Changes in Mycobacterium spp. population structure and pyrene mineralization in polycyclic aromatic hydrocarbon-amended soils
The effect of pyrene and phenanthrene contamination on soil Mycobacterium spp. community structure was examined using PCR-amplification of 16S rRNA genes with primers specific for the fast-growing group of Mycobacterium spp. and separation of phylotypes by temperature gradient gel electrophoresis (T...
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Published in: | Soil biology & biochemistry Vol. 37; no. 10; pp. 1929 - 1937 |
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Abstract | The effect of pyrene and phenanthrene contamination on soil
Mycobacterium spp. community structure was examined using PCR-amplification of 16S rRNA genes with primers specific for the fast-growing group of
Mycobacterium spp. and separation of phylotypes by temperature gradient gel electrophoresis (TGGE). The degradative potential of the soil microbial community was measured over time by mineralization of
14C-pyrene added to the contaminated soils. PCR-TGGE profiles, in combination with band sequencing and phylogenetic analysis of the prominent phylotypes, indicated shifts in the
Mycobacterium spp. community during incubation. Reductions in species diversity and enrichments of specific populations were observed in all pyrene- and phenanthrene-treated soils, in contrast to the relatively stable control soil profiles. Mineralization studies indicated the shortest acclimation periods and the highest initial rates of pyrene degradation occurred in soils pre-exposed to phenanthrene, or a mixture of phenanthrene and pyrene, for 14 weeks. Pre-exposure of soil microorganisms to a single dose of pyrene for the same length of time also decreased the acclimation period for the degradation of pyrene. Monthly application of either pyrene or phenanthrene to soils, however, resulted in an increase in pyrene degradative potential 6 weeks after the first pre-exposure, but a decrease in degradative potential 14 weeks after the first pre-exposure. Similar PCR-TGGE profiles were obtained from soils with comparable pyrene mineralization curves or degradative potentials. |
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AbstractList | The effect of pyrene and phenanthrene contamination on soil Mycobacterium spp. community structure was examined using PCR-amplification of 16S rRNA genes with primers specific for the fast-growing group of Mycobacterium spp. and separation of phylotypes by temperature gradient gel electrophoresis (TGGE). The degradative potential of the soil microbial community was measured over time by mineralization of super(14)C-pyrene added to the contaminated soils. PCR-TGGE profiles, in combination with band sequencing and phylogenetic analysis of the prominent phylotypes, indicated shifts in the Mycobacterium spp. community during incubation. Reductions in species diversity and enrichments of specific populations were observed in all pyrene-and phenanthrene-treated soils, in contrast to the relatively stable control soil profiles. Mineralization studies indicated the shortest acclimation periods and the highest initial rates of pyrene degradation occurred in soils pre-exposed to phenanthrene, or a mixture of phenanthrene and pyrene, for 14 weeks. Pre-exposure of soil microorganisms to a single dose of pyrene for the same length of time also decreased the acclimation period for the degradation of pyrene. Monthly application of either pyrene or phenanthrene to soils, however, resulted in an increase in pyrene degradative potential 6 weeks after the first pre-exposure, but a decrease in degradative potential 14 weeks after the first pre-exposure. Similar PCR-TGGE profiles were obtained from soils with comparable pyrene mineralization curves or degradative potentials. The effect of pyrene and phenanthrene contamination on soil Mycobacterium spp. community structure was examined using PCR-amplification of 16S rRNA genes with primers specific for the fast-growing group of Mycobacterium spp. and separation of phylotypes by temperature gradient gel electrophoresis (TGGE). The degradative potential of the soil microbial community was measured over time by mineralization of 14C-pyrene added to the contaminated soils. PCR-TGGE profiles, in combination with band sequencing and phylogenetic analysis of the prominent phylotypes, indicated shifts in the Mycobacterium spp. community during incubation. Reductions in species diversity and enrichments of specific populations were observed in all pyrene- and phenanthrene-treated soils, in contrast to the relatively stable control soil profiles. Mineralization studies indicated the shortest acclimation periods and the highest initial rates of pyrene degradation occurred in soils pre-exposed to phenanthrene, or a mixture of phenanthrene and pyrene, for 14 weeks. Pre-exposure of soil microorganisms to a single dose of pyrene for the same length of time also decreased the acclimation period for the degradation of pyrene. Monthly application of either pyrene or phenanthrene to soils, however, resulted in an increase in pyrene degradative potential 6 weeks after the first pre-exposure, but a decrease in degradative potential 14 weeks after the first pre-exposure. Similar PCR-TGGE profiles were obtained from soils with comparable pyrene mineralization curves or degradative potentials. The effect of pyrene and phenanthrene contamination on soil Mycobacterium spp. community structure was examined using PCR-amplification of 16S rRNA genes with primers specific for the fast-growing group of Mycobacterium spp. and separation of phylotypes by temperature gradient gel electrophoresis (TGGE). The degradative potential of the soil microbial community was measured over time by mineralization of 14C-pyrene added to the contaminated soils. PCR-TGGE profiles, in combination with band sequencing and phylogenetic analysis of the prominent phylotypes, indicated shifts in the Mycobacterium spp. community during incubation. Reductions in species diversity and enrichments of specific populations were observed in all pyrene- and phenanthrene-treated soils, in contrast to the relatively stable control soil profiles. Mineralization studies indicated the shortest acclimation periods and the highest initial rates of pyrene degradation occurred in soils pre-exposed to phenanthrene, or a mixture of phenanthrene and pyrene, for 14 weeks. Pre-exposure of soil microorganisms to a single dose of pyrene for the same length of time also decreased the acclimation period for the degradation of pyrene. Monthly application of either pyrene or phenanthrene to soils, however, resulted in an increase in pyrene degradative potential 6 weeks after the first pre-exposure, but a decrease in degradative potential 14 weeks after the first pre-exposure. Similar PCR-TGGE profiles were obtained from soils with comparable pyrene mineralization curves or degradative potentials. |
Author | Cheung, Pui-Yi Kinkle, Brian K. |
Author_xml | – sequence: 1 givenname: Pui-Yi surname: Cheung fullname: Cheung, Pui-Yi email: cheungpi@yahoo.com – sequence: 2 givenname: Brian K. surname: Kinkle fullname: Kinkle, Brian K. |
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Keywords | Biodegradation Phylogenetic analysis PCR-TGGE 16S rDNA Mycobacterium spp PAH Microbial communities Mycobacterium Hydrocarbon Ribosomal DNA Population structure Phylogeny Polycyclic aromatic compound Polymerase chain reaction Pyrene Soils Amendment Mycobacteriales Mineralization Mycobacteriaceae Bacteria Actinomycetes Soil science Microbial community |
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Snippet | The effect of pyrene and phenanthrene contamination on soil
Mycobacterium spp. community structure was examined using PCR-amplification of 16S rRNA genes with... The effect of pyrene and phenanthrene contamination on soil Mycobacterium spp. community structure was examined using PCR-amplification of 16S rRNA genes with... |
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SubjectTerms | 16S rDNA Agronomy. Soil science and plant productions Biochemistry and biology Biodegradation Biological and medical sciences Chemical, physicochemical, biochemical and biological properties community structure Fundamental and applied biological sciences. Psychology gel electrophoresis gene amplification General agronomy. Plant production Microbial communities mineralization Mycobacterium Mycobacterium spp Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries PAH PCR-TGGE Phylogenetic analysis phylogeny Physics, chemistry, biochemistry and biology of agricultural and forest soils polluted soils polycyclic aromatic hydrocarbons polymerase chain reaction soil bacteria soil pollution Soil science Soil-plant relationships. Soil fertility. Fertilization. Amendments |
Title | Changes in Mycobacterium spp. population structure and pyrene mineralization in polycyclic aromatic hydrocarbon-amended soils |
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