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ENVIRONMENTAL AND PUBLIC HEALTH MICROBIOLOGY

Aerobic Mineralization of 2,6-Dichlorophenol by Ralstonia sp. Strain RK1

Patrick Steinle, Gerhard Stucki, Rolf Stettler, Kurt W. Hanselmann
Patrick Steinle
Environmental Technology, Ciba Specialty Chemicals, CH-4133 Pratteln, and
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Gerhard Stucki
Environmental Technology, Ciba Specialty Chemicals, CH-4133 Pratteln, and
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Rolf Stettler
Institute of Plant Biology/Microbiology, University of Zurich, Zurich, Switzerland
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Kurt W. Hanselmann
Institute of Plant Biology/Microbiology, University of Zurich, Zurich, Switzerland
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DOI: 10.1128/AEM.64.7.2566-2571.1998
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    Fig. 1.

    Growth characteristics of Ralstonia sp. strain RK1 on 2,6-DCP as determined with batch cultures. (A) Mineralization of 60 μM 2,6-DCP by Ralstonia sp. strain RK1 in a batch culture. Symbols: □, 2,6-DCP concentration; •, chloride ion concentration; ▴, CFU per milliliter. (B) Lag phase ofRalstonia sp. strain RK1 with increasing initial concentrations of 2,6-DCP. (C) Growth rate of Ralstonia sp. strain RK1 at different initial concentrations of 2,6-DCP. Solid line, curve obtained with the Monod equation (23) with a maximal growth rate of 0.082 h−1 and a Ksof 24.1 μM obtained by Lineweaver-Burk linearization of the first five data points; dashed line, prediction from Haldane equation (Monod with inhibition; Ki = 787 μM, as determined by linear regression of the last four data points). μ, growth rate. Error bars represent standard deviations from two cultures. The samex axis applies to panels B and C.

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    Fig. 2.

    Mineralization of high concentrations of 2,6-DCP in fixed-bed reactor 1. Symbols: ▴, 2,6-DCP feed concentration; ▪, 2,6-DCP effluent concentration; ◊, chloride ion effluent concentration. The arrows indicate experimental changes described in the text. d, days.

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    Fig. 3.

    Mineralization of low concentrations of 2,4-DCP, 2,6-DCP, and 2,4,6-TCP with short HRTs in fixed-bed reactor 2. (A) Symbols: ▪, feed concentration of chlorophenols (CP); ▴, effluent concentration of chlorophenols; ⧫, HRT. (B) Effluent concentrations of the three chlorophenol congeners. Symbols: □, 2,4,6-TCP; ▵, 2,6-DCP; ⧫, 2,4-DCP. (C) Reactor performance. Symbols: □, volumetric degradation (vol. deg.) yield; ▴, conversion coefficient [(feed concentration − outflow concentration)/feed concentration]. The same x axis applies to panels A through C. d, days; lr, liter reactor volume.

Tables

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  • Table 1.

    Taxonomic features of genera and species related toRalstonia sp. strain RK1

    TaxonGelatin lysedNitrate reductaseAcid formed from glucoseGrowth on d-glucoseGrowth on gluconateGrowth on adipatePigment excretionFlagellum(a)
    Ralstonia sp. strain RK1−b−−−++−−
    Ralstonia eutrophaa−+−−++−+
    Alcaligenes faecalisa−−−−−−−+
    Burkholderiaad+−+++++
    Pseudomonas pickettiia−+++++−+
    • ↵a Data from reference18.

    • ↵b −, less than 10% of all strains tested are positive; +, more than 90% of all strains tested are positive; d, between 10 and 90% of all strains tested are positive.

  • Table 2.

    Species related to Ralstonia sp. strain RK1

    TaxonEMBL accession no.% 16S rRNA homology with Ralstonia sp. strain RK1
    Ralstonia sp. strain RK1AJ002302100
    Alcaligenes sp.L3165097.3
    Ralstonia eutrophaM3202195.7
    Pseudomonas solanacearumX6703593.3
    Pseudomonas pickettiiL3736792.7
    Burkholderiasp.X9218890.7
    Alcaligenes faecalisD8800886.8
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Aerobic Mineralization of 2,6-Dichlorophenol by Ralstonia sp. Strain RK1
Patrick Steinle, Gerhard Stucki, Rolf Stettler, Kurt W. Hanselmann
Applied and Environmental Microbiology Jul 1998, 64 (7) 2566-2571; DOI: 10.1128/AEM.64.7.2566-2571.1998

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Aerobic Mineralization of 2,6-Dichlorophenol by Ralstonia sp. Strain RK1
Patrick Steinle, Gerhard Stucki, Rolf Stettler, Kurt W. Hanselmann
Applied and Environmental Microbiology Jul 1998, 64 (7) 2566-2571; DOI: 10.1128/AEM.64.7.2566-2571.1998
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KEYWORDS

Chlorophenols
Gram-Negative Aerobic Rods and Cocci

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