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Abstracts
of Recent Publications |
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001-Asha Rani , Shalini Porwal , Rakesh Sharma , Atya
Kapley , Hemant, Purohit ,Vipin Chandra Kalia.
Institute of Genomics and Integrative Biology
(IGIB), CSIR, Delhi University Campus, Mall Road,
Delhi – 110007, India. Assessment
of microbial diversity in effluent treatment plants
by culture dependent and cul ture independent
approaches. Bioresource Technology,
2008, 1 – 10.
Microbial community structure of two distinct
effluent treatment plants (ETPs) of pesticide
and pharmaceutical industries were assessed and
defined by (i) culture dependent and culture independent
approaches on the basis of 16S rRNA gene sequencing,
and (ii)diversity index analysis – operational
taxonomic units (OTUs). A total of 38 and 44 bacterial
OTUs having 85–99% similarity with the closest
match in the database were detected among pharmaceutical
and pesticide sludge samples, respectively. Fifty
percent of the OTUs were related to uncultured
bacteria. These OTUs had a Shannon diversity index
value of 2.09–2.33 for culturables and in
the range of 3.25–3.38 for unculturables.
The high species evenness values of 0.86 and 0.95
indicated the vastness of microbial diversity
retrieved by these approaches. The dominant cultured
bacteria indicative of microbial diversity in
functional ETPs were Alcaligenes, Bacillus
and Pseudomonas. Brevundimonas, Citrobacter,
Pandoraea and Stenotrophomonas were
specific to pesticide ETP, where as Agrobacterium,
Brevibacterium, Micrococcus, Microbacterium, Paracoccus
and Rhodococcus were specific to pharmaceutical
ETP. These microbes can thus be maintained and
exploited for efficient functioning and maintenance
of ETPs.
Keywords:
Effluent; Metagenomics; Microbial diversity; Unculturable;
16S rRNA gene.
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002-Lisa
M. Gieg, Kathleen E. Duncan, and Joseph M. Suflita.
Department of Botany and Microbiology, University
of Oklahoma, 770 Van Vleet Oval, Rm. 135, Norman,
OK 73019. Bioenergy Production via Microbial
Conversion of Residual Oil to Natural Gas.
Applied and Environmental Microbiology,
74, 2008, 3022-3029.
World requirements for fossil energy are expected
to grow by more than 50% within the next25 years,
despite advances in alternative technologies.
Since conventional production methods retrieve
only about one-third of the oil in place, either
large new fields or innovative strategies for
recovering energy resources from existing fields
are needed to meet the burgeoning demand. The
anaerobic biodegradation of n-alkanes
to methane gas has now been documented in a few
studies, and it was speculated that this process
might be useful for recovering energy from existing
petroleum reservoirs. We found that residual oil
entrained in a marginal sandstone reservoir core
could be converted to methane, a key component
of natural gas, by an oil-degrading methanogenic
consortium. Methane production required inoculation,
and rates ranged from 0.15 to 0.40  mol/day/g
core (or 11 to 31  ìmol/day/g
oil), with yields of up to 3 mmol CH 4/g
residual oil. Concomitant alterations in the hydrocarbon
profile of the oil-bearing core revealed that
alkanes were preferentially metabolized. The consortium
was found to produce comparable amounts of methane
in the absence or presence of sulfate as an alternate
electron acceptor. Cloning and sequencing exercises
revealed that the inoculum comprised sulfate-reducing,
syntrophic, and fermentative bacteria acting in
concert with aceticlastic and hydrogenotrophic
methanogens. Collectively, the cells generated
methane from a variety of petroliferous rocks.
Such microbe-based methane production holds promise
for producing a clean-burning and efficient form
of energy from underutilized hydrocarbon-bearing
resources.
Keywords:Residual
Oi l , Natural Gas, biodegradation, alkanes, methane,
Microbial Conversion.
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003-
R. Vílchez, C. Pozo, M. A. Gómez,
B. Rodelas and J. González-López.
Helmholtz Center for Infection Research, Department
of Cell Biology and Immunology, Inhoffenstrabe
7, D-38124 Braunschweig, Germany. Dominance
of sphingomonads in a copper-exposed biofilm community
for groundwater treatment. Microbiology,
153, 2007, 325-337.
The structure, biological activity and microbial
biodiversity of a biofilm used for the removal
of copper from groundwater were studied and compared
with those of a biofilm grown under copper-free
conditions. A laboratory-scale submerged fixed
biofilter was fed with groundwater(2.3 l h -1)
artificially polluted with Cu(II) (15 mg l -1)
and amended with sucrose (150 mg l -1)
as carbon source. Between 73 and 90% of the Cu(II)
was removed from water during long-term operation
(over 200 days). The biofilm was a complex ecosystem,
consisting of eukaryotic and prokaryotic micro-organisms.
Scanning electron microscopy revealed marked structural
changes in the biofilm induced by Cu(II), compared
to the biofilm grown in absence of the heavy metal.
Analysis of cell-bound extracellular polymeric
substances (EPS) demonstrated a significant modification
of the composition of cell envelopes in response
to Cu (II). Transmission electron microscopy and
energydispersive X-ray microanalysis (EDX) showed
that copper bioaccumulated in the EPS matrix by
becoming bound to phosphates and/or silicates,
where as copper accu mulated only intracytoplasmically
in cells of eukaryotic microbes. Cu(II) also decreased
sucrose consumption, ATP content and alkaline
phosphatase activity of the biofilm. A detailed
study of the bacterial community composition was
conducted by 16S rRNA-based temperature gradient
gel electrophoresis (TGGE) profiling, which showed
spatial and temporal stability of the species
diversity of copper-exposed biofilms during biofilter
operation. PCR reamplification and sequencing
of 14 TGGE bands showed the prevalence of alphaproteobacteria,
with most sequences (78%) affiliated to the Sphingomonadaceae.
The major cultivable colony type in plate counts
of the copper-exposed biofilm was also identified
as that of Sphingomonas sp. These data
confirm a major role of these organisms in the
composition of the Cu (II)-removing community.
Keywords:Groundwater
treatment, biological activity, biofilm, eukaryotic
microbes, rRNA, PCR, alkaline.
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004-Catherine
A. Lozupone and Rob Knight. Departments of Molecular,
Cellular, and Developmental Biology and Chemistry
and Biochemistry, University of Colorado, Boulder,
CO 80309. Global patterns in bacterial
diversity. PNAS, 104, 2007,
11436-11440.
Microbes are difficult to culture. Consequently,
the primary source of information about a fundamental
evolutionary topic, life’s diversity, is
the environmental distribution of gene sequences.
We report the most comprehensive analysis of the
environmental distribution of bacteria to date,
based on 21,752 16S rRNA sequencescompiled from
111 studies of diverse physical environments.
We clustered the samples based on similarities
in the phylogenetic lineages that they contain
and found that, surprisingly, the major environmental
determinant of microbial community composition
is salinity rather than extremes of temperature,
pH, or other physical and chemical factors represented
in our samples. We find that sediments are more
phylogenetically diverse than any other environment
type. Surprisingly, soil, which has high species-level
diversity, has below-average phylogenetic diversity.
This work provides a framework for understanding
the impact of environmental factors on bacterial
evolution and for the direction of future sequencing
efforts to discover new lineages
Keywords:
environmental distribution, microbial ecology,
phylogenetic diversity, UniFrac, bacterial diversity.
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005-Daisuke
Inoue, Shoji Hara, Mari Kashihara, Yusaku Murai,
Erica Danzl, Kazunari Sei,Shinji Tsunoi, Masanori
Fujita, and Michihiko Ike. Division of Sustainable
Energy and Environmental Engineering, Osaka University,
2-1Yamadaoka, Suita, Osaka 565-0871, Japan. Degradation
of Bis(4- Hydroxyphenyl)Methane (Bisphenol F)
by Sphingobium yanoikuyae Strain FM-2 Isolated
from River Water. Applied and Environmental
Microbiology, 74, 2008, 352–358.
Three bacteria capable of utilizing bis(4- hydroxyphenyl)methane
(bisphenol F [BPF]) as the sole carbon source
were isolated from river water, and they all belong
to the family Sphingomonadaceae. One
of the isolates, designated Sphingobium yanoikuyae
strain FM-2, at an initial cell density of 0.01
(optical density at 600 nm) completely degraded
0.5 mM BPF within 9 h without any lag period under
inductive conditions. Degradation assays of various
bisphenols revealed that the BPF-metabolizing
system of strain FM-2 was effective only on the
limited range of bisphenols consisting of two
phenolic rings joined together through a bridging
carbon without any methyl substitution on the
rings or on the bridging structure. A BPF biodegradation
pathway was proposed on the basis of metabolite
production patterns and identification of the
metabolites. The initial step of BPF biodegradation
involves hydroxylation of the bridging carbon
to form bis(4-hydroxyphenyl) methanol, followed
by oxidation to 4,4- di hydroxybenzophenone. T
h e 4 , 4 - dihydroxybenzophenone appears to be
furtheroxidized by the Baeyer-Villiger reaction
to 4- hydroxyphenyl 4-hydroxybenzoate, which is
then cleaved by oxidation to form 4-hydroxybenzoate
and 1,4-hydroquinone. Both of the resultant simple
aromatic compounds are mineralized.
Keywords:Microbial
Conversion, alkanes, methane, Bioenergy Production,
Residual Oil, Natural Gas.
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006-Kathryn
A. Harrison, Roland Bol, Richard D. Bardgett.
Soil and Ecosystem Ecology Laboratory, Institute
of Environmental and Natural Sciences, Lancaster
University, Lancaster, LA1 4YQ, UK. Do
plant species with different growth strategies
vary in their ability to compete with soil microbes
for chemical forms of nitrogen? Soil
Biology & Biochemistry, 40, 2008, 228–237.
We used dual labelled stable isotope (13 c
and 15 N) techniques to examine how
grassland plant species with different growth
strategies vary in their ability to compete with
soil microbes for different chemical forms of
nitrogen (N), both inorganic and organic. We also
tested whether some plant species might avoid
competition by preferentially using different
chemical forms of N than microbes. This was tested
in a pot experiment where monocultures of five
co-existing grassland species, namely the grasses
Agrostis capillaris, Anthoxanthum odoratum,
Nardus stricta, Deschampsia flexuosa and
the herb Rumex acetosella, were grown
in field soil from an acid semi-natural temperate
grassland. Our data show that grassland plant
species with different growth strategies are able
to compete effectively with soil microbes for
most N forms presented to them, including inorganic
N and amino acids of varying complexity. Contrary
to what has been found in strongly N limited ecosystems,
we did not detect any differential uptake of N
on the basis of chemical form, other than that
shoot tissue of fast-growing plant species was
more enriched in 15 from N ammonium-nitrate and
glycine, than from more complex amino acids. Shoot
tissue of slowgrowing species was equally enriched
in 15 N from all these N forms. However,
all species tested, least preferred the most complex
amino acid phenylalanine, which was preferentially
used by soil microbes. We also found that while
fastgrowing plants took up more of the added N
forms than slow-growing species, this variation
was not related to differences in the ability
of plants tocompete with microbes for N forms,
as hypothesised. On the contrary, we detected
no difference in microbial biomass or microbial
uptake of 15N between fast and slow-growing plant
species, suggesting that plant traits that regulate
nutrient capture, as opposed to plant species-specific
interactions with soil microbes, are the main
factor controlling variation in uptake of N by
grassland plant species. Overall, our data provide
insights into the interactions between plants
and soil microbes that influence plant nitrogen
use in grassland ecosystems.
Keywords:
Amino acids; Grassland; Organic nitrogen; Inorganic
nitrogen; Microbial biomass; Plantmicrobial competition;
Stable isotopes; Growth strategies; Nitrogen.
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ENVIS
CENTRE Newsletter Vol.6, No 2 June 2008 |
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