Abstract:Aims: To develop a defined medium for Clostridium scatologenes ATCC 25775, which produces the malodorants 3‐methylindole (skatole) and 4‐methylphenol (p‐cresol).
Methods and Results: Clostridium scatologenes was cultured in anaerobic broth medium (pH 6·3) at 37°C containing ammonia, minerals and a commercial vitamin solution. Data indicate α‐ketoglutarate, l‐glutamate or l‐glutamine is a required nutrient that can also serve as a primary carbon and energy source. When cultured in defined medium containing gl… Show more
“…Sample preparation and detection of analytes using HPLC were achieved as previously described with modification (Kridelbaugh and Doerner 2009). Immediately prior to HPLC analysis, samples were passed over a Hypersep C18 100 mg 1 ml −1 columns (Thermo Fisher Scientific Inc., Waltham, MA, USA).…”
Section: Methodsmentioning
confidence: 99%
“…Lactobacillus sp. pep8 was routinely cultured at ambient temperature in semi-defined medium (Kridelbaugh and Doerner 2009) with 10 mmol l )1 glucose (SD-glc) with 5 ll l )1 vitamin K1 (Sigma Chem. Co, St Louis, MO, USA) and 50 ml l )1 each of mineral solutions #1 and #2 (Bryant and Burkey 1953) replacing the salt solution (Holdeman et al 1977).…”
Aims: To determine the source material and the responsible micro‐organisms of 4‐ethylphenol production in swine lagoon sediment slurries.
Methods and Results: Swine lagoon sediment was blended and incubated with tryptone–yeast extract broth containing 10 mmol l−1 each of 4‐hydroxycinnamic as well as other phenolics. 4‐Ethylphenol was only produced from 4‐hydroxycinnamic acid. Denaturing gradient gel electrophoresis analysis indicated that the microbial community was substantially altered from inclusion of 4‐hydroxycinnamic acid. Serial dilutions and selective plating were employed to isolate a culture capable of 4‐hydroxycinnamic acid conversion to 4‐ethylphenol. Morphological and ribosomal gene analysis indicated the isolate to be a Lactobacillus sp., Lactobacillus sp. pep8 converted 4‐vinylphenol, but not 4‐hydroxy‐3‐phenylpropionate, to 4‐ethylphenol and did not convert 4‐hydroxy‐3‐methoxycinnamic acid to 4‐ethyl‐2‐methoxyphenol. A p‐coumaric acid decarboxylase (pdc) gene identical to Lact. plantarum pdc genes was cloned from Lactobacillus sp. pep8.
Conclusions: Swine lagoon sediments produce 4‐ethylphenol from 4‐hydroxycinnamic acid due, in part, to the activity of Lactobacillus spp.
Significance and Impact of the Study: 4‐Ethylphenol, a malodourant of swine and beef wastes, is generated from plant materials by indigenous lactobacilli suggesting that altering the amount dietary of plant material may influence levels of 4‐ethylphenol in the wastes.
“…Sample preparation and detection of analytes using HPLC were achieved as previously described with modification (Kridelbaugh and Doerner 2009). Immediately prior to HPLC analysis, samples were passed over a Hypersep C18 100 mg 1 ml −1 columns (Thermo Fisher Scientific Inc., Waltham, MA, USA).…”
Section: Methodsmentioning
confidence: 99%
“…Lactobacillus sp. pep8 was routinely cultured at ambient temperature in semi-defined medium (Kridelbaugh and Doerner 2009) with 10 mmol l )1 glucose (SD-glc) with 5 ll l )1 vitamin K1 (Sigma Chem. Co, St Louis, MO, USA) and 50 ml l )1 each of mineral solutions #1 and #2 (Bryant and Burkey 1953) replacing the salt solution (Holdeman et al 1977).…”
Aims: To determine the source material and the responsible micro‐organisms of 4‐ethylphenol production in swine lagoon sediment slurries.
Methods and Results: Swine lagoon sediment was blended and incubated with tryptone–yeast extract broth containing 10 mmol l−1 each of 4‐hydroxycinnamic as well as other phenolics. 4‐Ethylphenol was only produced from 4‐hydroxycinnamic acid. Denaturing gradient gel electrophoresis analysis indicated that the microbial community was substantially altered from inclusion of 4‐hydroxycinnamic acid. Serial dilutions and selective plating were employed to isolate a culture capable of 4‐hydroxycinnamic acid conversion to 4‐ethylphenol. Morphological and ribosomal gene analysis indicated the isolate to be a Lactobacillus sp., Lactobacillus sp. pep8 converted 4‐vinylphenol, but not 4‐hydroxy‐3‐phenylpropionate, to 4‐ethylphenol and did not convert 4‐hydroxy‐3‐methoxycinnamic acid to 4‐ethyl‐2‐methoxyphenol. A p‐coumaric acid decarboxylase (pdc) gene identical to Lact. plantarum pdc genes was cloned from Lactobacillus sp. pep8.
Conclusions: Swine lagoon sediments produce 4‐ethylphenol from 4‐hydroxycinnamic acid due, in part, to the activity of Lactobacillus spp.
Significance and Impact of the Study: 4‐Ethylphenol, a malodourant of swine and beef wastes, is generated from plant materials by indigenous lactobacilli suggesting that altering the amount dietary of plant material may influence levels of 4‐ethylphenol in the wastes.
“…For the isolation of its genomic DNA, C. scatologenes were grown under anaerobic conditions using the medium reported previously (6). Genomic DNA was isolated using a Wizard Genomic DNA purification kit (Promega) and fragmented using Covaris S220 (Covaris, Inc.).…”
Clostridium scatologenes ATCC 25775 is a strictly anaerobic and chemolithoautotrophic acetogenic bacterium that converts syngas into multi-carbon compounds such as acetate, indole, 3-methylindole, and 4-methylphenol. Here we report the draft genome sequence of C. scatologenes ATCC 25775 (7.3 Mbp) to elucidate its metabolic pathway for syngas fermentation.
“…As medium shows positive effects on anammox process, many studies focused their attention on this area. Unfortunately, there is no systemic medium development study like those for other bacteria [48, 49]. …”
Section: Basal and Designated Medium Developmentmentioning
From discovery in the early 1990s to completion of full-scale anammox reactor, it took almost two decades to uncover the secret veil of anammox bacteria. There were three milestones during the commercialization of anammox: the development of the first enrichment culture medium, the completion of the first commercial anammox reactor, and the fast start-up of full-scale anammox plant. Till now, the culture of anammox bacteria experienced a big progress through two general strategies: (a) to start up a reactor from scratch and (b) to seed the reactor with enriched anammox sludge. The first full-scale anammox reactor took 3.5 years to realize full operation using the first approach due to several reasons besides the lack of anammox sludge. On the other hand, the first Asian anammox reactor started up in two months, thanks to the availability of anammox seed. Along with the implementation of anammox plants, anammox eventually becomes the priority choice for ammonium wastewater treatment.
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