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Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X
International Journal of Pharmaceutical Sciences Review and Research Page 125
Available online at www.globalresearchonline.net
Siddharth Vats
*
, Dr Rajesh Kumar and Kanupriya Miglani
University Institute of Engineering and Technology, Kurukshetra University, Kurukshetra, Haryana, India.
Accepted on: 11-04-2011; Finalized on: 28-09-2011.
ABSTRACT
Earth is our home and it is in danger. Pollution is threatening its sustainability and carrying capabilities. Heavy metal pollution can
cause toxicity by inhibiting metabolic reactions. The Minimum Inhibitory Concentration (MIC) of the isolated samples against Nickel
(Ni
2+
), Lithium (Li
1+
), Copper (Cu
2+
), Manganese (Mn
2+
), Zinc (Zn
+2
) and Iron (Fe
+3
) was determined in solid media. Multiple metal
resistances of the isolate associated with resistance to various antibiotics were also determined. Salt tolerance was determined both
in solid and liquid media. Identified halo-tolerant, metal resistant bacteria find use in the bioremediation of heavy metal
contaminated sewage and waste water, and also for the digestion of the high salt rich soil grown plants. Enzymes from these
microbes can be used for various bioremediation purposes. Though amylases originate from different sources (plants, animals, and
microorganisms), the microbial amylases are the most abundantly produced and used in industry, due to their productivity and
thermo stability. Microbe identified is Pseudomonas lini and show remarkable heavy metal tolerance, high salinity tolerance,
antibiotic resistance and amylolytic activities.
Keywords: Heavy metal, Pollution, Halotolerant, thermostability, antibiotics resistant.
INTRODUCTION
Our earth is the only planet which has been found to
support life. It supports millions of species and billion of
living organisms. But population explosion has led to its
uncontrolled exploitation. Man to full fill its need has
established industries which twenty four in to seven,
produces toxic products and cause pollutions and harm
nature. Pollution of heavy metal is one of the important
menaces. And this pollution is increasing with the
expansion of the industries. Heavy metals pose a real
serious contamination of soil and water
1
. Water effluents
coming out from the industries and sewage wastes have
permanent toxic effects to human and the environments.
Metals like potassium, copper, nickel, zinc, manganese,
ferrous and lithium are the most commonly used and the
widest spread contaminant.2
Heavy metals frequently
generate strong reactive species and directly or indirectly
cause gene mutation and harm living cells. Iron, copper
and zinc are the metal with dual role. At trace level these
metal ions are very essential but beyond a concentration
they start showing negative effects. These metals are
used as the Co- factors in the enzymatic reactions but
their over presence can also inhibit the metabolic
reactions and can cause toxicity in the living organisms.
Microbes especially Bacteria are most abundant and are
almost omnipresent, they found every environment
hospitable. They can survive almost any kind of nutrients
available to them. Some heavy metals are micronutrients
but heavy metals in excess definitely toxic. These micro-
organisms react and respond with different ways like
biosorption to the cell wall, transport across the cell
membrane, oxidation- reduction reactions, complexation,
precipitations and entrapment in their extracellular
capsules.3
Enzymes are biological catalysts or assistants.
Enzymes consist of various types of proteins that work to
drive the chemical reaction required for a specific action.
Enzymes can either perform a reaction or speed it up. The
chemicals that are transformed with the help of enzymes
are called substrates. In the absence of enzymes, these
chemicals are called reactants. Biocatalysis involves
enzyme catalysis in the living cells. Over 3000 enzymes
have already been identified and the number is growing
with research in the field of genomics and proteomics.
Enzymes can be extracted from living tissues, purified and
even crystallized. Though amylases originate from
different sources (plants, animals, and microorganisms),
the microbial amylases are the most abundantly
produced and used in industry, due to their productivity
and thermo stability.4
Enzymes from bacterial and fungal
sources have dominated applications in industrial sectors.
Amylases are classified based on how they break down
starch molecules. α-amylase (alpha-amylase) -Reduces
the viscosity of starch by breaking down the bonds at
random, therefore producing varied sized chains of
glucose. ß-amylase (Beta-amylase) - Breaks the glucose-
glucose bonds down by removing two glucose units at a
time, thereby producing maltose. Amyloglucosidase
(AMG) - Breaks successive bonds from the non-reducing
end of the straight chain, producing glucose. The α-
amylase family comprises a group of enzymes with a
variety of different specificities that all act on one type of
substrate being glucose residues linked through α-1-1, α-
1-4, α-1-6, glycosidic bonds. Members of this family share
a number of common characteristic properties.5
Amylases
can be divided into two categories based upon their site
of action, endoamylases and exoamylases. Endoamylases
catalyze hydrolysis in a random manner in the interior of
ISOLATION, CHARACTERIZATION AND IDENTIFICATION OF HIGH SALINITY TOLERANT, HEAVY METAL
CONTAMINANT AND ANTIBIOTICS RESISTANT AMYLOLYTIC-THERMOPHILIC PSEUDOMONAS Sp.
Research Article
Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X
International Journal of Pharmaceutical Sciences Review and Research Page 126
Available online at www.globalresearchonline.net
the starch molecule producing linear and branched
oligosaccharides of various chain lengths. Exoamylases
act from the non-reducing end successively resulting in
short end products.
6
Amylases constitute a class of
industrial enzymes having approximately 25% of the
enzyme market.7,8
It is desirable that α- amylases should
be active at the high temperatures of gelatinization (100-
110°C) and liquefaction (80-90°C) to economize
processes, therefore there has been a need for more
thermophilic and thermostable α-amylases.
7
With the
availability of High salinity tolerant microbe number of
new possibilities for industrial processes has emerged.
While the most widely used thermostable enzymes are
the amylases in the starch industry.9-11
A number of other
applications are in various stages of development. The
spectrum of amylase application has widened in many
other fields, such as clinical, medical, and analytical
chemistries, as well as their wide spread application in
starch saccharification and in the textile, food,
fermentation, paper, brewing and distilling industries.12
Sources of contamination
Water effluents coming out from the industries and
sewage wastes have permanent toxic effects to human
and the environments.13
Resistance system of bacteria is
made so that all kinds of Bacteria are resistant to heavy
metals.14
Nickel is the 24th
most abundant element with
soft and hard metal like characteristics show binding
nature with sulphur, nitrogen and oxygen groups.15
Nickel
is the metal used mostly in alloy formation. The nickel
content of these alloys varies widely from, as examples,
1-3% for special engineering steels, 8-14% for stainless
steels, 15-40% for special engineering alloys, 40-90%
nickel for special alloys for the aerospace and electronic
industries. And these industries are the source of its
contamination. Chromium in natural environment mostly
present in hexa-valent and trivalent species.
16
Main
sources of chromium contamination are leather tanning,
chromium electroplating, alloy preparation and its use in
the nuclear power plant.17
Zinc serve as a co-factor in
various cellular processes carried out by more than 300
enzymes.
18
Zinc is an important player in the structural
stability and in transcription. It an important part and
adult human weight contain 2.5 gram of zinc mostly used
by the enzymes. Sources for the zinc contaminations are
permitted industries, residential wastes, human wastes,
corrosion and other sources. Sources for the copper
contaminations are copper pesticides, vehicle brake pads,
industrial copper use, soil erosion and copper in domestic
water discharge. Copper-containing pesticides are widely
used to control fungi, algae and roots. Big doses of copper
can cause liver and kidney damage. Iron as a pollutant is
released by iron and steel industries. Iron bearing water is
journal orange is colour. In cities manganese pollution is
increasing with the increase of traffics and most likely
source is exhaust.
19
MATERIALS AND METHODS
Materials
All the chemicals used were from Himedia and glass
wares used were from Perfitt.
Sample collection
Samples are collected from the sewage water, industrial
effluents disposal sites, waste water treatment plants and
sites where waste clothes are treated with chemicals.
Samples were collected in the sterile autoclaved plastic
cap bottles. 15 samples were collected and taken for
study.
Isolation of pure bacterial cultures
Different water samples were spreaded on nutrient agar
and pure colonies obtained. These pure colonies were
again spreaded on nutrient agar. After this, stock
solutions of each bacterium were prepared and used to
carry out study and to find the best bacteria among them.
Selection of thermostable microbes
Nutrient agar plates are made of pure colonies and are
incubated at a temperature of 40°C for 48 hours. Those
colonies which survive this temperature are selected and
tested also in nutrient broth. Microbes having good
growth in the solid as well as in liquid media are selected.
Selection of the high salinity tolerant microbes
To select halotolerant bacteria, pure culture were
spreaded on the 1 and 2 molar NaCl containing nutrient
agar plates and growth were observed incubating at 27°C
after 24-48 hours. The resistant bacteria are then
inoculated in 1 and 2 molar nutrient broth and best
growing microbe are selected.
Selection of amylolytic microbes
Halo tolerant microbes selected are sub cultured over 2%
starch enriched nutrient agar plate. After 48 hr
incubation bacterial colonies were flooded with 1 %
Iodine solution, to select isolates which show wide clear
zone around their colonies.
Selection of heavy metals resistant microbes
Selection of the heavy metal resistant microbe is done by
use of heavy metal incorporated media. Heavy metals
incorporated were Nickel (Ni
2+
), Lithium (Li
1+
), Copper
(Cu
2+
), Manganese (Mn
2+
), Zinc (Zn
+2
) and Iron (Fe
+3
).
Salinity tolerant microbes are exposed to high metal
concentration. Chemicals used were LiCl [Lithium
chloride], MnSO4.H2O [Manganese (II) Monohydrate],
CuSO4.5H2O [Copper (II) Sulphate Pentahydrate],
ZnSO4.7H2O [Zinc Sulphate], [Ferrous III Sulphate] Fe.Cl3
and NiSO4.6H2O [Nickle Sulphate].
Antibiotic resistance
Antibiotic resistance of the halotolerant, multiple metal
resistance thermophilic microbe was determined Kirby-
Bauer disc diffusion method.20
After incubation of the
Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X
International Journal of Pharmaceutical Sciences Review and Research Page 127
Available online at www.globalresearchonline.net
microbe grown on MHA, it is considered as resistant or
susceptible based on the clear zone shown or not by the
antibiotics.
RESULTS AND DISCUSSION
Isolation and identification of the bacteria with heavy
metal resistance
A no. of microbes were screened from the samples
collected from the various effluents sites near
Kurukshetra University and were screened for high
salinity tolerance, multiple heavy metal resistance. Halo-
tolerant Bacteria with highest salinity tolerance and
multiple heavy metal resistance ability was selected.
Bacteria showed (table 1 & 3) MIC for different metal
ranging from 400µg/ml to 1800µg/ml. The test indicates
multiple heavy metal and antibiotic resistance. Bacteria
have maximum resistance to lithium, ferrous, zinc and
manganese with moderate resistance to nickel and
copper.
Table 1: Resistance of bacteria to heavy metals
(Halotolerant, multiple heavy metal resistant Bacteria)
Resistance to MIC
Nickel (Ni
2+
) 1400µg/ml
Lithium (Li
1+
) 2000µg/ml
Copper (Cu
2+
) 1900µg/ml
Manganese (Mn
2+
) 1800µg/ml
Iron (Fe+3
) 1900µg/ml
Zinc (Zn+2
) 1200µg/ml
Antibiotic sensitivity of multiple heavy metal resistant
bacteria
Sensitivity of bacteria was tested against 15 antibacterial
antibiotics like amoxicillin, penicillin, methicillin,
doxocycline, chlorocycline, erythromycin, nitronidozole,
minocycline, clindocycline, ampiciline, clindomycine,
ofloxocine, rifampicine, gentamycine, vancomycine. It
was resistant again vancomycine, clindomycine,
amoxycilline, penicillin, methicilline, nitronidazole,
minocyline and streptomycine.
Salt resistance is very important characteristic of isolated
microbe and is use full in treating amylolitic waste rich in
salt. This is very important in bioremediation purposes.
We observed good resistance both in liquid media as well
as solid media by Pseudomoonas sp. against NaCl. Results
are notified in the table 2.
Table 2: Resistance of bacteria to salt concentration.
Salt Concentration (Molar) Resistivity
0.5 +++++
1.0 +++++
1.5 +++++
2.0 +++++
2.5 +++
3.0 +
+: Growth; ++, ++++: Growth status; - : no growth
Table 3: Antibiotic Resistance of halotolerant and heavy metal resistant bacteria
Antibiotic disc of size 6mm Disc content Diameter of inhibition zone Resistivity of bacteria
Vancomycine 30 mcg 6 mm +++++
Erythromycin 15 mcg 49 mm - - - - -
Penicillin 10 mcg 6 mm +++++
Minocycline 30 mcg 15 mm - -
Gentamycine 10 mcg 25 mm - -
Rifampicin 5 mcg 12 mm - -
Oflaxacine 5 mcg 25 mm - -
Amoxycoline 25 mcg 6 mm +++++
Methicilline 5 mcg 6 mm +++++
Chloroamphinicole 30 mcg 47 mm - - - - -
Spectinomycine 100 mcg 6 mm +++++
Metronidazole 5 mcg 6 mm +++++
Nitronidazole 10 mcg 20 mm - -
Clindomycine 10 mcg 30 mm - - -
Ampicilline 5 mcg 25 mm - - -
Deoxycholine 10 mcg 6 mm +++++
+: Resistance; +++, +++++: growth status; - : Susceptibility to antibiotics.
Identification of the microbe
The microbe isolated was sent to Microbial Type Culture
Collection and Gene Bank, Institute of Microbial
Technology, Chandigarh India. Biochemical and
morphological test were also conducted by them and also
in our labs (table 4.1 to 4.4). Microbe identified is
Pseudomonas lini.
Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X
International Journal of Pharmaceutical Sciences Review and Research Page 128
Available online at www.globalresearchonline.net
Table 4: biochemical characterization of halo tolerant
heavy metal resistant bacteria
Table 4.1: Colony morphology
Configuration Circular
Margin Entire
Elevation Flat
Surface Smooth
Color Cream
Opacity Opaque
Gram’s reaction Negative
Cell shape Rod
Size 0.8x2
-3
Spore No
Motility No
Table 4.2: Biochemical test
MacConkey Yes
Voges Proskauer Test No
Citrate utilization Yes
Dextrose ( Acid production) Yes
Starch hydrolysis Yes
Oxidase test Yes
Catalase test Yes
Urea hydrolysis No
Indole Negative
Gelatine hydrolysis No
H2S production No
Esculin hydrolysis No
Ornithine decarboxylase No
Lysine decarboxylase No
Table 4.3: Utilization of different carbon and nitrogen
sources
Carbon sources Utilization Nitrogen sources Utilization
Maltose Yes Beef extract Yes
Sucrose Yes Yeast extract Yes
Galactose Yes Peptone Yes
Fructose Yes Glutamine Yes
Starch Yes Aspartic acid Yes
Lactose Yes Leucine Yes
Glycerol Yes Glycine Yes
Table 4.4: Growth at different pHs and temperature:
Temperature (°C) Growth pH Growth
4 No 4.0 No
10 No 5.0 Yes
15 No 6.0 Yes
20 No 7.0 Yes
25 No 8.0 Yes
30 Yes 9.0 Yes
37 Yes 10.0 Yes
40 Yes 11.0 Yes
42 No 12.0 Yes
CONCLUSION
During the present study focus was to isolate microbe
which is heavy metal tolerant, high salinity tolerant, and
also produce amylase enzymes and can with stand heavy
temperature. The microbe isolated is resistant to nickel,
copper, manganese, ferrous, lithium and zinc. Heavy
metals are very important and essential trace elements
according to various studies. And microbes present in the
nature have direct or indirect interactions with the heavy
metals. Developments of heavy metal resistance also
have some health implications because microbes which
are metal resistant and are also antibiotics resistant.
Heavy metal pollution is affecting land, air and water. And
on inhalation or in consumption in excess amount they
are toxic to the living beings. Heavy metal resistant
microorganisms can be used for the bioremediation of
pollution caused by heavy metals.3
Multiple metal
resistant microbes have advantages over the single metal
resistant microbes. Heavy metals and biocides are two
components which itself are not as such antibiotics but
they have antibiotics properties and so help in selection
of the microbes which are antibiotics resistant too. This is
because genes responsible for the metal resistance lie
near to the genes responsible for the antibiotics
resistance.
3
Experiments are underway to develop and
integrated bioremediation system using some of the
resistant microbes.
REFERENCES
1. Cheng S. Heavy metal pollution in china: Origin, pattern and
control. Environmental sciences and pollution research.
2003; 10:192-198.
2. Patterson JW. Waste water treatment technology. Ann
Arbor Science publishers, Ann Arbor, MI, USA. 1977.
3. Singh V, Chauhan PK, Kanta R, Dhewa T, Kumar V. Isolation
and characterization of pseudomonas Resistant to heavy
metals contaminants. 2010; 2 (30):164-167.
4. Burhan A, Nisa, U, Gökhan C, Ömer C, Ashabil A, Osman G.
Enzymatic properties of a novel thermostable, thermophilic,
alkalineand chelator resistant amylase from an alkaliphilic
Bacillus Sp. Isolate ANT-6. Proc Biochem 2003; 38: 1397-
1403.
5. Van der Maarel MJEC, Van der Veen B,Utdehaag JCM,
Leenhuis H, Dijkhuizen L. Properties and applications of
starch converting enzymes of the alpha amylase family. J
Biotechnol. 2 0 0 2 ; 94: 137-155.
6. Gupta R, Gigras P, Mohapatra H, Goswami,VK and
Chauhan B . Microbial alpha amylases: a biotechnological
perspective. Proc biochem. 2003; 38 : 1599 – 1616.
7. Sindhu GS, Sharma P, Chakrabarti T, Gupt JK. Strain
improvement for the production of a thermostable α-
amylase. Enzy MicrobioTechnol 1997; 24:584-589.
8. Rao MB, Tanksale AM, Gathe MS, Deshpande VV.
Molecular and Biotechnological aspects of microbial
proteases. Microbio Mol Biol Rev. 1998; 62(3): 597-635.
Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X
International Journal of Pharmaceutical Sciences Review and Research Page 129
Available online at www.globalresearchonline.net
9. Poonam N, Dalel S. Enzyme and microbial systems involved
in starch processing. Enzyme Micro Technol. 1995; 17:770-
778.
10. Crab W, Mitchinson C. Enzymes involved in the processing
of starch to sugars. Trends Biotechnology 1997;15: 349-
352.
11. Sarikayle E, Migossa T, Adachi M, Mikami B. Comparison of
degradation abilities of alpha and beta amylases on raw
starch granules. Proc Biochem 2000;35: 711-715.
12. Pandey A, Nigam P, Soccol CR, Soccol VY, Singh D,
Mohan R. Advances in microbial amylases. Biotechnol Appl
Biochem . 2000 ;31: 135–152.
13. Rehman A, Zahoor A, Munner BV, Hasnain S. Chromium
tolerance and reduction potential of a bacillus sp.ev3
isolated from metal contaminates was water. Bulletin of
Environmental and Contamination toxicology. 2008; 81:25-
29.
14. Silver S, Phung LT. Bacterial heavy metal resistance: new
surprises. Annu. Rev. Microbiol. 1956; 50:753-89.
15. Costa M, Klein CB,. Nickle carcinogenesis, mutation,
epigenetics, or selection. Environmen Heal. Perspec. PartA.
1999; 107; 438-439.
16. Chung J, Nerenberg R, Rittmann BE. Bioreduction of
solution chromate using a hydrogel based membrane
biofilm reactor. Water Research. 2006; 40:1634-1642.
17. Thacker U, Parikh R, Shouche Y, Madamwar D. Hesavalent
chromium reduction by provideria sp. Process
Biochemistry. 2006; 41:112-1337.
18. McCall KA, Huang CC, Fierke CA. Function and mechanism
of zinc metalloenzymes. J of Nutri. 2000; 130:1437s-1446s
19. Joselow MM, Tobias ED, Kohler R, Coleman S, Bogden J,
Gause D (1978) Manganese pollution in the city
environment and its relationship to traffic density. Ann. J
Pubic Health 68:557-560.
20. Singh V, Chauhan PK, Kanta R, Dhewa J, Kumar V. Isolation
and characterization of Pseudomans resistant to heavy
metals contaminants. Int. J. Of Pharma Sci. Review and
Res. 2010.3(2):164-167.
****************

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Isolating Pseudomonas lini for Heavy Metal Bioremediation

  • 1. Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X International Journal of Pharmaceutical Sciences Review and Research Page 125 Available online at www.globalresearchonline.net Siddharth Vats * , Dr Rajesh Kumar and Kanupriya Miglani University Institute of Engineering and Technology, Kurukshetra University, Kurukshetra, Haryana, India. Accepted on: 11-04-2011; Finalized on: 28-09-2011. ABSTRACT Earth is our home and it is in danger. Pollution is threatening its sustainability and carrying capabilities. Heavy metal pollution can cause toxicity by inhibiting metabolic reactions. The Minimum Inhibitory Concentration (MIC) of the isolated samples against Nickel (Ni 2+ ), Lithium (Li 1+ ), Copper (Cu 2+ ), Manganese (Mn 2+ ), Zinc (Zn +2 ) and Iron (Fe +3 ) was determined in solid media. Multiple metal resistances of the isolate associated with resistance to various antibiotics were also determined. Salt tolerance was determined both in solid and liquid media. Identified halo-tolerant, metal resistant bacteria find use in the bioremediation of heavy metal contaminated sewage and waste water, and also for the digestion of the high salt rich soil grown plants. Enzymes from these microbes can be used for various bioremediation purposes. Though amylases originate from different sources (plants, animals, and microorganisms), the microbial amylases are the most abundantly produced and used in industry, due to their productivity and thermo stability. Microbe identified is Pseudomonas lini and show remarkable heavy metal tolerance, high salinity tolerance, antibiotic resistance and amylolytic activities. Keywords: Heavy metal, Pollution, Halotolerant, thermostability, antibiotics resistant. INTRODUCTION Our earth is the only planet which has been found to support life. It supports millions of species and billion of living organisms. But population explosion has led to its uncontrolled exploitation. Man to full fill its need has established industries which twenty four in to seven, produces toxic products and cause pollutions and harm nature. Pollution of heavy metal is one of the important menaces. And this pollution is increasing with the expansion of the industries. Heavy metals pose a real serious contamination of soil and water 1 . Water effluents coming out from the industries and sewage wastes have permanent toxic effects to human and the environments. Metals like potassium, copper, nickel, zinc, manganese, ferrous and lithium are the most commonly used and the widest spread contaminant.2 Heavy metals frequently generate strong reactive species and directly or indirectly cause gene mutation and harm living cells. Iron, copper and zinc are the metal with dual role. At trace level these metal ions are very essential but beyond a concentration they start showing negative effects. These metals are used as the Co- factors in the enzymatic reactions but their over presence can also inhibit the metabolic reactions and can cause toxicity in the living organisms. Microbes especially Bacteria are most abundant and are almost omnipresent, they found every environment hospitable. They can survive almost any kind of nutrients available to them. Some heavy metals are micronutrients but heavy metals in excess definitely toxic. These micro- organisms react and respond with different ways like biosorption to the cell wall, transport across the cell membrane, oxidation- reduction reactions, complexation, precipitations and entrapment in their extracellular capsules.3 Enzymes are biological catalysts or assistants. Enzymes consist of various types of proteins that work to drive the chemical reaction required for a specific action. Enzymes can either perform a reaction or speed it up. The chemicals that are transformed with the help of enzymes are called substrates. In the absence of enzymes, these chemicals are called reactants. Biocatalysis involves enzyme catalysis in the living cells. Over 3000 enzymes have already been identified and the number is growing with research in the field of genomics and proteomics. Enzymes can be extracted from living tissues, purified and even crystallized. Though amylases originate from different sources (plants, animals, and microorganisms), the microbial amylases are the most abundantly produced and used in industry, due to their productivity and thermo stability.4 Enzymes from bacterial and fungal sources have dominated applications in industrial sectors. Amylases are classified based on how they break down starch molecules. α-amylase (alpha-amylase) -Reduces the viscosity of starch by breaking down the bonds at random, therefore producing varied sized chains of glucose. ß-amylase (Beta-amylase) - Breaks the glucose- glucose bonds down by removing two glucose units at a time, thereby producing maltose. Amyloglucosidase (AMG) - Breaks successive bonds from the non-reducing end of the straight chain, producing glucose. The α- amylase family comprises a group of enzymes with a variety of different specificities that all act on one type of substrate being glucose residues linked through α-1-1, α- 1-4, α-1-6, glycosidic bonds. Members of this family share a number of common characteristic properties.5 Amylases can be divided into two categories based upon their site of action, endoamylases and exoamylases. Endoamylases catalyze hydrolysis in a random manner in the interior of ISOLATION, CHARACTERIZATION AND IDENTIFICATION OF HIGH SALINITY TOLERANT, HEAVY METAL CONTAMINANT AND ANTIBIOTICS RESISTANT AMYLOLYTIC-THERMOPHILIC PSEUDOMONAS Sp. Research Article
  • 2. Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X International Journal of Pharmaceutical Sciences Review and Research Page 126 Available online at www.globalresearchonline.net the starch molecule producing linear and branched oligosaccharides of various chain lengths. Exoamylases act from the non-reducing end successively resulting in short end products. 6 Amylases constitute a class of industrial enzymes having approximately 25% of the enzyme market.7,8 It is desirable that α- amylases should be active at the high temperatures of gelatinization (100- 110°C) and liquefaction (80-90°C) to economize processes, therefore there has been a need for more thermophilic and thermostable α-amylases. 7 With the availability of High salinity tolerant microbe number of new possibilities for industrial processes has emerged. While the most widely used thermostable enzymes are the amylases in the starch industry.9-11 A number of other applications are in various stages of development. The spectrum of amylase application has widened in many other fields, such as clinical, medical, and analytical chemistries, as well as their wide spread application in starch saccharification and in the textile, food, fermentation, paper, brewing and distilling industries.12 Sources of contamination Water effluents coming out from the industries and sewage wastes have permanent toxic effects to human and the environments.13 Resistance system of bacteria is made so that all kinds of Bacteria are resistant to heavy metals.14 Nickel is the 24th most abundant element with soft and hard metal like characteristics show binding nature with sulphur, nitrogen and oxygen groups.15 Nickel is the metal used mostly in alloy formation. The nickel content of these alloys varies widely from, as examples, 1-3% for special engineering steels, 8-14% for stainless steels, 15-40% for special engineering alloys, 40-90% nickel for special alloys for the aerospace and electronic industries. And these industries are the source of its contamination. Chromium in natural environment mostly present in hexa-valent and trivalent species. 16 Main sources of chromium contamination are leather tanning, chromium electroplating, alloy preparation and its use in the nuclear power plant.17 Zinc serve as a co-factor in various cellular processes carried out by more than 300 enzymes. 18 Zinc is an important player in the structural stability and in transcription. It an important part and adult human weight contain 2.5 gram of zinc mostly used by the enzymes. Sources for the zinc contaminations are permitted industries, residential wastes, human wastes, corrosion and other sources. Sources for the copper contaminations are copper pesticides, vehicle brake pads, industrial copper use, soil erosion and copper in domestic water discharge. Copper-containing pesticides are widely used to control fungi, algae and roots. Big doses of copper can cause liver and kidney damage. Iron as a pollutant is released by iron and steel industries. Iron bearing water is journal orange is colour. In cities manganese pollution is increasing with the increase of traffics and most likely source is exhaust. 19 MATERIALS AND METHODS Materials All the chemicals used were from Himedia and glass wares used were from Perfitt. Sample collection Samples are collected from the sewage water, industrial effluents disposal sites, waste water treatment plants and sites where waste clothes are treated with chemicals. Samples were collected in the sterile autoclaved plastic cap bottles. 15 samples were collected and taken for study. Isolation of pure bacterial cultures Different water samples were spreaded on nutrient agar and pure colonies obtained. These pure colonies were again spreaded on nutrient agar. After this, stock solutions of each bacterium were prepared and used to carry out study and to find the best bacteria among them. Selection of thermostable microbes Nutrient agar plates are made of pure colonies and are incubated at a temperature of 40°C for 48 hours. Those colonies which survive this temperature are selected and tested also in nutrient broth. Microbes having good growth in the solid as well as in liquid media are selected. Selection of the high salinity tolerant microbes To select halotolerant bacteria, pure culture were spreaded on the 1 and 2 molar NaCl containing nutrient agar plates and growth were observed incubating at 27°C after 24-48 hours. The resistant bacteria are then inoculated in 1 and 2 molar nutrient broth and best growing microbe are selected. Selection of amylolytic microbes Halo tolerant microbes selected are sub cultured over 2% starch enriched nutrient agar plate. After 48 hr incubation bacterial colonies were flooded with 1 % Iodine solution, to select isolates which show wide clear zone around their colonies. Selection of heavy metals resistant microbes Selection of the heavy metal resistant microbe is done by use of heavy metal incorporated media. Heavy metals incorporated were Nickel (Ni 2+ ), Lithium (Li 1+ ), Copper (Cu 2+ ), Manganese (Mn 2+ ), Zinc (Zn +2 ) and Iron (Fe +3 ). Salinity tolerant microbes are exposed to high metal concentration. Chemicals used were LiCl [Lithium chloride], MnSO4.H2O [Manganese (II) Monohydrate], CuSO4.5H2O [Copper (II) Sulphate Pentahydrate], ZnSO4.7H2O [Zinc Sulphate], [Ferrous III Sulphate] Fe.Cl3 and NiSO4.6H2O [Nickle Sulphate]. Antibiotic resistance Antibiotic resistance of the halotolerant, multiple metal resistance thermophilic microbe was determined Kirby- Bauer disc diffusion method.20 After incubation of the
  • 3. Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X International Journal of Pharmaceutical Sciences Review and Research Page 127 Available online at www.globalresearchonline.net microbe grown on MHA, it is considered as resistant or susceptible based on the clear zone shown or not by the antibiotics. RESULTS AND DISCUSSION Isolation and identification of the bacteria with heavy metal resistance A no. of microbes were screened from the samples collected from the various effluents sites near Kurukshetra University and were screened for high salinity tolerance, multiple heavy metal resistance. Halo- tolerant Bacteria with highest salinity tolerance and multiple heavy metal resistance ability was selected. Bacteria showed (table 1 & 3) MIC for different metal ranging from 400µg/ml to 1800µg/ml. The test indicates multiple heavy metal and antibiotic resistance. Bacteria have maximum resistance to lithium, ferrous, zinc and manganese with moderate resistance to nickel and copper. Table 1: Resistance of bacteria to heavy metals (Halotolerant, multiple heavy metal resistant Bacteria) Resistance to MIC Nickel (Ni 2+ ) 1400µg/ml Lithium (Li 1+ ) 2000µg/ml Copper (Cu 2+ ) 1900µg/ml Manganese (Mn 2+ ) 1800µg/ml Iron (Fe+3 ) 1900µg/ml Zinc (Zn+2 ) 1200µg/ml Antibiotic sensitivity of multiple heavy metal resistant bacteria Sensitivity of bacteria was tested against 15 antibacterial antibiotics like amoxicillin, penicillin, methicillin, doxocycline, chlorocycline, erythromycin, nitronidozole, minocycline, clindocycline, ampiciline, clindomycine, ofloxocine, rifampicine, gentamycine, vancomycine. It was resistant again vancomycine, clindomycine, amoxycilline, penicillin, methicilline, nitronidazole, minocyline and streptomycine. Salt resistance is very important characteristic of isolated microbe and is use full in treating amylolitic waste rich in salt. This is very important in bioremediation purposes. We observed good resistance both in liquid media as well as solid media by Pseudomoonas sp. against NaCl. Results are notified in the table 2. Table 2: Resistance of bacteria to salt concentration. Salt Concentration (Molar) Resistivity 0.5 +++++ 1.0 +++++ 1.5 +++++ 2.0 +++++ 2.5 +++ 3.0 + +: Growth; ++, ++++: Growth status; - : no growth Table 3: Antibiotic Resistance of halotolerant and heavy metal resistant bacteria Antibiotic disc of size 6mm Disc content Diameter of inhibition zone Resistivity of bacteria Vancomycine 30 mcg 6 mm +++++ Erythromycin 15 mcg 49 mm - - - - - Penicillin 10 mcg 6 mm +++++ Minocycline 30 mcg 15 mm - - Gentamycine 10 mcg 25 mm - - Rifampicin 5 mcg 12 mm - - Oflaxacine 5 mcg 25 mm - - Amoxycoline 25 mcg 6 mm +++++ Methicilline 5 mcg 6 mm +++++ Chloroamphinicole 30 mcg 47 mm - - - - - Spectinomycine 100 mcg 6 mm +++++ Metronidazole 5 mcg 6 mm +++++ Nitronidazole 10 mcg 20 mm - - Clindomycine 10 mcg 30 mm - - - Ampicilline 5 mcg 25 mm - - - Deoxycholine 10 mcg 6 mm +++++ +: Resistance; +++, +++++: growth status; - : Susceptibility to antibiotics. Identification of the microbe The microbe isolated was sent to Microbial Type Culture Collection and Gene Bank, Institute of Microbial Technology, Chandigarh India. Biochemical and morphological test were also conducted by them and also in our labs (table 4.1 to 4.4). Microbe identified is Pseudomonas lini.
  • 4. Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X International Journal of Pharmaceutical Sciences Review and Research Page 128 Available online at www.globalresearchonline.net Table 4: biochemical characterization of halo tolerant heavy metal resistant bacteria Table 4.1: Colony morphology Configuration Circular Margin Entire Elevation Flat Surface Smooth Color Cream Opacity Opaque Gram’s reaction Negative Cell shape Rod Size 0.8x2 -3 Spore No Motility No Table 4.2: Biochemical test MacConkey Yes Voges Proskauer Test No Citrate utilization Yes Dextrose ( Acid production) Yes Starch hydrolysis Yes Oxidase test Yes Catalase test Yes Urea hydrolysis No Indole Negative Gelatine hydrolysis No H2S production No Esculin hydrolysis No Ornithine decarboxylase No Lysine decarboxylase No Table 4.3: Utilization of different carbon and nitrogen sources Carbon sources Utilization Nitrogen sources Utilization Maltose Yes Beef extract Yes Sucrose Yes Yeast extract Yes Galactose Yes Peptone Yes Fructose Yes Glutamine Yes Starch Yes Aspartic acid Yes Lactose Yes Leucine Yes Glycerol Yes Glycine Yes Table 4.4: Growth at different pHs and temperature: Temperature (°C) Growth pH Growth 4 No 4.0 No 10 No 5.0 Yes 15 No 6.0 Yes 20 No 7.0 Yes 25 No 8.0 Yes 30 Yes 9.0 Yes 37 Yes 10.0 Yes 40 Yes 11.0 Yes 42 No 12.0 Yes CONCLUSION During the present study focus was to isolate microbe which is heavy metal tolerant, high salinity tolerant, and also produce amylase enzymes and can with stand heavy temperature. The microbe isolated is resistant to nickel, copper, manganese, ferrous, lithium and zinc. Heavy metals are very important and essential trace elements according to various studies. And microbes present in the nature have direct or indirect interactions with the heavy metals. Developments of heavy metal resistance also have some health implications because microbes which are metal resistant and are also antibiotics resistant. Heavy metal pollution is affecting land, air and water. And on inhalation or in consumption in excess amount they are toxic to the living beings. Heavy metal resistant microorganisms can be used for the bioremediation of pollution caused by heavy metals.3 Multiple metal resistant microbes have advantages over the single metal resistant microbes. Heavy metals and biocides are two components which itself are not as such antibiotics but they have antibiotics properties and so help in selection of the microbes which are antibiotics resistant too. This is because genes responsible for the metal resistance lie near to the genes responsible for the antibiotics resistance. 3 Experiments are underway to develop and integrated bioremediation system using some of the resistant microbes. REFERENCES 1. Cheng S. Heavy metal pollution in china: Origin, pattern and control. Environmental sciences and pollution research. 2003; 10:192-198. 2. Patterson JW. Waste water treatment technology. Ann Arbor Science publishers, Ann Arbor, MI, USA. 1977. 3. Singh V, Chauhan PK, Kanta R, Dhewa T, Kumar V. Isolation and characterization of pseudomonas Resistant to heavy metals contaminants. 2010; 2 (30):164-167. 4. Burhan A, Nisa, U, Gökhan C, Ömer C, Ashabil A, Osman G. Enzymatic properties of a novel thermostable, thermophilic, alkalineand chelator resistant amylase from an alkaliphilic Bacillus Sp. Isolate ANT-6. Proc Biochem 2003; 38: 1397- 1403. 5. Van der Maarel MJEC, Van der Veen B,Utdehaag JCM, Leenhuis H, Dijkhuizen L. Properties and applications of starch converting enzymes of the alpha amylase family. J Biotechnol. 2 0 0 2 ; 94: 137-155. 6. Gupta R, Gigras P, Mohapatra H, Goswami,VK and Chauhan B . Microbial alpha amylases: a biotechnological perspective. Proc biochem. 2003; 38 : 1599 – 1616. 7. Sindhu GS, Sharma P, Chakrabarti T, Gupt JK. Strain improvement for the production of a thermostable α- amylase. Enzy MicrobioTechnol 1997; 24:584-589. 8. Rao MB, Tanksale AM, Gathe MS, Deshpande VV. Molecular and Biotechnological aspects of microbial proteases. Microbio Mol Biol Rev. 1998; 62(3): 597-635.
  • 5. Volume 10, Issue 2, September – October 2011; Article-024 ISSN 0976 – 044X International Journal of Pharmaceutical Sciences Review and Research Page 129 Available online at www.globalresearchonline.net 9. Poonam N, Dalel S. Enzyme and microbial systems involved in starch processing. Enzyme Micro Technol. 1995; 17:770- 778. 10. Crab W, Mitchinson C. Enzymes involved in the processing of starch to sugars. Trends Biotechnology 1997;15: 349- 352. 11. Sarikayle E, Migossa T, Adachi M, Mikami B. Comparison of degradation abilities of alpha and beta amylases on raw starch granules. Proc Biochem 2000;35: 711-715. 12. Pandey A, Nigam P, Soccol CR, Soccol VY, Singh D, Mohan R. Advances in microbial amylases. Biotechnol Appl Biochem . 2000 ;31: 135–152. 13. Rehman A, Zahoor A, Munner BV, Hasnain S. Chromium tolerance and reduction potential of a bacillus sp.ev3 isolated from metal contaminates was water. Bulletin of Environmental and Contamination toxicology. 2008; 81:25- 29. 14. Silver S, Phung LT. Bacterial heavy metal resistance: new surprises. Annu. Rev. Microbiol. 1956; 50:753-89. 15. Costa M, Klein CB,. Nickle carcinogenesis, mutation, epigenetics, or selection. Environmen Heal. Perspec. PartA. 1999; 107; 438-439. 16. Chung J, Nerenberg R, Rittmann BE. Bioreduction of solution chromate using a hydrogel based membrane biofilm reactor. Water Research. 2006; 40:1634-1642. 17. Thacker U, Parikh R, Shouche Y, Madamwar D. Hesavalent chromium reduction by provideria sp. Process Biochemistry. 2006; 41:112-1337. 18. McCall KA, Huang CC, Fierke CA. Function and mechanism of zinc metalloenzymes. J of Nutri. 2000; 130:1437s-1446s 19. Joselow MM, Tobias ED, Kohler R, Coleman S, Bogden J, Gause D (1978) Manganese pollution in the city environment and its relationship to traffic density. Ann. J Pubic Health 68:557-560. 20. Singh V, Chauhan PK, Kanta R, Dhewa J, Kumar V. Isolation and characterization of Pseudomans resistant to heavy metals contaminants. Int. J. Of Pharma Sci. Review and Res. 2010.3(2):164-167. ****************