms
Ochrobactrum
Ochrobactrum - drug effects
Ochrobactrum - metabolism
Organic acids
Phenanthrene
Phenanthrenes - analysis
Phenanthrenes - chemistry
Phenanthrenes - pharmacology
Polycyclic aromatic hydrocarbons
proteins
Research Article
resistance mechanisms
soil
Soil - chemistry
Soil contamination
Soil Microbiology
Soil Pollutants - analysis
Soil Pollutants - chemistry
Soil Pollutants - pharmacology
Sphingobacterium - drug effects
Sphingobacterium - metabolism
Sphingobium
Sphingomonas
Studies
toxicity
Waste Water Technology
Water Management
Water Pollution Control
title Characterization of Cu(II) and Cd(II) resistance mechanisms in Sphingobium sp. PHE-SPH and Ochrobactrum sp. PHE-OCH and their potential application in the bioremediation of heavy metal-phenanthrene co-contaminated sites
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