chapter 7 microbial dna extraction from soil (culture...
TRANSCRIPT
Chapter 7
Microbial DNA extraction
from soil (culture
independent) and its PCR
amplification by different
methods
7.1 Introduction
The diversity of microorganisms in soil is critical to the maintenance of good soil health, because
microorganisms are involved in many important functions such as soil formation, toxin removal,
and elemental cycles of C, N, P, and others. Previously, studies on the development of “bacterial
communities required the isolation of the organisms from sample, followed by a series of
morphological and biochemical tests to identify the bacteria. However, the majorities of bacteria
in the environment are not readily cultivable” (Moyer et al.1994, Marchesi et al. 1998).
“Furthermore, culture dependent community structure analysis produce spatial and heavily
biased results. Since in the mid 1980s, the use of 16S ribosomal nucleic acid–(rRNA) techniques
has facilitated the molecular identification of a wide variety of as yet uncultivated
microorganisms and novel microbial groups in various environments”( Torsvik et al. 1990 ).
There are two approaches for the extraction of DNA from soil: the bacterial fractionation
approach, involves the separation of bacterial cells from the bulk of the soil prior to cell lysis and
recovery of bacterial community DNA, and the direct lysis approach, bacterial cells are lysed
directly in the presence of the soil matrix. Direct lysis methods are more often used than cell
extraction ones because they are less time consuming and give better recovery, resulting in an
extracted DNA more representative of the whole microbial community present in the sample.
“The major disadvantage of direct lysis is that the method also extracts other organic soil
components, such as humic and fluvic acids. Since these contaminants can prevent subsequent
molecular analysis, such as restriction digestion, Polymerase Chain Reaction (PCR), and
cloning” (Olson et al., 1991), an extensive purification steps were then required to successfully
amplify a PCR product, including CsCl-ethidium bromide density gradient centrifugation or the
use of commercial reagents. These steps increase both the complexity and the cost of the
technique. This paper describes in detail a method for extracting DNA from soil which involves
minimal purification prior to PCR amplification. An additional advantage is that only 1 gm of
soil sample is required results in analyzing a soil sample in a short span of time. Thus a PCR
product was obtained rapidly and inexpensively from small amount of soil.
Several methods for extracting microbial DNA from soil have been described. “Many of
these techniques employ extensive purification steps to ensure that the DNA is suitable for use in
the polymerase chain reaction” (Roose-Amsaleg, et al, 2001). Thus, selection of an appropriate
DNA extraction and purification procedure from among the procedures that have been described
to date remains a major problem in the application of molecular techniques to studies of soil and
sediment microbial communities. The objective of this study is to evaluate different methods for
extracting high yield of high-purity microbial community DNA using single soil samples
emphasized PCR amplification in evaluating DNA purity because Taq polymerase is sensitive to
humic contaminants. Amplification of DNA from soil is often inhibited by co-purified
contaminants. A rapid, inexpensive, large-scale DNA extraction methods involving minimal
purification have been developed that is applicable to soil. DNA is also suitable for PCR
amplification using various DNA targets. DNA was extracted from 1g of soil using direct lysis
with liquid nitrogen and SDS followed by sodium acetate precipitation, polyethylene glycol
precipitation, phenol extraction and isopropanol precipitation. This method was compared to
other DNA extraction methods with regard to DNA purity and size.
7.2 Material and methods
The soil sample was collected from Kukrail Forest. Soil samples were immediately placed on dry
ice, mixed, and then stored at -20°C prior to DNA extraction. Subsample (approximately 1 g) of
soil was set aside for use in microbial analysis.
Six DNA extraction methods were evaluated in this study using single type of soil. Three
methods were Mannitol-based DNA extraction method grinded with liquid nitrogen and others
were based on PEG-NaCl method without liquid nitrogen, bead beating without liquid nitrogen
and Sodium phosphate -SDS based method.
7.2.1 DNA extraction using mannitol method with liquid nitrogen
Three different protocols are used in this method which gives a very good yield of DNA
directly isolated from soil sample. Take 1:10 ratio of extraction buffer with respect to soil sample
i.e. 10 ml of isolation buffer is added in 1g of soil sample in all three protocols of this method.
7.2.1.1 Protocol I: Using PEG/NaCl with mannitol
DNA was extracted from soil samples by directly lysing the cells with liq.N2.Soil sample of 1 gm
were mixed with 10 ml of DNA extraction buffer (1M Tris-HCL [pH 8.0], 5 M NaCl, 0.5 M
EDTA (pH-7.8), 10 % CTAB , 20 % SDS and rest of volume Mannitol ) in centrifuge tubes and
incubated for 1 hr at 65°C with occasional stirring. The supernatant were collected after
centrifugation at 1000 rpm for 15 min at room temperature and mixed with half volume PEG and
1 volume of NaCl and incubated at 4 C for overnight. The pellet was recovered by
centrifugation at 12,000 rpm and dissolved in 1ml of TE buffer (Tris-HCl 10 mM, Na2EDTA 1
mM; pH 8.0). The DNA sample was then extracted with PCI; aqueous layer was taken in fresh
tube and allowed to precipitate at 4 C with 1/10th volume of 3 M sodium acetate (pH 5.2) and 2
volumes ethanol. The pellet was redissolved in 50 μl TE buffer.
7.2.1.2 Protocol II: Using Phenol/Chloroform/Isoamylalcohol (P/C/I), with mannitol
DNA was extracted from soil samples by directly lysing the cells with liq.n2.Soil sample of 1 gm
were mixed with 10 ml of DNA extraction buffer (1M Tris-HCL [pH 8.0], 5 M NaCl, 0.5 M
EDTA (pH-7.8), 10 % CTAB , 20 % SDS and rest of volume Mannitol) in centrifuge tubes and
incubated for 1 hr at 65° C with occasional stirring. After centrifugation, the supernatant was
extracted with an equal volume of PCI followed by centrifugation at 12,000 rpm at 4 C.
Aqueous layer was taken and allowed to precipitate overnight at 4 C with 1/10th
volume of 3 M
sodium acetate (pH 5.2) and 2 volumes ethanol. The pellet was recovered by centrifugation at
12,000 rpm and dissolved in 50 μl TE buffer.
7.2.1.3 Protocol III: Using CTAB with mannitol
DNA was extracted from soil samples by directly lysing the cells with liq.n2.Soil sample of 1 gm
were mixed with 10 ml of DNA extraction buffer (1M Tris-HCL [pH 8.0], 5 M NaCl, 0.5 M
EDTA (pH-7.8), 10 % CTAB , 20 % SDS and rest of volume Mannitol) in centrifuge tubes and
incubated for 1 hr at 65° C with occasional stirring. After centrifugation, 50 µl of 5 M NaCl and
50 µl of 10 % CTAB (Cetrimide) (made in 0.7 M NaCl solution CTAB were added to the
supernatant and incubated at room temperature for 10 min. This was followed by addition of
equal volume of PCI and centrifugation at 12,000 rpm 4 C. Aqueous layer was taken and
allowed to precipitate overnight at 4 C with 1/10th
volume of 3 M sodium acetate (pH 5.2) and
2 volumes ethanol. The pellet was recovered by centrifugation at 12,000 rpm and dissolved in 50
μl TE buffer.
7.2.2 DNA extraction using PEG / NaCl method without liquid nitrogen
DNA was extracted from soil samples by directly lysing the cells with liq.N2 .Soil sample of 1
gm were mixed with 10 ml of DNA extraction buffer (120 mM Na2HPO4 (pH 6.8), 5 % SDS
(w/v) and 0.02 g PVPP) in centrifuge tubes and incubated for 1 hr at 65°C with occasional
stirring. The supernatant were collected after centrifugation at 1000 rpm for 15 min at room
temperature and mixed with half volume PEG and 1 volume of NaCl and incubated at 4 C for
overnight. The pellet was recovered by centrifugation at 12,000 rpm and dissolved in 1ml of TE
buffer (Tris-HCl 10 mM, Na2EDTA 1 mM; pH 8.0). The DNA sample was then extracted with
PCI; aqueous layer was taken in fresh tube and allowed to precipitate at 4 C with 1/10th volume
of 3 M sodium acetate (pH 5.2) and 2 volumes ethanol. The pellet was redissolved in 50 μl TE
buffer.
7.2.3 DNA extraction using bead beating without liquid nitrogen
Extraction buffer (120 mM K2HPO4 pH 8.0, 5 % CTAB in 120 mM K2HPO4 pH 8.0 CTAB,
0.50 ml PCI) was mixed with 1g (wet weight) of soil. Glass beads 0.5g, were added and the
sample blended in a Bead-Beater for 2 minutes with intermittent cooling on ice and centrifuge 15
min at maximum speed (10,000 rpm). The sample was incubated at 65° C for 1 h, transferred to
centrifuge tubes and centrifuged at 8000 rpm for 15 min. The supernatant was collected, and the
soil pellet re-extracted with further extraction buffer (10 ml), incubation at 65º C for 10 min and
centrifugation as above. Supernatants were transferred to centrifuge tubes containing 1 volume
of Chloroform and isoamyl alcohol and vortexed. The supernatant was collected by centrifuge
for 10 min at 12000 rpm 0.1 volume 3 M NaAc and 1 volume ethanol (cool), let the DNA to
precipitate for 2 h on ice. Centrifuge 15 min, 12,000 rpm and wash the pellet with 70 % ethanol,
Add 50 µL TE buffer into the DNA pellet.
7.2.4 DNA extraction using sodium phosphate buffer & SDS method with bead beating &
liquid nitrogen
Soil sample of 1 g was introduced into a 25 mL erlenmeyer flask containing 10 ml sodium
phosphate buffer (and 0.1 % Tween 80, pH 7). The mixture was incubated under constant
agitation overnight at room temperature. The supernatant from this suspension was centrifuged at
5000 rpm for 10 min. The pellet was washed four times with TE buffer 50/50 ( 50 mM Tris-HCl,
50 mM EDTA, pH 8 ) at 3000 rpm for 3 min and the cells were lysed mechanically by
maceration of the liquid nitrogen-frozen pellet. The macerate was transferred to a 15-mL
centrifuge tube to which 2 mL TE buffer 50/50 and an equivalent volume of phenol-chloroform-
isoamyl alcohol (25:24:1) were added, and the mixture was centrifuged at 5000 rpm for 10 min.
DNA from the collected supernatant was precipitated by adding 0.7 vol. ice-cold isopropanol and
10 vol. 3 M sodium acetate and chilling this mixture for 2 h at -20°C.Another centrifugation at
5000 rpm for 10 min yielded a DNA pellet, which was washed two times with ice-cold 70 %
ethanol and once with 95 % ethanol. The DNA was resuspended in 50 µL TE buffer (10 mM
Tris-HCl, 0.1 mM EDTA, pH 8.0).
7.2.5 Determination of purity and yield of DNA
The concentration of the DNA in the sample can be measured by monitoring the absorbance of a
dilute solution of the sample at 260 nm, and can be calculated based on the value of 1.0 A260 unit
= 50 μg/ml of DNA, taking into account the dilution factor of the sample (Sambrook et al.,
1989). Purity of the DNA was determined by taking absorbance reading at 230, 260 and 280 nm.
A260 /A280 and A260 /A230 ratios were calculated to evaluate levels of protein and humic acid
impurities respectively in both extraction methods.
7.2.6 PCR amplification of soil extracted DNA
Soil DNA was amplified by PCR (BIORAD). Each 25 l PCR mixture contained 1 l template
DNA, 2.5 l 1x PCR buffer, 1 l of each deoxyribonucleoside triphosphate (dNTP), 1 l of
forward and reverse primers and 0.5 l Taq DNA polymerase The primers used to amplify SSU
ribosomal genes (FP1) 5’-TGGGGAGCAAACAGGATTAG-3’ and (RP1) 5’-
TAAGGTTCTTCGCTTGCTT-3’.The amplification cycle consisted of an initial denaturation
step of 5 min at 94 C, followed by 35 cycles of 1 min at 94 C (denaturation), 1 min at 59 C
(annealing) and 2 min at 72 C (extension), with a final extension step for 10 min at 72 C
Successful amplification was confirmed by agarose gel electrophoresis and ethidium bromide
staining. An aliquot (6 μl) of each amplification reaction was analysed on 0,8 % w/v agarose gels
cast and run in TAE buffer (pH 8.2) .Gels were stained with ethidium bromide and photographed
using transmitted U.V. light using BIO RAD Gel DocTM XR. A 100 base pair marker was
included on gel.
7.3 Results
DNA extraction from soil has three requirements; extraction of high molecular weight DNA;
extraction of DNA free from inhibitors for subsequent molecular biological manipulations to be
performed; representative lysis of microorganisms. It is important to select an extraction and
purification method, which yields DNA of suitable quantity and purity. The extraction methods
are strongly influenced by several parameters, such as incomplete cell lysis, DNA sorption to soil
surfaces, extraction of humic contaminants, and DNA degradation. In this chapter, we tested a
number of DNA extraction methods for their ability to fulfill these requirements. Here six
methods are considered for isolation of DNA and compared. The inclusion of Mannitol in the
extraction buffer has been proved to increase the efficiency of extraction. Further purification of
DNA has been tried with three different procedures, viz., by using PEG-NaCl, CTAB and PCI.
The size of extracted DNA ranged from less than 500 bp to greater than 20 kb in size. Higher
molecular weight DNA is desirable for PCR since the greater the size of the DNA, the less likely
is the formation of chimeras during PCR, hence better for microbial diversity analysis. .
7.3.1 Metagenomic DNA from soil
Various DNA isolation protocols are compared on the basis of DNA yield (Table 7.1). DNA
yield was increased by using liquid nitrogen and bead beating. It was further improved by adding
mannitol in the extraction buffer. The SDS method has been the most widely used cell lysis
treatment from DNA extraction from pure cultures, soils and sediments. Trevors et al., (1992)
found that the SDS-based cell lysis protocol gave the highest DNA yields in comparison with
freezing-thawing lysis protocols. More et al., (1994) showed that the mechanical treatment was
more effective and less selective than chemical lysis, attributed to increased cell lysis. According
to Frostegard et al., (1999) grinding homogenizes the soil and increase the release of bacteria
from inner compartment, making them available for subsequent lysis.
1 2 3 4 5 6 7
Figure 7.1 Visualization of soil DNA showing smear by respective methods. lane 1 Marker;
lane 2 Mannitol -PEG/NaCl method; lane 3- Mannitol P/C/I; lane 4 Mannitol - CTAB; lane
5-DNA extraction using PEG / NaCl Method without Liquid Nitrogen; lane 6 -DNA
extraction using Sodium Phosphate buffer & SDS method with bead beating & Liquid
Nitrogen; and lane 7 -DNA extraction using bead beating without liq. N2.
7.3.2 Determination of purity and yield of DNA
Table 7.1: Amount of DNA extracted from various isolation protocols
DNA Extraction Protocol Amount
(mg/ml)
DNA extraction by PEG / NaCl without liq. N2 0.75
DNA extraction using Phosphate buffer with bead beating without liq. N2
0.80
DNA extraction using Na2HPO4,buffer & SDS method with bead beating &
liq N2
1.25
DNA extraction by Mannitol method with Liq N2
Protocol I: 2.25
Protocol II: 2.50
Protocol III: 2.75
Since organic matter is the major source of inhibitors that may be co-extracted from soil
with the microbial DNA. In particular, humic acids pose a considerable problem and will
interfere in enzymatic manipulations of DNA. The humic materials in soil have similar size and
charge characteristics to DNA resulting in their co-purification, evident by the extractions being
brown in colour. Humic contaminants also interfere in DNA quantitation since they exhibit
absorbance at both 230 nm and at 260 nm, the later used to quantitate DNA. This characteristic
can be used to determine the level of contamination of humic material by examining absorbance
ratios. A high 260/230 ratio (>2) is indicative of pure DNA, while a low ratio is indicative of
humic acid contamination and a high 260/280 ratio (>1.7) is indicative of pure DNA, while a low
ratio is indicative of protein contamination.
Table 7.2 Comparison of DNA extraction methods for humic acid contamination
DNA Extraction Protocol A 260/230 A 260/280
DNA extraction by PEG / NaCl without liq. N2 1.10 1.25
DNA extraction using Phosphate buffer with bead beating
without liq. N2
1.20 1.42
DNA extraction using Na2HPO4,buffer & SDS method with
bead beating & liq N2
1.24 1.69
DNA extraction by Mannitol method with liq N2
Protocol I: 1.89 1.80
Protocol II: 1.94 1.85
Protocol III: 2.05 1.85
When the DNA extraction methods were compared (Table 7.2), the bead beating method and
PEG / NaCl Method with Liquid Nitrogen method consistently extracted DNA with higher
260/230 and 260/280 ratios. This indicated that the DNA was contaminated with fewer humic
acid-like compounds. Furthur more Mannitol based methods and the Sodium phosphate-SDS
method may remove humic acid material very effectively than the other methods of extraction.
7.3.3 PCR Amplification using 16S rRNA primers
The impurities mainly removed by method using Mannitol and SDS, which proved to be
an efficient protocol for extraction. Among the three purification methods that were applied to
soil-extracted DNA, protocols #1, #2, #3 and #6 yielded DNA ready for efficient PCR
amplification. The size of amplicons is estimated 225 bp. Since PCR involves successive
enzymatic reactions and since DNA polymerase requires contamination-free sites. It appears that
extraction method of all three Mannitol Methods (P/C/I, PEG/NaCl and CTAB) and sodium
phosphate SDS method gave the very good quantity of DNA for the amplification by PCR
while other method were not sufficient for the PCR due to probably due to contaminating (DNA-
adhering) substances like humic acid. These contaminating materials were removed and this
could have led to inhibition of the initial PCR product on the original DNA. Humic acid
impurities may affect DNA hybridization efficiency too. In the method using Mannitol with liq.
N2 showed a very good chemical lysis than the other methods so according to this concept
Mannitol may also play a important role in chemical lysis of the cells with the other chemicals
like CTAB, SDS, EDTA and Tris-HCL etc so that the lysis of cells may be good in comparison
to other methods and the yield of soil DNA become high.
1 2 3 4 5 6 7
Figure 7.2 Visualization of PCR Amplification of soil DNA extracted by different methods
showing bands on elecrtophoresis lane 1 Marker; lane 2 Mannitol- PEG/NaCl method; lane
3- Mannitol -P/C/I; lane 4 Mannitol - CTAB; lane 5-DNA extraction using PEG / NaCl
225bp
method without Liquid Nitrogen; lane 6-DNA extraction using bead beating without liq.
N2; lane 7-DNA extraction using Sodium Phosphate buffer & SDS method with bead
beating & Liquid Nitrogen
Thus, we compared the obtained yield of soil DNA by all used methods. Amplification of
DNA by PCR was used to determine its quality. Among the methods only Sodium phosphate-
SDS with liquid nitrogen, all three mannitol Methods with liquid nitrogen, ready for
efficient PCR amplification. And other Bead beating without liq N2, and PEG-NaCl without liq.
N2, even though giving an acceptable level of DNA, was not suitable for PCR amplification.
PCR involves successive enzymatic reactions and since DNA polymerase requires
contamination-free sites. The described method allows the use of large scale preparations
providing greater probability of detecting genes present in low abundance in the soil
environment. Because this method is applicable to even the more challenging heavily
contaminated soils, molecular microbial biodiversity assessment can now be more readily
applied.
7.4 Conclusion
For Metagenomic studies it is important to select an extraction and purification method,
which yields DNA of suitable quantity and purity from the soil. The extraction methods are
strongly influenced by several parameters, such as incomplete cell lysis, DNA sorption to soil
surfaces, extraction of humic contaminants, and DNA degradation. In this study, we tested a
number of DNA extraction methods for their ability to fulfill these requirements. Here six
methods are considered for isolation of DNA and compared. The inclusion of Mannitol in the
extraction buffer has been proved to increase the efficiency of extraction. Further purification of
DNA has been tried with three different procedures, viz., by using PEG-NaCl, CTAB and PCI.
The size of extracted DNA ranged from less than 500 bp to greater than 2 kb in size. Higher
molecular weight DNA is desirable for PCR since the greater the size of the DNA, the less likely
is the formation of chimeras during PCR, hence better for microbial diversity analysis.
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List of Publications
1. Paper Published/ Book Chapters: (Total: 4)
1. Faria Fatima, Ira Chaudhary, J Ali, S Rastogi, N Pathak. Exploring microbial diversity
for development National conference on biodiversity, development and poverty
alleviation 22 may, 2010.
2. Faria Fatima, Ira Chaudhary, Jasarat Ali, Smita Rastogi, Neelam Pathak. Microbial
DNA extraction from soil by different methods and its PCR amplification. Biochem.Cell
Arch. 2011, 11: 1-6.
3. Ira Chaudhary, Faria Fatima, Rolee Sharma, Smita Rastogi and Neelam Pathak.
Isolation of a Noval Laccase- producing Fungus from litter in Upper Soil Horizon, Braz.
J. Microbial. 2011. (Communicate).
4. Ira Chaudhary, Faria Fatima, Smita Rastogi, Neelam Pathak, Zeeshan. Isolation and
Characterization of microbes with Phosphate Solubilizers and lignin degrading abilities.
Biochem. Cell. Arch. Vol. 11, No.2, 2011.
Abstract: (Total: 15)
1. Faria Fatima, Nilesh Kumar, Srika Singh ,Preeti Bajpai and Neelam Pathak.
Biological Synthesis of Nanoparticles by Novel Phosphate solubilizsing Fungus
(Bipolaris tetramera) and their antibacterial activity. Alumni Meet and National
Seminar on “Frontier Agriculture-2013”. Deva University Of Agriculture and
technology, Kumarganj Faizabad .April 20-21, 2013.
2. Faria Fatima, Jiya Naseem, Erum Sheikh, Pawan Kushwaha, Preeti Bajpai, Neelam
Pathak. Extracellular synthesis of silver and gold Nanoparticles bu Bipolaris
tetramera and their antibacterial activity. Innovations in sciences for better
tomorrow, “LUSCON 2013” 20-21 March 2013 Lucknow (Awarded II Prize in
poster presentation)
3. Faria Fatima, Erum Sheikh, Pawan kushwaha, Priyanka verma, Priti bajpai,
Neelam Pathak and A.K Srivastava. Fungus mediated extracellular synthesis of
silver and gold nanoparticles and their antibacterial activity. National seminar on
stress, development and adaptation: Biochemical Basis and Biotechnological
Approaches 15-16 March 2013 Lucknow.
4. Jasarat Ali, Faria Fatima and Neelam Pathak. Screening. Biochemical and
Molecular Characterization of bacteria having (1-Aminocyclopropane-1-
Carboxylate)-Deaminase Producing Potential. Alumni Meet and National Seminar
on “Frontier Agriculture-2013”. Deva University of Agriculture and technology,
Kumarganj Faizabad .April 20-21, 2013.
5. Faria Fatima. Biodiversity Analysis of Phosphate Solubilizers at biochemical and
Molecular level. Bright international conference and events on World congress
biotechnology, 4-6 May 2012.
6. Faria Fatima, Ira Chaudhary, Neelam Pathak Smita Rastogi and Rolee Sharma.
Isolation, Biochemical and Molecular Characterization of microbes with Phosphate
solubilizing abilities. International Conference on Microbial, Plant and Animal
research (ICMPR-2012), March 29-31, 2012 Jaipur.
7. Faria Fatima, Jasarat ali and Neelam Pathak. Isolation , biochemical and molecular
characterization of microbes with phosphate solubilizing abilities. Department of
Biotechnology, Integral University, Nov 11, 2012 Lucknow.
8. Jasarat Ali, Faria Fatima, Farina Mujeeb and Neelam Pathak. Isolation of ACC
Deaminase Producing Microrganisms and their Biochemical and Molecular
Characterization. Department of Biotechnology, Integral University, Nov 11, 2012
Lucknow.
9. Ira Chaudhary, Faria Fatima, Neelam Pathak Smita Rastogi and Rolee Sharma.
Isolation of Lignin Peroxidase –Producing lignin degrading fungus from soil.
International Conference on Microbial, Plant and Animal research (ICMPR-2012),
March 29-31, 2012 Jaipur.
10. Ira Chaudhary, Faria Fatima ,Neelam Pathak, Smita Rastogi, Rolee Sharma.
Isolation of Lignin Peroxidase- producing Plant Pathogenic Fungus from the effluent
sample: Planetary Scientific Research Centre Conferences, April 28-29, 2012
Singapore.
11. Ira Chaudhary, Faria Fatima, Smita Rastogi, Neelam Pathak. Isolation of
Ligninolytic Enzymes - producing Microorganisms from the Soil. National seminar
on reactive oxygen species: roles in animal and plant biology Dec 23 – 24.
12. Faria Fatima, Ira Chaudhary, Neelam Pathak. Biochemical and molecular analysis
of Rhizosphere microbe’s National symposium on biodiversity and food security:
Challenges and divising strategies. Dec 10- 11 IIPR Kanpur.
13. Ira Chaudhary, Faria Fatima, Smita Rastogi, Neelam Pathak. Biodiversity analysis
of lignin degrading microorganisms by assaying enzymes. National symposium on
biodiversity and food security: Challenges and divising strategies. Dec 10- 11 IIPR
Kanpur.
14. Faria Fatima, Ira Chaudhary, Jasarat Ali, Smita Rastogi and Neelam Pathak. Direct
isolation of DNA from soil and its PCR amplification for microbial diversity
analysis. SAARC Workshop on Biodiversity Conservation, Sep. 21- 22, 2010.
15. Ira Chaudhary, Faria Fatima, Smita Rastogi and Neelam Pathak. Isolation and
characterization of microbes with phosphate solubilizing and lignin degrading
abilities. SAARC Workshop on Biodiversity Conservation, Sep. 21- 22, 2010.
Poster Paper- (Total: 5)
1. Faria Fatima, Jiya Naseem, Erum Sheikh, Pawan Kushwaha, Preeti Bajpai, Neelam
Pathak. Extracellular synthesis of Silver and Gold nanoparticles by Bipolaris
tetramera and their antibacterial activity. Innovations in sciences for better tomorrow,
“LUSCON 2013” 20-21 March 2013.
2. Faria Fatima, Erum Sheikh, Pawan kushwaha, Prriyabka verma, Priti bajpai, Neelam
Pathak and A.K srivastava.Fungus mediated extracellular synthesis of silver and Gold
nanoparticles and their antibacteria activity. National seminar on stress, development
and adaptation: Biochemical Basis and Biotechnological Approaches 15-16 March
2013.
3. Faria Fatima, Nilesh Kumar, Sarika Singh, Preeti Bajpai and Neelam Pathak.
Biological Synthesis of Nanoparticles by Novel Phosphate solubilizing Fungus
(Bipolaris tetramera) and their antibacterial activity. Alumni Meet and National
Seminar on “Frontier Agriculture-2013”. Deva University Of Agriculture and
technology, Kumarganj, Faizabad April 20-21, 2013.
4. Faria Fatima, Ira Chaudhary, Neelam Pathak Smita Rastogi and Rolee Sharma.
Isolation, Biochemical and Molecular Characterization of microbes with phosphate
solubiling abilities. International Conference on Microbial, Plant and Animal research
(ICMPR-2012),March 29-31,2012.
5. Ira Chaudhary, Faria Fatima, Smita Rastogi, Neelam Pathak. Isolation of
Ligninolytic Enzymes producing Microorganisms from the Soil. National seminar on
reactive oxygen species: roles in animal and plant biology, Dec 23 - 24 2011.
Poster presentation Awards
First Best Poster presentation Award
Faria Fatima, Nilesh Kumar, Srika Singh ,Preeti Bajpai and Neelam
Pathak.Biological Synthesis of Nanoparticles by Novel Phosphate solubilizsing
Fungus (Bipolaris tetramera) and their antibacterial activity. Alumni Meet and
National Seminar on “Frontier Agriculture-2013”. Narendra Deva University Of
Agriculture and technology, Kumarganj Faizabad. April 20-21, 2013.
Second Best Poster Award
Faria Fatima, Jiya Naseem, Erum Sheikh, Pawan Kushwaha, Preeti Bajpai, Neelam
Pathak. Extracellular synthesis of Silver and Gold nanoparticles by Bipolaris
tetramera and their antibacterial activity. Innovations in sciences for better
tomorrow, “LUSCON 2013” 20-21 March 2013.
Oral Presentation for Young Scientist award in SAARC Workshop at BHU, Varanasi
Faria Fatima, Ira Chaudhary, Jasarat Ali, Smita Rastogi and Neelam Pathak. Direct
isolation of DNA from soil and its PCR amplification for microbial diversity analysis.
SAARC Workshop on Biodiversity Conservation, Sep. 21- 22, 2010.