Literature DB >> 16348772

Persistence of free plasmid DNA in soil monitored by various methods, including a transformation assay.

G Romanowski1, M G Lorenz, G Sayler, W Wackernagel.   

Abstract

The persistence and stability of free plasmid pUC8-ISP DNA introduced into 10-g samples of various soils and kept at 23 degrees C were monitored over a period of 60 days. The soils were sampled at a plant science farm and included a loamy sand soil (no. 1), a clay soil (no. 2), and a silty clay soil (no. 3). Four different methods allowed monitoring of (i) the production of acid-soluble radioactive material from [H]thymidine-labeled plasmid DNA, (ii) the decrease of hybridizing nucleotide sequences in slot blot analysis, (iii) the loss of plasmid integrity measured by Southern hybridization, and (iv) the decay of the biological activity as determined by transformation of Ca-treated Escherichia coli cells with the DNA extracted from soil. Acid-soluble material was not produced within the first 24 h but then increased to 45% (soil no. 1), 27% (soil no. 2), and 77% (soil no. 3) until the end of incubation. A quite parallel loss of material giving a slot blot hybridization signal was observed. Southern hybridization indicated that after 1 h in the soils, plasmid DNA was mostly in the form of circular and full-length linear molecules but that, depending on the soil type, after 2 to 5 days full-length plasmid molecules were hardly detectable. The transforming activity of plasmid DNA reextracted from the soils followed inactivation curves over 2 to 4 orders of magnitude and dropped below the detection limit after 10 days. The inactivation was slower in soil no. 2 (28.2-h half-life time of the transforming activity of a plasmid molecule) than in soils no. 3 (15.1 h) and no. 1 (9.1 h). The studies provide data on the persistence of free DNA molecules in natural bacterial soil habitats. The data suggest that plasmid DNA may persist long enough to be available for uptake by competent recipient cells in situ.

Entities:  

Year:  1992        PMID: 16348772      PMCID: PMC183041          DOI: 10.1128/aem.58.9.3012-3019.1992

Source DB:  PubMed          Journal:  Appl Environ Microbiol        ISSN: 0099-2240            Impact factor:   4.792


  20 in total

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3.  A rapid alkaline extraction procedure for screening recombinant plasmid DNA.

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5.  Genomic sequencing.

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7.  Production of extracellular nucleic acids by genetically altered bacteria in aquatic-environment microcosms.

Authors:  J H Paul; A W David
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8.  Release of transforming plasmid and chromosomal DNA from two cultured soil bacteria.

Authors:  M G Lorenz; D Gerjets; W Wackernagel
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10.  Adsorption of DNA to sand and variable degradation rates of adsorbed DNA.

Authors:  M G Lorenz; W Wackernagel
Journal:  Appl Environ Microbiol       Date:  1987-12       Impact factor: 4.792

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  23 in total

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Authors:  Jamie S Young; Eamonn Gormley; Elizabeth M H Wellington
Journal:  Appl Environ Microbiol       Date:  2005-04       Impact factor: 4.792

3.  Natural Transformation of Acinetobacter calcoaceticus by Plasmid DNA Adsorbed on Sand and Groundwater Aquifer Material.

Authors:  B Chamier; M G Lorenz; W Wackernagel
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4.  Degradation and half-life of DNA present in biomass from a genetically-modified organism during land application.

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5.  Laboratory-scale evidence for lightning-mediated gene transfer in soil.

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6.  Use of polymerase chain reaction and electroporation of Escherichia coli to monitor the persistence of extracellular plasmid DNA introduced into natural soils.

Authors:  G Romanowski; M G Lorenz; W Wackernagel
Journal:  Appl Environ Microbiol       Date:  1993-10       Impact factor: 4.792

7.  Inducible cell lysis system for the study of natural transformation and environmental fate of DNA released by cell death.

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8.  Interference of humic acids and DNA extracted directly from soil in detection and transformation of recombinant DNA from bacteria and a yeast.

Authors:  C C Tebbe; W Vahjen
Journal:  Appl Environ Microbiol       Date:  1993-08       Impact factor: 4.792

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10.  Genetic exchange in soil between introduced chlorobenzoate degraders and indigenous biphenyl degraders.

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