関: Sphingomonadaceae

Wikipedia preview

出典(authority):フリー百科事典『ウィキペディア（Wikipedia）』「2015/08/28 16:55:04」(JST)

wiki en

Sphingomonas was defined in 1990 as a group of Gram-negative, rod-shaped, chemoheterotrophic, strictly aerobic bacteria. They possess ubiquinone 10 as their major respiratory quinone, contain glycosphingolipids (GSLs) instead of lipopolysaccharide (LPS) in their cell envelopes, and typically produce yellow-pigmented colonies.^[1]

By 2001, the genus included more than 20 species that were quite diverse in terms of their phylogenetic, ecological, and physiological properties. As a result, the Sphingomonas were subdivided into four genera: Sphingomonas, Sphingobium, Novosphingobium, Sphingosinicella, and Sphingopyxis. These genera are commonly referred to collectively as sphingomonads. The sphingomonads are widely distributed in nature, having been isolated from many different land and water habitats, as well as from plant root systems, clinical specimens, and other sources; this is due to their ability to survive in low concentrations of nutrients, as well as to metabolize a wide variety of carbon sources. Numerous strains have been isolated from environments contaminated with toxic compounds, where they display the ability to utilize the contaminants as nutrients.^[1]

Some of the sphingomonads (especially Sphingomonas paucimobilis) also play a role in human disease, primarily by causing a range of mostly nosocomial, non-life-threatening infections that typically are easily treated by antibiotic therapy.^[2]^[3]

Due to their biodegradative and biosynthetic capabilities, sphingomonads have been utilised for a wide range of biotechnological applications, from bioremediation of environmental contaminants to production of extracellular polymers such as sphingans (e.g., gellan, welan, and rhamsan) used extensively in the food and other industries^{[citation needed]}. The shorter carbohydrate moiety of GSL compared to that of LPS results in the cell surface being more hydrophobic than that of other Gram-negative bacteria, probably accounting for both Sphingomonas' sensitivity to hydrophobic antibiotics and its ability to degrade hydrophobic polycyclic aromatic hydrocarbons.^[1] One strain, Sphingomonas sp. 2MPII, can degrade 2-methylphenanthrene.^[4] In May 2008, Daniel Burd, a 16-year-old Canadian, won the Canada-Wide Science Fair in Ottawa after discovering that Sphingomonas can degrade over 40% of the weight of plastic bags (Polyethylene) in less than three months.^[5]

A Sphingomonas sp. strain BSAR-1 expressing a high activity alkaline phosphatase (PhoK) has also been applied for bioprecipitation of uranium from alkaline solutions. The precipitation ability was enhanced by overexpressing PhoK protein in E. coli. This is the first report of bioprecipitation of uranium under alkaline conditions.^[6]

References

^ ^a ^b ^c Sphingomonas, Microbewiki
^ Sphingomonas paucimobilis: a persistent Gram-negative nosocomial infectious organism., Ryan MP, Adley CC., J Hosp Infect. 2010 Jul;75(3):153-7. doi: 10.1016/j.jhin.2010.03.007.
^ Sphingomonas paucimobilis Bloodstream Infections Associated with Contaminated Intravenous Fentanyl, Lisa L. Maragakis, Romanee Chaiwarith, Arjun Srinivasan, Francesca J. Torriani, Edina Avdic, Andrew Lee, Tracy R. Ross, Karen C. Carroll, and Trish M. Perl, Emerging Infectious Diseases Vol. 15, No. 1, January 2009
^ G.M. Ni'matuzahroh; M. Gilewicz; M. Guiliano & J.C. Bertrand (May 1999). "In-vitro study of interaction between photooxidation and biodegradation of 2-methylphenanthrene by Sphingomonas sp 2MPII". Chemosphere 38 (11): 2501–2507. doi:10.1016/S0045-6535(98)00456-1. ISSN 0045-6535. PMID 10204235.
^ TheRecord.com—CanadaWorld—WCI student isolates microbe that lunches on plastic bags
^ K.S. Nilgiriwala; A. Alahari; A. S. Rao & S.K. Apte (Sep 2008). "Cloning and Overexpression of Alkaline Phosphatase PhoK from Sphingomonas sp. Strain BSAR-1 for Bioprecipitation of Uranium from Alkaline Solutions". Applied and Environmental Microbiology 74 (17): 5516–5523. doi:10.1128/AEM.00107-08. ISSN 1098-5336. PMC 2546639. PMID 18641147.

External links

Article describing the discovery of Sphingomonas as a biodegrader of plastic bags Kawawada, Karen, The Record (May 22, 2008).

English Journal

Fungal-bacterial consortia increase diuron degradation in water-unsaturated systems.

Ellegaard-Jensen L, Knudsen BE, Johansen A, Albers CN, Aamand J, Rosendahl S.SourceDepartment of Biology, Copenhagen University, Universitetsparken 15, DK-2100 Copenhagen Ø, Denmark; Department of Geochemistry, Geological Survey of Denmark and Greenland (GEUS), Øster Voldgade 10, DK-1350 Copenhagen K, Denmark. Electronic address: Leael@bio.ku.dk.
The Science of the total environment.Sci Total Environ.2014 Jan 1;466-467:699-705. doi: 10.1016/j.scitotenv.2013.07.095. Epub 2013 Aug 25.
Bioremediation of pesticide-polluted soil may be more efficient using mixed fungal-bacterial cultures rather than the individual strains alone. This may be due to cooperative catabolism, where the first organism transforms the pollutant to products which are then used by the second organism. In addi
PMID 23973535

Genotypic diversity and antibiotic resistance in Sphingomonadaceae isolated from hospital tap water.

Narciso-da-Rocha C, Vaz-Moreira I, Manaia CM.SourceCBQF - Centro de Biotecnologia e Química Fina - Laboratório Associado, Escola Superior de Biotecnologia, Universidade Católica Portuguesa/Porto, Rua Dr. António Bernardino Almeida, Porto 4200-072, Portugal.
The Science of the total environment.Sci Total Environ.2014 Jan 1;466-467:127-35. doi: 10.1016/j.scitotenv.2013.06.109. Epub 2013 Jul 25.
The aim of this study was to infer about the modes and extent of dispersion of Sphingomonadaceae via tap water. Sphingomonadaceae isolated from tap water samples in different places of a hospital were compared, based on intra-species genetic variability and antibiotic resistance phenotypes. These is
PMID 23892027

Engineering bacteria for bioremediation of persistent organochlorine pesticide lindane (γ-hexachlorocyclohexane).

Chaurasia AK, Adhya TK, Apte SK.SourceMolecular Biology Division, Bhabha Atomic Research Centre, Trombay, Mumbai 400 085, India; Samsung Biomedical Research Institute, School of Medicine, SKKU, Suwon 440 746, South Korea.
Bioresource technology.Bioresour Technol.2013 Dec;149:439-45. doi: 10.1016/j.biortech.2013.09.084. Epub 2013 Sep 29.
Strategies were designed for bioremediation of the highly persistent toxic pesticide γ-hexachlorocyclohexane (γ-HCH) or lindane from the environment. Lindane caused the loss of stress-protective chaperone GroEL, and inhibited photosynthesis, respiration and nitrogen-fixation in Anabaena, resulting
PMID 24135568

Japanese Journal

The lin Genes for γ-Hexachlorocyclohexane Degradation in Sphingomonas sp. MM-1 Proved to Be Dispersed across Multiple Plasmids

TABATA Michiro,ENDO Ryo,ITO Michihiro,OHTSUBO Yoshiyuki,KUMAR Ashwani,TSUDA Masataka,NAGATA Yuji
Bioscience, Biotechnology, and Biochemistry 75(3), 466-472, 2011
… A γ-hexachlorocyclohexane (HCH)-degrading bacterium, Sphingomonas sp. …
NAID 130000645248

アルギン酸代謝酵素の構造と機能

落合秋人,高瀬隆一,三上文三,橋本渉,村田幸作
ビタミン 84(11), 525-531, 2010-11-25
… A gram-negative and alginate-assimilating bacterium, Sphingomonas sp. …
NAID 110007989343

Related Pictures

★リンクテーブル★

リンク元	「スフィンゴモナス」「Sphingomonadaceae」「スフィンゴモナス属」
拡張検索	「Sphingomonas属」

「スフィンゴモナス」

Sphingomonas
Scientific classification
Kingdom:	Bacteria
Phylum:	Proteobacteria
Class:	Alphaproteobacteria
Order:	Sphingomonadales
Family:	Sphingomonadaceae
Genus:	Sphingomonas
Species
	Sphingomonas abaci; Sphingomonas adhaesiva; Sphingomonas aerolata; Sphingomonas aestuarii; Sphingomonas alaskensis; Sphingomonas alpina; Sphingomonas aquatilis; Sphingomonas aromaticivorans; Sphingomonas asaccharolytica; Sphingomonas astaxanthinifaciens; Sphingomonas aurantiaca; Sphingomonas azotifigens; Sphingomonas baekryungensis; Sphingomonas capsulata; Sphingomonas changbaiensis; Sphingomonas chlorophenolica; Sphingomonas chungbukensis; Sphingomonas cloacae; Sphingomonas cynarae; Sphingomonas desiccabilis; Sphingomonas dokdonensis; Sphingomonas echinoides; Sphingomonas elodea; Sphingomonas endophytica; Sphingomonas faeni; Sphingomonas fennica; Sphingomonas formosensis; Sphingomonas ginsengisoli; Sphingomonas ginsenosidimutans; Sphingomonas glacialis; Sphingomonas haloaromaticamans; Sphingomonas hankookensis; Sphingomonas herbicidovorans; Sphingomonas histidinilytica; Sphingomonas indica; Sphingomonas insulae; Sphingomonas japonica; Sphingomonas jaspsi; Sphingomonas jejuensis; Sphingomonas jinjuensis; Sphingomonas kaistensis; Sphingomonas koreensis; Sphingomonas laterariae; Sphingomonas leidyi; Sphingomonas macrogoltabidus; Sphingomonas mali; Sphingomonas melonis; Sphingomonas molluscorum; Sphingomonas mucosissima; Sphingomonas natatoria; Sphingomonas oligophenolica; Sphingomonas oryziterrae; Sphingomonas panni; Sphingomonas parapaucimobilis; Sphingomonas paucimobilis; Sphingomonas phyllosphaerae; Sphingomonas pituitosa; Sphingomonas polyaromaticivorans; Sphingomonas pruni; Sphingomonas rosa; Sphingomonas roseiflava; Sphingomonas rubra; Sphingomonas sanguinis; Sphingomonas sanxanigenens; Sphingomonas sediminicola; Sphingomonas soli; Sphingomonas starnbergensis; Sphingomonas stygia; Sphingomonas subarctica; Sphingomonas suberifaciens; Sphingomonas subterranea; Sphingomonas taejonensis; Sphingomonas terrae; Sphingomonas trueperi; Sphingomonas ursincola; Sphingomonas wittichii; Sphingomonas xenophaga; Sphingomonas yabuuchiae; Sphingomonas yanoikuyae; Sphingomonas yunnanensis