Present Day Problems on Water


In recent years bacteria have been drawing a tremendous attention due to their ability to treat waste water and thereby improve water quality.

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Hence, a study was undertaken to explore the nature of bacteria in order to exploit them as a tool in the bioremediation of dyehouse wastes. Effluent samples were collected from textile dyeing units and a Common Effluent-Treatment Plant (CETP) located in Tiruppur and Telungupalayam, Tamil Nadu. Totally 112 bacterial strains were obtained from Textile dyeing units and the CETP, based on their growth on nutrient agar medium supplemented with mixed azo dyes and their ability to decolorize mixed reactive azo dyes was studied. The effect of nutrient on decolorization revealed 0.5% of yeast extract was the best nitrogen source for up to 98% decolorization of mixed dye. Out of 112 strains 5 most effective strains were selected based on their decolorization of the dye up to 2700 mg L-1 through an acclimatization study. Optimum decolorization took place strictly under static conditions and pH and temperature were maintained constant at 7.0 and 30°C, respectively. The degradation product after decolorization was examined by TLC and FTIR. Dyehouse effluent is tough to be degraded because of the presence of dyes, which have complex aromatic molecular structure and synthetic origin. Because the color in dyehouse effluent is highly visible and affects aesthetics, water transparency and gas solubility in water, and especially because many dyes are made from known carcinogens like benzidine, dye effluent treatment becomes inevitable. In this research study, a novel fungus, paecilomyces variotii has been tried degrade the dye house effluent. The effects of environmental factor, namely the concentration of effluent on the % COD removal was determined. A kinetic model was established giving the dependence of COD removal rate on effluent COD (first order) and Biomass concentration (first order). The specific COD removal rate was calculated as
K=0.4566 1/gDCMh  at 32°C.

                 Water pollution control is at present one of the major thrust areas of scientific research. Colour removal in particular, has recently become an area of major scientific interest as indicated by Moosvi et al. (2005). Dyes are released into the environment through industrial effluents from three major sources such as textile, dyestuff manufacturing and paper industries. One of the most pressing environmental problems related to dye effluents is the improper disposal of waste water from dyeing industry. With regard to their color removal by conventional treatment methods lead to severe water pollution, thus developing cost effective clean-up operations. Microbial degradation seems to be promising compared to other organisms and the method of application are simpler compared to other available methods (Jayarajan et al., 2011). The majority of synthetic dyes currently used are the highly water soluble azo-reactive dyes. Azo dyes are characterized by the existence of nitrogen-nitrogen double bonds (-N = N-) and the bright color of their aqueous solutions. The azo-reactive dyes are used extensively in textile industries to their favourable characteristics of bright color, water-fast and simple application techniques with low energy consumption (Othman et al., 2011). Commonly used conventional treatments (biological, chemical oxidation and adsorption) often fail to generate final effluents with the required discharge quality at affordable costs (El-Shora and Metwally, 2008).
                           The removal of the polluting dyes is a serious problem, particularly for small scale textile industries where working conditions and low economic status do not allow them to treat their wastewater before disposal and they have no choice other than to dump all effluents into the main stream of water sources. Microbial decolourization and degradation is an environmental- friendly and cost-competitive alternative to chemical decomposition processes (Verma and Madamwar, 2003). At present, bioremediation relies on the pollutant-degrading capacities of naturally occurring microbial consortia in which bacteria play a central role (O’Neill et al., 2000). The ability of microorganisms to carry out dye decolorization has recently received much attention as microbial decolorization of dyes is a cost-effective method for removing them from the environment (Kalyani et al., 2008).
                             Approximately 10,000 commercial dyes and dyestuffs are used in the coloring industries (Robinson et al., 2001). As more than 10% of the dyestuff used during these dyeing processes does not bind to the fibers, large amount of dyes are released into the environment, therefore resulting in serious environmental pollution (Pearce et al., 2003) .The physical and chemical methods have disadvantages of being highly expensive, coupled with the formation of large amounts of sludge and the emission of toxic substances. In addition, the accumulation of concentrated sludge creates an additional disposal problem. The general approach of bioremediation is to improve the natural degradation capacity of the native organism. Several microorganisms have been reported by a number of investigators which have the capacity to decolorize various textile azo dyes (An et al., 2002; Sarnaik and Kanekar, 1999). The degradation of azo dyes produces aromatic amines which are carcinogenic and mutagenic. Recently, several reports appeared showing that the microorganism has the ability not only to decolorize dyes but also to detoxify it (Adedayo et al., 2004; Kumar et al., 2007; Rajaguru et al., 2000). The process of biodegradation is a well-established and powerful technique for treating domestic and industrial effluents. Microbial populations has an amazing and extensive capacity to degrade a variety of organic compounds (Manogari et al., 2008).
Currently, extensive research is being focused on finding an optimal microbial biomass that would be as cheap as possible for the removal of contaminating dyes from large volume of polluted water (Youssef et al., 2008). In this study, the screening of bacteria from dye effluent was done for adapting them for maximum removal of textile dye.
                         Azo dyes are widely used in textile finishing and have become of concern in wastewater treatment because of their color, bio-recalcitrance and potential toxicity to animals and humans. Thus, wastewater with azo dyes must be decolorized and furthermore mineralized in appropriate systems (Chang et al., 2000; Uddin et al., 2007). An attempt was made to isolate bacterial strains from dyewaste effluent and their decolorization efficiency was studied.
                   Composting is the process of converting all biodegradable into organic manure. In composting process certain input should be made into waste to convert the process in a short time. The major input in the compost process is microbial inoculant for composting. The microbial inoculant contains microbial consortia with different microorganism targeting different substrate. The promising microbes are Pleurotus, Trichoderma, Bacillus,  Pseudomonas and Streptomyces. In the Department of Environmental Studies, microbial consortia contains several promising microns are blended in a lignite based material and being sold as biomineralizer. Application of biomineralizer to the waste material quickly accelerate the composting process. Cowdung is the other important input for composting. Cowdung is the source of  nitrogen as well as microorganism.
                  The Noyyal river is a tributary of the Cauvery, a large interstated river which cuts through the States of Karnataka and Tamilnadu and enters the Bay of Bengal. The Noyyal flows through the districts of Coimbatore, Erode and Karur and the urban centres of Coimbatore and Tiruppur, in western Tamilnadu (see Map 1). A number of industrial units such as textile units, chemicals, and electroplating are located in the river basin which discharge their untreated and partially treated effluents into the river. In addition, sewage from Coimbatore and Tiruppur cities is also being discharged into the river without much treatment, making the Noyyal one of the highly polluted rivers in the country.
                  The Noyyal is a seasonal river which has good flow only for short periods during the North-East and South-West monsoons. Occasionally flash floods occur when there is heavy rain in the catchment areas. Apart from these periods, there is only scanty flow for most parts of the year. The river supplies water to several irrigation tanks located in and around Coimbatore town and downstream3. Nearly 6,000 acres of cultivable land in Coimbatore district are irrigated using the river water.
                  The Noyyal river basin covers a total area of 3510 km2 and is located between north latitude 10056’ and 11019’ and east longitude 76041’ and 77056’. The length of the Noyyal river is about 170 km from west to east. The average width of the basin is 25 km. The basin is widest in the central part with a width of 35 km.
                  The entire area of the basin is situated in the state of Tamilnadu, in parts of Coimbatore, Erode and Karur districts. The Noyyal confluences with the Cauvery River at Noyyal village.
Drinking and Industrial Water
                          Apart from agriculture, the water resources available in the basin are also used by the domestic and industrial sectors. Since the Noyyal river is not a perennial river there is no drinking water supply scheme with the Noyyal as the source. The two major cities, Coimbatore
and Tiruppur receive water from the Bhavani in the neighbouring basin. But the villages in the Noyyal basin generally depend on ground water from public and private wells. The industries in Coimbatore and Tiruppur also depend on groundwater for their processing. In Tiruppur a ‘private
water market’ is active, which supplies water for industries and domestic sectors through lorry tankers. Recently a mega public private water supply project was commissioned to supply 185 million litres per day (mld) of water from the Cauvery river to Tiruppur for both domestic and industrial use.
Ground Water
The Noyyal basin comes mostly under hard rock. Water supply in the major portion of Noyyal river basin is derived from deep dug wells reaching 35-45 metres below ground level investing enormous amount of capital and labour which was a continuous process till the1980s to keep pace with the receding water table. After electrification of wells there has been considerable increase in ground water withdrawals which in turn is depleting the groundwater level below
50-60 metres. At this stage, borewell drilling machinery came to the market
and rich farmers went in for bore wells which depleted the ground water table further in an alarming way. Most of the open wells have been abandoned and farmers have gone in for bore wells and pump the water through compressors. Even this is not successful unless
groundwater recharge is taken up on a massive scale. In the industrial locations of the basin, particularly Tiruppur, ground water pollution is also significant.
Isolation of microorganisms from dyewaste effluent: Samples were collected from a Textile dyeing unit and three different Common Effluent Treatment Plants (CETPs) located in Tirupur and Telungupalayam, Tamil Nadu, India in the year 2009. Initially serial dilution plating technique was followed for the isolation of bacteria and then were cultivated on nutrient Agar medium with a composition of (g L-l): peptone (5.0), yeast extract (2.0), Beef extract (3.0), NaCl (5.0), agar (16.0). The plates were incubated at 30°C for 24 h. Colonies of different morphology were isolated and utilized for decolorization study.
Dyes and media: The common name of the reactive azo dyes viz., Blue RR, Red ME4B, Black B, Yellow MR, Yellow ME4G, Turquise prine, Red RR, Yellow MER, Yellow M4G, Blue MR, Red M5B, Yellow RR and Navy Blue used for the biodecolorization studies were a generous gift from the Tirupur textile unit. All other chemicals were analytical grade. The Mineral Salts Medium (MSM) of pH 7.0 contained (g L-1) the following composition NaCl (1.0), CaCl2•2H2O (0.1), MgSO4•7H2O (0.5), KH2PO4 (1.0) and Na2HPO4 (1.0).
Screening of microorganisms based on decolorization activity: Isolates were individually tested for their growth and decolorization ability on nutrient agar medium containing 100 ppm of each dye. All the dyes were prepared separately and each of the cultures was tested against a single dye. The plates were incubated at 30°C till zone formation. Based on the growth on the nutrient agar medium, secondary screening was performed with the same procedure on solid MSM medium incorporated with 10 ppm of different dyes.
Acclimatization study: The acclimatization was done by gradually exposing the isolates to increasing concentrations of four different mixed azo dyes viz., Blue RR, Black B, Red RR and Yellow RR. The stock mixture contained 250 mg-l of each dye. Cultures which were obtained from secondary screening were utilized for the study. The set-up contained liquid MSM composed of 100 ppm of mixed dye amended with optimized concentration of 0.5% yeast extract. When decolorization occurred, an additional 200 ppm of dye was added to the same flask. Likewise the dye was added in increasing concentrations to the decolorized medium. Consecutive cycles of dye decolorization were studied by the repeated additions of mixed dye to the medium.
Influences of additional sources of carbon and nitrogen on decolorization efficiency of mixed azo dyes: Five Efficient Strains (ES) were selected from the acclimatization study and their efficiency of decolorization was studied in three separate C and N source media, namely Liquid MSM containing 0.5% of yeast extract, a second containing MSM with 1% glucose and a third with MSM alone. The media were inoculated with the respective bacterial strains by adding inocula of uniform cell density (λ600 =1 OD). The medium to inoculum ratio (v/v) was 50:1. All the cultures were incubated at 30°C. The absorbance was measured at its maximum of 598 nm against a blank. Decolorization of the medium was observed on a daily basis using spectrophotometric readings at 598 nm. The percentage of decolorization was calculated as follows:% Decolorization = Initial absorbance - Observed absorbance/Initial absorbance x 100
A total of 112 strains were isolated from various places in and around Tirupur city including dyeing unit and CETP plant .During primary screening, the percentage of 48.21 isolates were obtained from Textile dyeing unit and CETP resolves 51.78% . Upon secondary screening about 10.71% of isolates represent dyeing unit and 33.92% represent CETP were obtained when cultured on MSM containing the dye as only source of C and N.. From acclimatization study, out of 50 isolates checked only 10% of isolate represent CETP had effective decolorization ability was obtained. The isolates from dyeing unit resolved only 2% of total isolates. Finally out of 112 isolates the 5 most effective isolates were included for further analysis.
Analysis of biodegraded product: The degraded product was extracted from the efficient strains. Cells were centrifuged and supernatant was extracted with equal volume of ethyl acetate and then dried over anhydrous sodium sulphate. The residue was dissolved in a small amount of methanol and this was utilized for a TLC test. The developing solvent systems used were ethyl acetate: hexane (2:3, v/v) for biotransformed intermediates/products and ethyl acetate: methanol (7:3, v/v) for residual dye. The bands of aromatic components were observed under UV light (365 nm) and other bands were observed by exposing the plates to iodine vapor in an iodine chamber. Dry pellets were utilized for FTIR spectral analysis.
Throughout India, there is grave concern and constant attention given to the treatment of industrial effluents from textile and dye manufacturing units. Several researchers have demonstrated the possibility of utilizing microorganisms for biotreatment of textile wastewater. In India, most textile units are scattered and/or operated from private homes. Therefore, it is necessary to collect and treat the waste in common effluent treatment plants. Biological methods are simple to use and the cost of operation is low (Padmavathy et al., 2003).
Screening of microorganism: The present investigation describes the isolation of native bacterial strains from different dye units with the ability to decolorize azo dyes. Totally 112 isolates were obtained from dyewaste effluents of Tirupur and Telungupalayam dye units. A significant growth was observed on Nutrient agar medium incorporated with 100 ppm of different dyes. All the 112 isolates were tested for their decolorization ability on MSM supplemented with 10 ppm dye concentration. We isolated 50 strains from secondary screening using which decolorization was done in MSM. These 50 strains were adapted to high dye concentrations as they were collected from sites near textile industries. The effectiveness of microbial decolorization depends on the adaptability and the activity of selected microorganisms (Abd El-Rahim and Moawad, 2003).
Acclimatization study: The acclimatization was done by gradually exposing the selected 50 isolates (obtained from secondary screening) in increasing concentrations of dye. Decolorization occurred only when nitrogen source was available in the growth medium. Most of the Dyeing unit in and around Tirupur region utilizing reactive dyes for dyeing fabrics. Thus our microbe have significant potential for decolorization of reactive textile dyes and are an important and promising material for the removal of reactive dyes from textile effluents. Consecutive cycles of dye decolorization were studied by the repeated additions of mixed dye to the medium. Since waste of textile industries consist of a mixture of various dyes, the ability of the different isolates to decolorize the mixed textile dyes was studied. The set up contained 0.5% of yeast extract.
Yeast extract was found to be the most effective supplement for promoting higher decolorization efficiency. Such organic nitrogen sources are considered essential media supplements for the regeneration of NADH that act as electron donors for the reduction of azo dyes by microorganisms (Khehra et al., 2005).
All the decolorization experiments were done under static conditions. Of the total isolates, the five most efficient stains (3.57%) were obtained through acclimatization capable of decolorizing 2700 ppm of mixed dye within 13 days of incubation. Our isolate KP 23 took 24 h for 98% decolorization of initial 100 ppm dye. The dye was added additionally as soon as in the decolorized medium. Like wise the dye was added in increasing concentration in the decolorized medium. The results are summarized in Table 1. Upon the addition of final dye (total concentration 2700 ppm) the decolorization efficiency was only 76%. Since the isolate KP 23 represent CETP can be effectively utilized for the treatment of real textile effluent .
Table 1:            Effect of continuous addition of mixed azo dye in the ongoing study of superior strain KP 23 (obtained from CETP)


Total dye added in medium(ppm)







Azoreductase-driven bacterial decolorization of azo dyes is inhibited by the presence of oxygen primarily owing to the competition in the oxidation of reduced electron carriers (e.g., NADH) with either oxygen or azo groups as the electron acceptor. In static incubation, only a trace amount of oxygen was transferred, probably onto the broth surface and thus, the cells mostly sedimented to the bottom of the flasks were likely to undertake decolorization under anaerobic conditions (Mathew and Madamwar, 2004).
However, the isolates proved very effective in their decolorization capability and therefore it can be utilized for real dyewaste water treatment. The acclimatization was done by gradually exposing Pseudomonas sp. SUK1 to increasing concentrations of dye. Pseudomonas sp. SUK1 was consecutively transferred into the nutrient medium with increasing concentration of Red BLI dye up to 600 mg L-1 at 30°C and static conditions. (Kalyani et al., 2008). The decolorization potential of Reactive Yellow 42 (RY 42), Reactive Blue 13 (RB 13) and Reactive Red 58 (RR 58) by the bacterium Micrococcus sp was investigated by Olukanni et al. (2009).
The repeated use of microorganisms is important from the commercial point of view. This study was carried out to examine the ability of a pure culture to decolorize repeated additions of mixed azo dyes in static condition. The decolorization of the dye solution could be selectively supported by the media composition. The yeast extract medium was the most suitable for the decolorization of dye. However, we were not successful in isolating bacteria capable of decolourizing and utilizing only dyes as the sole source of carbon and energy.
Decolourization occurred only when additional nitrogen energy source was available in the growth medium. The culture exhibited the ability to decolourize repeated additions which is significant for its commercial application. Normally the dye concentration in the effluent varies within a narrow range of 0.1-0.2 g L-1 (O’Neill et al., 2000). Isolates could decolourize dyes far above the reported dye concentration in wastewaters and thus could be successfully employed for treatment of dye-bearing industrial wastewaters. Moreover, it exhibited efficient decolourizing ability even for mixed dye tests.
Effect of carbon and nitrogen source: All the 5 ES namely TU57, TR26, VP9, KP27, KP23 were tested for their decolorization activity in liquid MSM medium supplemented separately with 1% glucose, 0.5%yeastextract and MSM alone. Other inorganic sources were also tried for the effective decolorization of dyes but isolates could not able to utilize as growth factor also we found no growth in those medium (data not shown) Spectrophotometric analysis revealed that the strains could utilize the mixed dye (100 ppm) and decolorize it up to 83.8-91.8% when 0.5% of yeast extract was supplemented in the medium (Fig. 1). However, Glucose (Fig. 2) resolved only 5.8-11.1% of decolorization, while we could achieve only 1.04-2.08% of decolorization (Fig. 3) when dye alone was used.
Fig. 1:   Effect of yeast extract (0.5%) on decolorization of 100 ppm of mixed dye

Fig. 2:   Effect of glucose (1%) on decolorization of 100 ppm of mixed dye

Fig. 3:   Effect of dye alone for the decolorization of 100 ppm of mixed dye

 The ES could not utilize dye as the sole source of C and N. It was observed that the decolorization was due to degradation since the centrifuged pellet of the isolates after decolorization showed a white pellet instead of dye colour.
Study revealed that the isolates were able to decolorize the dye up to 91% when 0.5% of yeast extract was supplemented in the medium (Joshi et al., 2008). Yeast Extract (YE) alone resulted in much higher decolorization of AO7 as compared to glucose alone, peptone or starch when novel microbial consortia were used. The yeast extract medium was most appropriate for the decolorization of dye Navy blue 2GL as compared to the beef extract and nutrient broth medium (Dawkar et al., 2009). An earlier report showed that maximum decolorization of Acid Black 210 by Vibrio harveyi TEMS1 was observed when the yeast extract concentration was 5 g L-1 (Ozdemir et al., 2008). The decolorization efflciency is strongly affected by the medium compositions. Organic nitrogen sources such as peptone or yeast extract incorporation shows higher decolourization when compared with inorganic sources nitrate and ammonium chloride (Ramya et al., 2008). Yeast extract, a powder supplement consisting of protein, free amino nitrogen, B vitamins, minerals, nucleotides and other yeast cell components, has been the most commonly used nitrogen source for dye decolourization processes. A number of studies reported that yeast extract was the best nitrogen source for efficient decolorization of various textile dyes.
This may be owing to the metabolism of yeast extract which is considered essential for the regeneration of NADH. Many pure cultures like Pseudomonas luteola, Klebsiella pneumoniae and Aeromonas hydrophila have exhibited effective decolourization of different dyes in the presence of yeast extract (Elisangela et al., 2009) With glucose as the only carbon source, the culture showed negligible decolourization (5.57%), while with yeast extract as the sole carbon source, 23% decolourization of RV 5 was observed (Moosvi et al., 2005) The growth of Pseudomonas luteola was directly related to the concentration of yeast extract and when the concentration of yeast extract was reduced growth and colour removal decreased (Hu, 1998). The ability of Staphylococcus aureus, Bacteroides fragilis, Bacillus subtilis, Bacillus cereus, Clostridium perfringens, Escherichia coli and Peptostreptococcus spp. to reduce and stabilize textile effluents containing predominantly indigo blue was carried out by Ajibola et al. (2005).
TLC and FTIR result of biodegraded product: The dye decolorization study of bacterial isolate was further supported by TLC analysis. When the dye chromatogram was observed in UV light, the brown spot (Table 2) with Rf value 0.24, 0.3, 0.3, 0.25 and 0.3 were observed, while no such bands were observed for spots of dye and uninoculated medium, indicating that decolorization was due to dye degradation.
Fourier Transform Infrared Spectroscopy (FTIR) analyses were done for the control and the decolorised sample (Fig. 4 and 5) the results of which showed various peaks. The FTIR spectrum of control mixed dye displayed a peak at 3,415 cm-1 for the intramolecular hydrogen bonding aromatic -OH and O-H stretching;a peak at 2,929 cm-1 for C-H stretching of alkyl acetals and a peak at 2,445 cm-1 for N-H stretching of amines; a peak at 1,618 cm-1 for C = N stretching of azo group; a peak at 1,047 cm-1 for S = O stretching of sulfonic acid; a peak at 892 and 665 cm-1 for aromatic nature and C-Cl stretching, respectively. The degradation metabolites of mixed dye showed a peak at 3,227 cm-1 for secondary amides, 1,654 cm-1 for C = C and C = N stretching and presence of amide bond, a peak at 1,404 cm-1 for O = H stretching and a peak at 620 cm-1 for C-Cl stretching indicating the presence of alkyl chloride. It indicated formation of nitrosamines, alkyl chloride, secondary and tertiary amides after decolorization. We had used a mixture of azo dyes, so it was not possible to compare the parent dye compound with the decolorized compound because we did not know which peak was from which compound. As we obtained different peaks for the parent compound and the decolorized compound it confirmed that it was degraded by the strain KP23.
The chemical structure of the dyes greatly influenced their decolourization rates and the decolourization efflciency is limited to several azo dye structures. Dyes with simple structures and low molecular weights usually exhibited higher rates of colour removal, whereas colour removal was more difficult with highly substituted, high molecular weight dyes. For this reason, RY107 and RR198 which are both monoazo, showed a short decolourization time (12 and 10 h, respectively), while the highly substituted diazo RB5 and the triazo DB71 showed longer decolourization times (24 and 48 h, respectively). It has been reported that the turnover rate of monoazo dyes increased with increasing dye concentration, whereas the turnover rate of the diazo and triazo dyes remained constant as the dye concentration increased. Moreover, the azo compounds with hydroxyl or amino groups were more likely to be degraded than those with methyl, methoxy, sulfo or nitro groups. Usually, the presence of sulfonates in reactive dye structures resulted in low levels of colour removal (Elisangela et al., 2009).
It was observed that the significant level of bioremediation indicated the ability of the isolate ES to withstand high concentrations of azo dyes during the bioremediation process. The ES could decolorize mixed azo dyes at much above the reported dye concentration in the wastewaters and thus can be used successfully in the commercial treatment of textile wastewaters. The toxicity analysis of degraded product is under process.

  1. Abd El-Rahim, W.M. and H. Moawad, 2003. Enhancing bioremoval of textile dyes by eight fungal strains from media supplemented with gelatine wastes and sucrose. J. Basic Microbiol., 43: 367-375.
  1. Adedayo, O., S. Javadpour, C. Taylor, W.A. Anderson and M. Moo-Young, 2004. Decolourization and detoxification of methyl red by aerobic bacteria from a wastewater treatment plant. World. J. Biotecnol. Microbiol., 20: 545-550.
  1. Ajibola, V.O., S.J. Oniye, C.E. Odeh, T. Olugbodi and U.G. Umeh, 2005. Biodegradation of indigo containing textile effluent using some strains of bacteria. J. Applied Sci., 5: 853-855.

Antonette Idaa Sherley.J
Student, Department of EEE, Angel College of Engineering and Technology, Tirupur.
E-paper Presentation for E-Fest 2011 Contest


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Posted On:  Thursday, 11 October, 2012 - 18:20

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