Caldicellulosiruptor kristjanssonii sp. nov., a cellulolytic, extremely thermophilic, anaerobic bacterium.

A cellulolytic anaerobic bacterium, strain I77R1BT, was isolated from a biomat sample of an Icelandic, slightly alkaline, hot spring (78 degrees C). Strain I77R1BT was rod-shaped, non-spore-forming, non-motile and stained Gram-negative at all stages of growth. It grew at 45-82 degrees C, with an optimum growth temperature around 78 degrees C. At 70 degrees C, growth occurred at pH 5.8-8.0, with an optimum near pH 7.0. At the optimum temperature and pH, with 2 g cellobiose l-1 as substrate, strain I77R1BT had a generation time of 2 h. During growth on Avicel, strain I77R1BT produced acetate, hydrogen and carbon dioxide as major fermentation products together with small amounts of lactic acid and ethanol. The strain fermented many substrates, including cellulose, xylan, starch and pectin, but did not grow with casein peptone, pyruvate, D-ribose or yeast extract and did not reduce thiosulfate to H2S. The G+C ratio of the cellular DNA was 35 mol%. Comparative 16S rDNA analysis placed strain I77R1BT among species of Caldicellulosiruptor. The closest relative was Caldicellulosiruptor lactoaceticus. Hybridization of total DNA showed 42% hybridization to C. lactoaceticus and 22% hybridization to Caldicellulosiruptor saccharolyticus. A new species, Caldicellulosiruptor kristjanssonii sp. nov. (I77R1BT) is proposed.

Extremely thermophilic cellulolytic anaerobes from Icelandic hot springs.

Anaerobic enrichment cultures with Avicel as substrate and inoculated with biomat samples from Icelandic hot springs were cultured at 70 degrees C or 78 degrees C and examined for the presence of microorganisms that produce extracellular cellulolytic and xylanolytic enzymes. From four enrichments grown at 78 degrees C eighteen strains were isolated. Five of the strains were screened for their substrate utilization, and on the basis of differences in morphology and substrates used, the two most unique strains were selected for further characterization. All cellulolytic cultures were rod-shaped and non-sporeforming. Motility was not observed. Cells stained gram-negative at various stages of the growth phase. During growth on Avicel, most cultures produced acetate as the major fermentation product, with smaller amounts of lactic acid and ethanol. Carbon dioxide and hydrogen were also produced. The phenotypic characteristics of the enrichment cultures and of isolates are described and assessed in relation to temperature and pH in the hot spring environment. A comparison is made between Icelandic strains isolated in our laboratory and strains isolated from hot springs from other parts of the world. The biotechnological potential of this group of bacteria is briefly discussed.

Influence of pH and Temperature on Enumeration of Cellulose- and Hemicellulose-Degrading Thermophilic Anaerobes in Neutral and Alkaline Icelandic Hot Springs.

Cellulose- and hemicellulose-degrading thermophilic anaerobes were enumerated in biomat samples of various temperatures from two different hot springs in the Hverageroi area of Iceland: one spring had a pH near 7, the second had a pH near 9. The most-probable-number technique was used for enumeration of bacteria in the samples, with media at many different temperatures (37 to 90 degrees C) and two pH values (7 and 9). There were generally more xylan-degrading then cellulose-utilizing organisms in both environments. There was no growth at 80 degrees C in the neutral spring or at 37 degrees C in the alkaline spring. However, there were large numbers of both types of organisms in the alkaline spring at 80 degrees C and in the neutral spring at 37 degrees C. No cultures grew from the most-probable-number tubes inoculated with the Hverageroi samples and incubated at 90 degrees C or with media at pH 9. However, xylan-degrading cultures at 70 degrees C were enriched at pH 9 with samples from some other Icelandic hot springs.

Introduction of a de novo bioremediation ability, aryl reductive dechlorination, into anaerobic granular sludge by inoculation of sludge with Desulfomonile tiedjei.

Methanogenic upflow anaerobic granular-sludge blanket (UASB) reactors treat wastewaters at a high rate while simultaneously producing a useful product, methane; however, recalcitrant environmental pollutants may not be degraded. To impart 3-chlorobenzoate (3-CB)-dechlorinating ability to UASB reactors, we inoculated granular sludge in UASB reactors with either a pure culture of Desulfomonile tiedjei (a 3-CB-dechlorinating anaerobe) or a three-member consortium consisting of D. tiejei, a benzoate degrader, and an H2-utilizing methanogen. No degradation occurred in an uninoculated control reactor which was started with the same granular sludge, but inoculated reactors and granules from the inoculated UASB systems rapidly transformed 3-CB (54 mumol/day/g of granule biomass). After several months at a hydraulic retention time of 0.5 day, much shorter than the generation time of D. tiedjei, the reactors still dechlorinated 3-CB. This indicated that the bacteria were immobilized in the reactor granules, and by using an antibody probe for D. tiedjei, we demonstrated that this microorganism had colonized the sludge granules. These results represent the first addition of a pure culture or a defined microbial mixture to a viable waste treatment process to introduce a specific de novo degradative pathway into a granular-sludge consortium.

Description of an estuarine methylotrophic methanogen which grows on dimethyl sulfide.

Characteristics of an obligately methylotrophic coccoid methanogen (strain GS-16) previously isolated from estuarine sediment are described. Growth was demonstrated on dimethyl sulfide (DMS) or trimethylamine (TMA), but not on methane thiol, methane thiol plus hydrogen, dimethyl disulfide, or methionine. DMS-grown cells were able to metabolize DMS and TMA simultaneously when inoculated into media containing substrate levels of these compounds. However, TMA-grown cells could not metabolize [C]DMS to CH(4), although they could convert [C]methanol to CH(4). These results suggest that metabolism of DMS proceeds along a somewhat different route than that of TMA and perhaps also that of methanol. The organism exhibited doubling times of 23 and 32 h for growth (25 degrees C) in mineral media on TMA and DMS, respectively. Doubling times were more rapid ( approximately 6 h) when the organisms were grown on TMA in complex broth. In mineral media, the fastest growth on DMS occurred between pH levels of 7.0 and 8.7, at 29 degrees C, and with 0.2 to 0.4 M Na and 0.04 M Mg. Somewhat different results occurred for growth on TMA in complex broth. Cells had a moles percent G+C value of 44.5% for their DNA. Growth on DMS, TMA, and methanol yielded stable carbon isotope fractionation factors of 1.044, 1.037, and 1.063, respectively. Fractionation factors for hydrogen were 1.203 (DMS) and 1.183 (TMA).

Methanohalophilus zhilinae sp. nov., an alkaliphilic, halophilic, methylotrophic methanogen.

Methanohalophilus zhilinae, a new alkaliphilic, halophilic, methylotrophic species of methanogenic bacteria, is described. Strain WeN5T (T = type strain) from Bosa Lake of the Wadi el Natrun in Egypt was designated the type strain and was further characterized. This strain was nonmotile, able to catabolize dimethylsulfide, and able to grow in medium with a methyl group-containing substrate (such as methanol or trimethylamine) as the sole organic compound added. Sulfide (21 mM) inhibited cultures growing on trimethylamine. The antibiotic susceptibility pattern of strain WeN5T was typical of the pattern for archaeobacteria, and the guanine-plus-cytosine content of the deoxyribonucleic acid was 38 mol%. Characterization of the 16S ribosomal ribonucleic acid sequence indicated that strain WeN5T is phylogenetically distinct from members of previously described genera other than Methanohalophilus and supported the partition of halophilic methanogens into their own genus.

H(2)-CO(2) Recirculation and pH Control for Growth of Methanogens in Mass Culture.

We modified a fermentor (10-liter liquid volume) for the growth of anaerobic, H(2)-CO(2)-catabolizing bacteria. Gas in the fermentor (ca. 10% CO(2), 50% H(2), 40% CH(4)) was recirculated by a diaphragm pump. During growth, the gas composition was maintained by the addition of a mixture of 80% H(2) and 20% CO(2), and this addition was controlled by a pH auxostat. During gas addition, gas was discharged from the recirculating gas stream and was collected by the displacement of an acidified salt solution.

Isolation and characterization of a moderately halophilic methanogen from a solar saltern.

A moderately halophilic methanogenic bacterium was enriched with trimethylamine and isolated from the sediment of a solar salt pond (total dissolved solids of pond water, 250 g/liter; pH 7.5). The isolate (strain SF1, DSM 3243) was an irregular coccus which stained gram negative, with a diameter of 1 mum and a thin monolayered cell wall. The organism grew singly, in pairs, and in irregular clumps. Colonies were tannish yellow, circular, with entire edges, and about 1 mm in diameter within 1 week. Only methylamines or methanol was used for growth and methanogenesis. Most rapid growth (doubling time, 10.2 h) occurred at a temperature of 37 degrees C and a pH of 7.4. The optimum NaCl concentration was 2.1 M. Yeast extract or rumen fluid was required. The isolate was lysed by sodium dodecyl sulfate (0.1 g/liter) and was sensitive to chloramphenicol. The G+C content of the DNA was 41 (+/-1) mol%.