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ISOLATION AND CHARACTERIZATION OF CHROMIUM REMOVING BACTERIAzinc, cobalt <strong>and</strong> <strong>chromium</strong>. Among heavymetals <strong>chromium</strong> is the major pollutant <strong>of</strong> theleather tanning industry <strong>and</strong> is toxic to plants<strong>and</strong> animals around the environment [9].The damage to the environment by thehazardous tannery effluent is becoming anacute problem in several countries. Thechrome tanning process results in toxicmetals, especially <strong>chromium</strong> III passing towaste water <strong>and</strong> are not easily eliminated byordinary treatment process [13]. Tannerywaste waters are mainly characterized byhigh salinity, high organic loading <strong>and</strong>specific pollutants such as <strong>chromium</strong> [10].The industrial effluent released directly orindirectly into natural water resources, mostlywithout proper treatment, poses a majorthreat to the environment.Among the different forms <strong>of</strong> <strong>chromium</strong>, thehexavalent <strong>chromium</strong> Cr 6+ is the most toxic<strong>and</strong> carcinogenic due to its high solubility inwater, rapid permeability through biologicalmembranes <strong>and</strong> subsequent interaction withintracellular proteins <strong>and</strong> nucleic acids. Theheavy metals in general cannot bebiologically transformed to more or less toxicproducts <strong>and</strong> hence persist in the environmentindefinitely [35]. They are significantly toxiceven in small amounts <strong>and</strong> can cause diseasesin humans <strong>and</strong> animals as they causeirreversible changes in the body, especially inthe Central Nervous System [26]. Soilcontamination by heavy metals is <strong>of</strong>tenirreversible <strong>and</strong> may repress or even kill parts<strong>of</strong> the microbial community <strong>and</strong> it isgenerally assumed that the exposure to metalsleads to the establishment <strong>of</strong> a tolerant/resistant microbial population [32].Microorganisms play a significant <strong>and</strong> vitalrole in bioremediation <strong>of</strong> heavy metalcontaminated soil <strong>and</strong> wastewater.Indigenous soil microbes appear well suitedfor Chromium (VI) transformation in highlycontaminated soil <strong>and</strong> may accumulate<strong>chromium</strong> within its cells by adaptation to thehigh concentration <strong>of</strong> the metal. Very stablefinal <strong>chromium</strong> forms can be achieved as aresult <strong>of</strong> microbial activity, with minimal risk<strong>of</strong> re-release <strong>of</strong> Cr (VI) [22]. In this paper aneffort has been made to remove heavy metals<strong>from</strong> tannery effluent using microorganisms.[II] MATERIALS AND METHODS2.1 Tannery EffluentThe effluent was collected <strong>from</strong> a selectedleather processing industry situated atDindigul in Tamil Nadu, India at weeklyintervals for five weeks, pooled together <strong>and</strong>stored at 4 °C for analysis. The collectedtannery effluent was analyzed forphysicochemical properties like colour,odour, turbidity, pH, total suspended solids,total dissolved salts, chemical oxygendem<strong>and</strong> (COD), biological oxygen dem<strong>and</strong>(BOD) [1], carbonate, bicarbonate, sodium,potassium [20], <strong>chromium</strong>, copper,cadmium, nickel <strong>and</strong> zinc [1].2.2 Isolation <strong>of</strong> the microorganism <strong>from</strong>tannery effluent contaminated soilFor <strong>isolation</strong> <strong>of</strong> <strong>chromium</strong> resistant <strong>bacteria</strong>,1.0 g effluent treated soil sample wasdispersed in 100 mL <strong>of</strong> the sterile distilledwater. A serial dilution was made up to 10 -5<strong>from</strong> the effluent treated soil sample. 100 µL<strong>of</strong> each dilution was spread on to nutrientplates containing 10 µg potassiumdichromate (K 2 Cr 2 O 7 ) per mL <strong>of</strong> themedium. The growth <strong>of</strong> the <strong>bacteria</strong>l colonieswas observed after 24 h <strong>of</strong> incubation at 37°C. It was subcultured on nutrient agar platecontaining 10 µg <strong>of</strong> potassium dichromate(K 2 Cr 2 O 7 ) per mL. Biochemical tests likeGram staining [27], dextrose fermentation,sucrose fermentation, IMViC, catalaseactivity, starch hydrolysis [11] <strong>and</strong> gelatinSmrithi A <strong>and</strong> Usha K 645

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