@Research Paper <#LINE#>Study of Yearly Variation and Physico-Chemical study of River Water, Underground Water and Surface Water of Rewa City, MP, India<#LINE#>Manoj Kumar @Solanki,O.P.@Gupta,Shukdeo Prasad @Ahirwar<#LINE#>1-4<#LINE#>1.ISCA-IRJEvS-2013-146.pdf<#LINE#>3 Department of Chemistry, Govt. Engineering College, Rewa-486001, MP, INDIA @ Department of Chemistry, Govt. Science College, Rewa-486001, MP, INDIA @ Department of Chemistry, Govt. PG College, Niwari, Tikamgarh-472442, MP, INDIA <#LINE#>25/6/2013<#LINE#>12/7/2013<#LINE#>This paper present to the yearly variation and physico - chemical study of river water, underground water and surface water of rewa District, Madhya Pradesh state. The variable data of samples are within prescribed limits as suggested by World Health Organisation and Indian Standard institute and BIS desirable limit for drinking water for drinking purpose. Yearly variation in physical and chemical parameters like colour, odour, taste, total hardness, pH, total dissolved solids, total alkalinity, nitrate, chloride, sulphate, carbonate, bicarbonate, calcium, magnesium, BOD, COD in water. Were analyzed for a period of year 2012 and 2013 (summer). Were river water is indicated by Sample A , underground water is indicated by Sample B and surface water is indicated by Sample C . Some Parameters were found in some limits. <#LINE#> @ @ Manoj Kumar Solanki and O.P. Gupta, Physico-chemical and comparative analysis of river water, underground water and surface water of Rewa city MP, India, Poll Res., 32(2) 235-237 (2013) @No $ @ @ Jasrotia A.S. and Singh R., Hydro ISI. (1991) Indian standard specification for drinking water IS: 10500, Indian Standard Institution, 1-chemistry and ground water quality around Devak and Rui watershed of Jammu Region, Jammu and Kashmir Jour. Geol. Soc., India, 69, 1042-1054 (2007) @No $ @ @ Determination of turbidity by nephelometry, August, Edited by James W. O' DellInorganic Chemistry Branch, Chemistry Research Division, (1993) @No $ @ @ Taylor E .W., The examination of water and water supplies, J. and Churchill Ltd , London, (1949) @No $ @ @ Yadav Janeshwar, Pathak R. K., Rathour J aypal and Yadav Ankit, Physico-Chemical Analysis of Water and Locked Soil of Sadli Reservoir, Region Kasrawad, District Khargone M.P. INDIA, International Research Journal of Environment Sciences, 2(4), 26-29 (2013) @No $ @ @ Chaurasia Sadhana and Karan Raj, Water Quality and Pollution load of River Mandakini at Chitrakoot, India, International Research Journal of Environment Sciences, 2(6), 13-19 (2013) @No $ @ @ Dubey Savita, Analysis of Physico-Chemical Parameters of Kshipra river Water at Ujjain, International Research Journal of Environment Sciences, 2(7), 1-4 (2013) @No $ @ @ Kumar Naresh, Singh Ankusha and Sharma Priya, To study the Physico-Chemical properties and Bacteriological examination of Hot Spring water from Vashisht region in Distt. Kullu of HP, India, International Research Journal of Environment Sciences, 2(8), 28-31 (2013) @No $ @ @ Smitha, Ajay D. and Shivashankar P, Physico Chemical Analysis of the Freshwater at River Kapila, Nanjangudu Industrial Area , Mysore, India, International Research Journal of Environment Sciences, 2(8), 59-65 (2013) @No $ @ @ Neelesh Shrivastava, Mishra D.D., Mishra P.K. and Avinash Bajpai, A study on the sewage disposal into the Machna river in Betul City, Madhya Pradesh, India, Advances in Applied Science Research, 3(5), 25 73-2577 (2012) @No $ @ @ Tripathi A.K., Mishra U.K., Mishra Ajay and Dubey Parul, Assessment of Groundwater Quality Gurh Tehseel, Rewa District, Madhya Pradesh, India, 3(9), 2229-5518 (8) (2012) @No $ @ @ Mishra U.K., Tripathi A.K., Saras Tiwari and Ajay Mishra ,Assessment of Quality and Pollution Potential of Groundwater around Dab haura Area, Rewa District, Madhya Pradesh, India, 1(2), 1927-0550 (2012) @No $ @ @ Basavaraja Simpi, S.M. Hiremath, KNS Murthy, K.N. Chandra shekar appa, Anil N Patel, E.T. Puttiah, Analysis of Water Quality Using Physico-Chemical Parameters Hosahalli Tank in S. himoga District, Karnataka, India, 11(3), (2011) @No $ @ @ A. Agarwal, and M.Saxena, Assessmen to pollution by physic chemical water Advanced applied science research, 2(2) 185-189 (2011) @No $ @ @ Madhnure P., Sirsikar D.Y., Tiwari A.N., Ranjan B. Malpe D.B., Occurrence of fluoride in the ground waters Pandharkawada area, Yawatmal district, Maharastra, India, Curr. Sci,92(5), 675–679 (2007) @No $ @ @ Shakya Suman K., Alarming Trend's of River pollution in Kathmandu Nepal, A Journal of the environment, 6(7) (2001) @No <#LINE#>Effect of sewage on Growth Parameters and Chlorophyll content of Trigonella foenumgraecum (Methi)<#LINE#>Manisha@Pathrol,Angoorbala@Bafna<#LINE#>5-9<#LINE#>2.ISCA-IRJEvS-2013-158.pdf<#LINE#> Department of Biochemistry, Govt. Holkar Science College, Indore, MP, INDIA<#LINE#>5/7/2013<#LINE#>13/8/2013<#LINE#>Urban centers are discharging waste water into the water bodies and for irrigation in the agriculture fields. The major sources of organic pollution in fresh water bodies are sewage which contains various wastes. Disposal of waste water is one of the major problem of Indore & also other cities of Madhya Pradesh. So the this study was aimed to study the effect of different dilutions i.e 100%, 75%, 50%, 25% and 0% of sewage of Krishnapura nallah Indore on growth parameters and chlorophyll content of Trigonella foenumgraecum. The parameters studied were germination percentage, root length, shoot length, vigour index, fresh weight, dry weight and viability percentage, and chlorophyll content. At all the studied dilutions there was decrease in germination percentage, viability percentage, dry weight, total chlorophyll, chlorophyll a, and chlorophyll b content but increase in root length , shoot length, vigour index, and fresh weight. Maximum decrease in germination percentage (12.67%), viability percentage (10%) occurred at 0% and 25% dilutions respectively. Maximum increase in root length (18.65%) and shoot length (12.5%) occurred at 75% dilution of sewage. The vigour index reached its maximum increase (16.83%) at 25% dilution of sewage. In fresh weight and dry weight maximum increase (19.2%) and maximum decrease (32.07%) occurred at 50% and 25% 0r 0% dilution respectively. Maximum decrease in total chlorophyll (26.9%), chlorophyll a (75%) and chlorophyll b (22.44%) occurred at 50% and 0% respectively. <#LINE#> @ @ Nagajyothi P.C., Dinakr N., Suresh S., Udaykiran Y., Suresh C. and Damodharam T., Effect of industrial effluent on the morphological parameters and chlorophyll content of green gram (PhaseolusaureusRoxb, Journal of Environmental Biology, 30, 385-388 (2009) @No $ @ @ Otobbang E., Sadovnikova L., Lakimenko O., Nilsson I.and Persson J., Sewage sludge: Soil conditioner and nutrient source, II. Availability of Cu, Zn, Pb, and Cd to barley in a pot experiment, Acta Agric.Scand.Soil Plant Science, 47, 65-70 (1997) @No $ @ @ Hicks R.W. and Hird C., Soil and urban land use In Soil Their properties and management (Eds.: P.E.V. Charman and B.W. Murphy), 2nd Edn.Oxford University Press, 378-399 (2000) @No $ @ @ Bakhsh K. and Hassan S., Use of sewage water for radish cultivation: Acase study of Punjab, Pakistan J. Agric. Soc. Sci., , 322-326 (2005) @No $ @ @ Rehman S., Harris P.J.C. and Bourne W.F., Effect of pre-sowing treatment with calcium salts, Acaciaseeds, J.Plant Nutrition, 21, 277-285 (1998) @No $ @ @ Kabir M., Iqbal M.Z., Shafiq M. and Farooqi Z.R., Reduction in germination and seedling growth of Thespesia populnea l., caused by lead and cadmium treatments, Pak. J. Bot.,40(6), 2419-2426 (2008) @No $ @ @ Abdul Baki A.A. and Anderson J.D., Vigour determination of soyabean seeds by multiple criteria, Crop.sci., 13, 630-633 (1973) @No $ @ @ Lakon G., The vigour of seeds and its determination by Topographically Tetrazonium method, Saatgutwirtschaft, ,37-41 (1942) @No $ @ @ Sadasivam S. and Manickam A., In: Biochemical Methods for Agricultural Sciences, Willey Eastern Limited, New Delhi,184-185 (1992) @No $ @ @ Khan M.A., Kazi T.G., Ansari R., Mujtaba S.M., Khanzada.B., Khan.M.A., Shirani M.U. and Mumtaz S.,Effect of untreated sewage sludge on Wheat yield, metal uptake by grain and acculumation in the soil, Pakistan journal of Botany, 39(7), 2511-2517 (2007) @No $ @ @ Dash A.K., Impact of Domestic Waste Water on Seed Germination and Physiological parameters of Rice and Wheat, IJRRAS, 12(2), 2-5 (2012) @No $ @ @ Girisha S. and Raju N., Effect of Sewage Water on Seed germination and Vigour index of different Varieties of Groundnut (Arachis hypogea l.), Journal of Environmental Biology, 29(6), 937-939 (2008) @No $ @ @ Sawaf N., Response ofSorghumspp. to Sewage Waste-water Irrigation, International Journal of Agriculture & Biology,07(6), 869–874 (2005) @No $ @ @ Bazai Z.A. and Kabir Khan Achakzai A., Effect of waste water from Quetta city on the Germination and Seedling Growth of Lettuce (LactucasativaL), Journal of Applied Sciences, 6(2), 380-382 (2006) @No $ @ @ Tamrabet L., Bouzerzour H., Kribaa M. and Makhlouf M., The effect of sewage sludge application on Durum Wheat (Triticum durum), International Journal of Agriculture &Biology, 11(6), 741–745 (2009) @No $ @ @ Khan M.G., Danle G.l, Konji M., Thomas A., Eyasu S.S. and Awoke G., Impact of textile waste water on seed germination and some physiological parameters in pea (Pisum sativumL.), Lentil (Lens esculentum L. and gram (Cicer arietinum L.), Asian Journal of PlantScience, 10, 269-273 (2011) @No $ @ @ Liu D., Wang Y. and Zang X., Si Q., Effect of sewage irrigation on wheat growth and its activating oxygen metabolism, 13(10), 1319-22 (2002) @No <#LINE#>Physicochemical Study of Kanhan River Water Receiving Fly Ash Disposal Waste Water of Khaperkheda Thermal Power Station, India<#LINE#>PreranaB.@Thorat,Vijay N.@Charde <#LINE#>10-15<#LINE#>3.ISCA-IRJEvS-2013-160.pdf<#LINE#>Department of Chemistry, Arts, Commerce and Science College, Koradi, Dist Nagpur 441 111, INDIA @ Department of Microbiology, Arts, Commerce and Science College, Koradi, Dist Nagpur 441 111, INDIA<#LINE#>10/7/2013<#LINE#>28/8/2013<#LINE#>Fly ash resulting from coal- based thermal power plants is one of the alarming and continuously increasing sources of pollution leading to degradation of soil, water and air. Fly ash generated from thermal power plant and industrial waste discharged into the streams or dumped into surrounding land causes serious water and soil pollution problems. In the present study various parameters were studied to monitor the pollution of Kanhan River water due to water runoff from ash bund of Khaparkheda Thermal Power Station. These parameters produce various effects on environment and human being therefore their presence in water body is matter of concern. Values of conductivity, total dissolved solids, turbidity, chemical oxygen demand, alkalinity, hardness, and chlorides were very high in side stream water than the desirable values for drinking water. Concentration of copper, cadmium, zinc, lead, mercury and arsenic metals were observed within normal range posing no threats of pollution of heavy metals in water due to ash bund. <#LINE#> @ @ Shamshad A., Fulekar M.H.and Pathak B., Impact of Coal Based Thermal Power Plant on Environment and its Mitigation Measure, International Research Journal of Environment Sciences, 1(4), 60-64 (2012) @No $ @ @ Senapati M.R., Fly ash from thermal power plants – waste management and overview, Current Science, 100 (12), 25 (2011) @No $ @ @ Sharma S., M.H.Fulekar, Jayalakshmi C.P. and Straub C.P.,Fly ash dynamics in soilwater systems, Critical Reviews in Environmental Control ,19(3), 251-275 (1989) @No $ @ @ Ashoka D., Saxena M. and Asholekar S.R., Coal Combustion Residue-Environmental Implication and Recycling Potential, Resource Conservation And Recycling,,1342-1355, (2005) @No $ @ @ Asthana D. K., Asthana M., Environment, problems and solution (2001) @No $ @ @ National Environmental Engineering Research Institute Nagpur, Manual on water and waste water analysis, (1988) @No $ @ @ Chhatwal G.R., Mehra M.C., Satake M., Katyal T., Katyal M. and Magahiro T., Environmental Analysis, 130 (1989) @No $ @ @ IS: 3025 (PART II) ( 2004) @No $ @ @ Diwedi S. , World Academy of Science, Engineering and Technology, 71, (2010) @No $ @ @ Junshum P., Menasveta P. and Traichaiyaporn S., J. Agri. Soc. Sci.,3(3), (2007) @No $ @ @ De S., Mishra D. D., Jain B, and Bajpai,A., poll.res.26(3), 457-458, (2007) @No <#LINE#>Assessment of Physico-Chemical Characteristics of Sediments of a Lower Himalayan Lake, Mansar, INDIA<#LINE#>Chandrakiran,Kuldeep@Sharma<#LINE#>16-22<#LINE#>4.ISCA-IRJEvS-2013-164.pdf<#LINE#>Department of Zoology, University of Jammu, Jammu (180006), J&K, INDIA<#LINE#>16/7/2013<#LINE#>30/8/2013<#LINE#>Sediments are one of the most important constituent of lacustrine ecosystems. The study was conducted to assess the physico-chemical properties of sediments of Lake Mansar. The texture of sediment was sandy loam with sand (>60%) as dominant particle size class. Organic matter varied from 1.91% - 3.45 % and is significantly related with total nitrogen, pH and moisture content. pH of sediment was mostly alkaline with average value of 7.55 ±0.46. Lake sediment wasmild organic and probably in a process of accumulation of organic load from catchment area due to various natural (erosion) and anthropogenic causes (tourist and construction activities). Total phosphorus was fairly high but not related to organic matter which may be contributed by the domestic discharge, community bathing and washing and agricultural run-off. Thus, environmental surveillance of lake sediments is highly recommended in order to closely monitor the quality of sediments of LakeMansar. <#LINE#> @ @ Kalff J., Limnology, Prentice Hall, New Jersey, 592 (2002) @No $ @ @ Luque J.A. and Julia R., Lake sediments response to land use and climate change during the last 1000 years in the oligotrophic Lake Sanabria (Northwest of Iberian Peninsula), Sedi. Geol., 148, 343-355 (2002) @No $ @ @ Ryding S.O., Chemical and microbiological processes as regulators of the exchange of substances between sediments and water in shallow eutrophic lakes, Int. Revue. Ges. Hydrobiol., 70, 657-702 (1985) @No $ @ @ Bostrom B., Andersen J.M., Fleischer S. and Jansson M., Exchange of phosphorus across the sediment water interface, Hydrobiologia, 170, 133-155 (1988) @No $ @ @ Battarbee R.W., The importance of paleolimnology to lake restoration, Hydrobiologia, 395/396, 149-159 (1999) @No $ @ @ Matisoff G., Fisher J.B. and Matis S., Effects of benthic macroinvertebrates on the exchange of solutes between sediments and freshwater, Hydrobiologia, 122, 9-33 (1985) @No $ @ @ Sahoo J.K., Khuntia B.K. and Sial N.K., Nutrient dynamics in the sediments of lagoonal environment of Bahuda estuary, Orissa, J. Aquat. Biol., 22(1), 39-44 (2007) @No $ @ @ Malhotra Y.R., Gupta K. and Khajuria A., Seasonal variations in the population of macrobenthos in relation to some physico-chemical parameters of lake Mansar, J. Freshwater Biol., 2(2), 123-128 (1990) @No $ @ @ Khajuria A., Studies on nekton and benthos of Lake Mansar, Ph.D. Thesis, University of Jammu, Jammu (1992) @No $ @ @ Sharma M., Ecology and community structure of zooplankton of lake Mansar (J&K), Ph.D thesis, University of Jammu, Jammu (2001) @No $ @ @ Gupta S., Studies on the diversity of cladocerans in lakeMansar, Jammu, M.Phil dissertation, University of Jammu, Jammu (2002) @No $ @ @ Kour S., Studies on the diversity of Rotifers of lake Mansar in Jammu, M.Phil dissertation, University of Jammu, Jammu (2002) @No $ @ @ Kumar V., Rai S.P and Singh O., Water Quantity and Quality of Mansar Lake Located in the Himalayan Foothills, India, Lake and reservoir management, 22(3), 191-198 (2006) @No $ @ @ Zuber S.M., Ecology and economic valuation of lake Mansar, Jammu, Ph.D. Thesis, University of Jammu, Jammu (2007) @No $ @ @ Rai S.P., Kumar V. and Kumar B., Sedimentation rate pattern of a Himalayan foothill lake using 137Cs and 210Pb, Hydrobiological sciences-Journal-des Sciences Hydrologiques, 52(1),(2007) @No $ @ @ Chandrakiran and Sharma K., Sediment characteristics as one environmental cue to influence macrobenthic community composition of lower Himalayan lake Mansar (India), International Journal of Zoology and Research, 3(1), 17-26 (2013) @No $ @ @ Sharma K. and Singh P., Dynamics of migratory waterfowl abundance at Lake Mansar (Ramsar Site): A transient and wintering site, International journal of current life sciences, 3(2), 9-13 (2013) @No $ @ @ NIH, Water quality study of Mansar Lake, in district Udhampur, J&K, Tech. Rep. No., CS (AR)- 32/96-97, 1-40, (1997) @No $ @ @ Srivastava S.K. and Banerjee D.K., Speciation of metals in sewage sludge amended soils, Water, Air, Soil Pollut., 152, 219-232 (2004) @No $ @ @ Bates R.G., Electronic pH Determinations, John Willey and Sons Inc., New York. (1954) @No $ @ @ American Society for Testing and Materials (ASTM), 1985, Standard test method for particle-size analysis of soils D. 422-63 (1972) @No $ @ @ Gerakis A. and Baer B., A computer program for soil textural classification, Soil ScienceSociety of American Journal, 63, 807-808 (1999) @No $ @ @ Walkley A. and Black I.A., An examination of the Degtjareff method for determining soil Organic matter and a proposed modification of the chromic acid titration method, Soil Sci., (37), 29-38 (1934) @No $ @ @ Bremmer J.M., Total nitrogen, In: Method of Soil Analysis, Part 2. Black, C.A. (ed.), American society Agronomy, Inc. Publ. Median, USA (1965) @No $ @ @ Olsen S.R., and L.E. Sommers, Phosphorus, 403-430. In: A.L. Page. R.H.Miller, and D.R. Keeney (eds.), Methods of Soil Analysis. 2nd ed. Agronomy Series No.9, Part 2. Soil Science Society of America, Inc., Madison, WI. (1982) @No $ @ @ Boyd C.E., Wood C.W. and Thunjai T., Pond soil characteristics and dynamics of soil organic matter and nutrients, In: Nineteenth Annual Technical Report.McElwee K., Lewis K., Nidiffer M., and Buitrago P. (eds.), Pond Dynamics/Aquaculture CRSP, Oregon State University, Corvallis, Oregon, 1–10 (2002) @No $ @ @ Last W.M., Textural analysis of lake sediments, In: Tracking Enviromantal change using lake sediments, Last W.M. and Smol J.P. (eds.), Physical and geochemical methods. Kluwer Academic Publishers, The Netherlands, , (2001) @No $ @ @ Davies O.A. and Abowei J.F.N, Sediment Quality of Lower Reaches of Okpoka Creek, Niger Delta, Nigeria, European Journal of Scientific Research, 26(3), 437-442 (2009) @No $ @ @ Davies, O.A. and Tawari, C.C., Season and tide effects on sediment characteristics of trans-okpoka creek, upper bonny Estuary, Nigeria, Agric. Biol. J. N. Am., 1(2), 89-96 (2010) @No $ @ @ Griggs, G., an investigation of bottom sediments in a polluted marine environment upper Saromkos Gulf, Greece, Report of the environmental pollution control project, Athens, Greece, 1-30 (1975) @No $ @ @ Sharma V., Sharma K.K. and Sharma A., Sediment Characterization of Lower sections of a Central Himalayan river, Tawi, Jammu (J&K), India, International Research Journal of Environment Sciences, 2(3), 51-55 (2013) @No $ @ @ Chao W., Jin Q., Zhi-yong G., Li Z. and Xiao-chen L., Vertical distribution of phosphorus fractions in sedimenst of three typical shallow urban lakes in P.R. China, Polish J. of Environ. Stud., 17(1), 155-162 (2008) @No $ @ @ Hakanson L. and Jansson M., Principles of lake sedimentology, Springer Verlag, 316 (1993) @No $ @ @ Bragadeeswaran S., Rajasegar M., Srinivasan M. and KanagaRajan U., Sediment texture and nutrients of Arasalar estuary, Karaikkal, south-east coast of India, Journal ofEnvironmental Biology, 28(2), 237-240 (2007) @No $ @ @ Avnimelech Y., Ritva G., Meiier E. and Kochba M., Water content, organic carbon and dry bulk density in flooded sediments, Aquaculture Engineering, 25, 25-30 (2001) @No $ @ @ Martynova M.V., Impact of the chemical composition of bottom sediments on internal phosphorus load, Water Resources, 35(3), 339-345 (2008) @No $ @ @ Baer F.E., Chemistry of soil (Second ed. 1988), Oxford & IEM Publishing Co. New Delhi (1965) @No $ @ @ Carpenter, S.R. and Lodge, D.M., Effects of submerged macrophytes on ecosystem processes, Aquat. Bot., 26, 341-370 (1986) @No $ @ @ Saha, L.C., Seasonal variation in bottom soil properties in two freshwater ponds, Acta. Ecol., 3(20), 15-19 (1981) @No $ @ @ Sinha A.K., Singh D.K., Baruah A. and Sharma U.P., Seasonal variation of physico-chemical properties of bottom sediments of Kawar lake, Begusarai (Bihar), J. Freshwater. Biol., 4(4), 249-254 (1992) @No $ @ @ Muller B., Murki M., Dinkel C., Stierli R. and Wehrli B., In situ measurements in lake sediments using Ion-selective electrodes with a profiling lander system, American Chemical Society, 126-143 (2002) @No <#LINE#>Removal of Lead from Waste Water Using Low Cost Adsorbent<#LINE#>Dhanesh@Singh,M.@Mishra,A.K.@Mishra,Anjali@Singh<#LINE#>23-26<#LINE#>5.ISCA-IRJEvS-2013-170.pdf<#LINE#>Deptt. of Chemistry, K.G. Arts and Science College, Raigarh, CG, INDIA @ Deptt. of Applied Sciences, Singhania University, Pacheri-Bari, Dist. Jhunjhunu, Rajasthan, INDIA <#LINE#>30/7/2013<#LINE#>26/8/2013<#LINE#>The sorption of Lead (II) on chitosan has been found to be dependent on contact time, concentration, temperature, and pH of the solution. The process of removal follows first order kinetics and absorption of heat. <#LINE#> @ @ Singh Dhanesh and Singh Anjali, Chitosan for the Removal of Chromium from Waste Water, International Research Journal of Environment Sciences, 1(3), 1-7 (2012) @No $ @ @ Singh Dhanesh and Singh Anjali, Chitosan for the Removal of Cadmium rich Water, International Research Journal of Environment Sciences, 1(4), 1-7 (2012) @No $ @ @ Devi Priyamvada, Sirisha D. and Gandhi N., Study on the Quality of Water and Soil from Fish Pond in Around Bhimavaram West Godavari District, A.P., INDIA , Int. Res. J. Environmen Sci.,2(1), 58-62 (2013) @No $ @ @ Hasan Saba, Prakash Jyoti and Singh., Mycorrhizae and Phytochelators as Remedy in Heavy Metal Contaminated Land Remediation, Int. Res. J. Environmen Sci.,2(1), 74-78 (2013) @No $ @ @ Singh P.K., Imam Afzal, Singh Ravi, Singh Dhanesh and Sharma Shivi.,A Study about Ecological Imbalance in Surguja (India) Coalfield Area Due to Mining, Int. Res. J. Environment Sci.,2(4), 10-14 (2013) @No $ @ @ Vishwakarma P.P. and Singh V.N., Removal of Pb (II) by China Clay, Asian Environment, 11(3), 49-64 (1984) @No $ @ @ Pandey K.K., Prasad G. and Singh V.N., Fly ash China Clay for the removal of Cr (VI) from aqueous solution, Indian Journal of Chemistry, 23( A), 514-515 (1984) @No $ @ @ Namasivayam C. and Yamuna R.T., Environ Pollut.,9(1), 1- 4 (1985) @No $ @ @ Sekeran G., Shanmugasundaram K.A., Mariappan M. and Raghavan K.V., Indian J Chemical Technol2(311), 71-75 (1995) @No $ @ @ Findon A., Mckay G. and Blair H.S., Transport studies for the sorption of Lead ions by chitosan, J. Environ. Sci. Health,A2 8(1), 173-185 (1993) @No $ @ @ Gotoh T., Matsushima K. and Kikuchi K.I., Preparation of alginatechitosan hybrid gel beads and adsorption of divalent metal ions, Chemosphere, 5.5 (1), 135-140 (2004) @No $ @ @ Grosse D.N., A review of alternative treatment process for metal bearing hazardous waste streams, J. Air Pollution Contr. Assor.,36, 603-614 (1986) @No <#LINE#>Lead Uptake and Accumulation in Groundnut Crop Grown at Different Soil Lead Amendments<#LINE#>N.@Lakshmi<#LINE#>27-33<#LINE#>6.ISCA-IRJEvS-2013-171.pdf<#LINE#><#LINE#>31/7/2013<#LINE#>6/8/2013<#LINE#>The present study deals with lead (Pb) uptake and accumulation in groundnut (Arachis hypogea L.var TMV-2).Pot experiments were conducted taking native agricultural soil spiked with Lead Nitrate to get 10.2.g/g, 102 g/g and 1020 g/g and growing the groundnut species at these test concentrations along with control soil. Lead uptake and accumulation in different plants of root, stem, leaf, seed and whole plant were studies at different time intervals of crop ages of 30 days, 60 days and 90 days at different soil lead (Test) concentrations in comparisons with control soil. <#LINE#> @ @ Rooney C.P, Melaren R.G. and Cresswell R.J., Distribution and Phyto avialbility of lead in a soil contaminated with lead shot, Water, Air and Soil pollut,116, 535-548 (1999) @No $ @ @ Burzynski M., The uptake and transpiration of water and the accumulation of lead by plants growing on lead chloride solutions, Acta Societatis Botanicorum. Poloniae,56, 271-280 (1987) @No $ @ @ Mahmoud W.H. and A. El-Beltagy, Isolation, Identification and potential use of lead reduction from heavy metal polluted soil, Menufiya J. Agric. Res., 23,1461-1473 (1998) @No $ @ @ Wagner G.J., Accumulation of heavy metals in crop plants and its consequences to human health, Adv. Agron.,51, 173-177 (1993) @No $ @ @ Lucky T.D. and B. Kenugopal, Metal toxicity inmammals, Plenum Press, New York and London,(1997) @No $ @ @ Ramade F., Ecotoxicity, John Wiley and sons, Chichester, 119-135 (1987) @No $ @ @ Sharma P. and R.S. Dubey, Lead toxicity in plants, Braz. J. Plant Physiol., 17, 35-52 (2005) @No $ @ @ Johnson M.S. and Eaton J.W., Environmental contamination through residual trace metal dispersal from a derelict lead-zinc mine, J. Environ.Qual., 9, 175-179 (1980) @No $ @ @ Patra M., Bhowmik N., Bandopadhyay B. and Sharma A., Comparison of mercury, lead and arsenic with respect to genotoxic effects on plant systems and the development of genetic tolerance, Environ. Exp. Bot., 52, 199-223 (2004) @No $ @ @ Voutsa D., Griman B.A. and Samara C., Trace elements in vegetables grown in on industrial area in relation to soil and air particulate matter, Environ. Pollut.,94(3), 325-335 (1996) @No $ @ @ Kabata – Pendias A. and Pendias H., Trace elements in soils and plants (2nd edn.) CRC press, Florida, USA, 365 (1992) @No $ @ @ Brunet J., Repellin A., Varrault G., Terrync N. and Zuily-fodli Y., Lead accumulation in the roots of grass pea: A novel plant for phytoremediation systems? C.R. Biologies, 331, 859–864 (2008) @No $ @ @ Estrella-Gomez N., Mendoza-Cozatl D., Moreno-Sanchez R., Gonzalez Mendoza D., ZapataPerez O., Hernandez A.M., Santamaria J.M., The pb-hyperaccumulator aquatic fern salvinia minima baker, responds to pb 2+ by increasing phytochelatins via changes in smpcs expression and in phytochelatin synthase activity, Aquat. Toxicol., 91, 320-328 (2009) @No $ @ @ Ali B.M., Vajpayee P., Tripathi R.D., Raj U.N., Singht S.N., Singhgh S.P., Phytotemediation of lead, nickel and copper by salix acmophylla boiss, Bull. Environ. Contam. 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Environ., 41, 253-261 (1992) @No $ @ @ Kumar G., Sing P.R. and Sushila, Nitrate accumulation and biomass production in sesamum indium L. seedlings in lead enriched environment, Water, Air and Soil pollut., 66, 163-171 (1993) @No $ @ @ Bashmakov D.I., Lukatkin A.S., Revin V.V., Duchovskis P., Brazaityte A. and Baranauskis K., Growth of maize seedlings affected by different concentrations of heavy metals, Ekologija, 3, 22-27 (2005) @No $ @ @ Yang Y.Y., Jung J.Y., Song W.Y., Suh H.S. and Lee Y., Identification of rice varieties with high tolerance or sensitivity to lead and characterization of the mechanism of tolerance, Plant Physiol., 124, 1019-1026 (2000) @No <#LINE#>The Impact of Torrential Rainfall in Kedarnath, Uttarakhand, India during June, 2013<#LINE#>Manish@Sharma,SunilK.@Mishra,Shuchi@Tyagi<#LINE#>34-37<#LINE#>7.ISCA-IRJEvS-2013-175.pdf<#LINE#>2 Research and Technology Development Centre, Sharda University, Greater Noida, NCR 201308, INDIA HLM Group of Institutions, Ghaziabad, INDIA<#LINE#>4/8/2013<#LINE#>15/8/2013<#LINE#>Sometime due to major accident and leakage the situation become worst for the nearby peoples. Kedarnath is a town located in the Indian state of Uttarakhand and has gained importance because of Kedarnath Temple located at the latitude of 30.73 and the longitude of 79.06. This region is seismically and ecologically very sensitive and delicate, even a minute changes (anthropogenic or natural) can create a dangerous disaster. A natural hazardous has been happened in Kedarnath valley due to torrential rainfall during 16 and 17 June 2013. After viewing this disaster due to torrential rainfall an attempt has been made to utilize the high resolution satellite data of before and after the incident of the recent devastation in Kedarnath of Rudrapratap District, Uttarakhand. The objective of this study is to fundamentally focus the intercession of human being in nature and their consequences in terms of human's life. In our article we tried to focus the impact of this natural hazardous over the region of Kedarnath. <#LINE#> @ @ Kimothi M.M. and Juyal N., Int. J. Remote Sensing, 17 (1996) @No $ @ @ V. Joshi V, Naithani, A.K and Negi, G.C.S, In GAIA, 16, (2001) @No $ @ @ Joshi V., Murthy T.V.R, Arya A.S., Narayana A., Naithani A.K. and Garg J.K., Jour. Nepal Geo. Soc., 28, (2003) @No $ @ @ Kimothi M.M. and Juyal N., Int. J. 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During the investigation period 232 fungal colonies were observed. The maximum fungal species belongs to Deuteromycotina (200 colonies) and Zygomycotina (11 colonies) and 21 colonies of unknown were observed. Culture media namely, Potato Dextrose Agar (PDA) Czapeks Dox Agar(CZA) and Sabouraud’s Dextrose Agar (SA) supplemented with 1% Streptomycin was used as nutrient media for the growth and sporulation of soil fungi. The Present investigation was conducted to find out the fungal diversity in eight different crop fields such as Sunflower, Sesame, Capsicum, Rice, Green gram, Sugarcane, Ground nut and Black gram. The colonies of Aspergillus and Penicillium were predominant in all soil samples of crop fields. Among the isolates, Aspergillus niger, Aspergillus flavus, Aspergillus fumigatus, Aspergillus nidulans, Aspergillus terreus, Penicillium chrysogenum, Penicillium frequentans, Penicillium Funiculosum, Alternaria alternata, Curvularia lunata, Trichoderma viride,Rhizopus stolonifer were authentically characteraized and the percentile contribution of these isolates was statically analyzed.<#LINE#> @ @ Olson R.K., Schoeneberger M.M., Aschmann S.G., An Ecological Foundation for Temperate Agroforestry, In: North America Agroforestry: An Integrated Science and Practice, Garrett H.E., W.J. Rietveld and R.F. 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(Ed.), Plenum, New York, Adv Microb Ecol 15, 27–79 (1997) @No $ @ @ Trevors J.T., Bacterial biodiversity in soil with an emphasis on chemically-contaminated soils, Water Air Soil Pollut 10145–67 (1998b) @No $ @ @ Wall D.H., Virginia R.A., Controls on soil biodiversity: insights from extreme environments, Appl. Soil Ecol, 13, 137–150 (1999) @No $ @ @ Ainsworth G.C., Bisby G.R., Dictionary of the fungi, Commonwealth Mycological Institute Kew, Surrey, 445 (1995) @No $ @ @ Warcup J.H., The ecology of soil fungi, Trans Br Mycol Soc, 34, 376-399 (1951) @No $ @ @ Christensen M.A., View of fungal ecology, Mycologia, 811-19 (1989) @No $ @ @ Arunachalam K., Arunachalam R.S. 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Ecol18 10, 2277-2281 (2007) @No $ @ @ Dong A.R., Lv G.Z., Wu Q.Y., Song R.Q., Song F.Q., Diversity of soil fungi in Liangshui natural reserve, Xiaoxing’anling forest region, J. Northeast Forestry University, 32), 8-10 (2004) @No $ @ @ Zhang C.B., Jin Z.X., Li J.M., Diversity of bacterial physiological groups and microbial flora in the soil of eight forest types of Tiantai Mountain, Zhejiang, Biodiversity Sci, ), 382-388 (2001) @No $ @ @ Jha D.K., Sharma G.D., Mishra R.R., Ecology of soil micoflora and mycorrhizal symbionts in degraded forests at two altitudes, Biol.Fert.Soils, 12, 272-278 (1992) @No $ @ @ Parrotta J.A., Productivity, nutrient cycling and succession in single- and mixed-species plantations of Casuarina equisetifolia,Eucalyptus robusta and Leucaena leucocephala in Puerto Rico, For. Ecol. Manage, 124), 45-77 (1999) @No $ @ @ Sall S.N., Masse D., Reversat F.B., Guisse A., Chotte J.L., Microbial activities during the early stage of laboratory decomposition of tropical leaf litters: the effect of interactions between the litter quality and exogenous inorganic nitrogen, Biol. Fert. Soils, 39), 103-111(2003) @No $ @ @ Hackl E., Bachmann G., Boltenstern-Zechmeister S., Soil microbial biomass and rhizosphere effects in natural forest stands, Phyton, 40,83-90 ( 2000)@No $ @ @ Christensen M., Species diversity and dominance in fungal communities. In:Wicklow DT, Carroll GC (eds), The Fungal Community: Its Organization and Role in the Ecosystem, Marcel Dekker Inc, New York, 201-232 1981 @No $ @ @ Lodge D.J., Factors related to diversity of decomposer fungi in tropical forests, Biodivers. Conserv, , 681-688 1997 @No $ @ @ Mahalingam R., Bharathidasan R., Ambikapathy Vand V., Panneerselvam A., An investigation of the soil mycoflora in sugarcane field of Dharmapuri District, Tamilnadu, Adv .Appl.Sci. Res, 3(3), 1255-1261 (2012) @No $ @ @ Prince L., Prabakaran P., Studies on the Soil Mycoflora from the Sugarcane field in Thanjavur District, Tamilnadu, J. Microbiol. Biotech. Res , ), 63-69 (2012) @No $ @ @ Gaddeyya G., Shiny NiharikaP., Bharathi P., Ratna Kumar P.K., Isolation and identification of soil mycoflora in different crop fields at Salur Mandal, Adv. Appl. Sci. Res,), 2020-2026 (2012) @No $ @ @ Behera B. C., Mishra R. R., Thatoi H. N., Diversity of soil fungi from mangroves of Mahanadi delta, Orissa, India,J. Microbiol. Biotech. Res., (),375-378 (2012) @No <#LINE#>Assessing the Susceptibility of Bacillus Subtilis to the Toxic effects of two lower Molecular Weight Phthalate Congeners in Pure Culture<#LINE#>Sandy Edward@Hinga,Jun@Yao,Qian@Yiguang,Ying@Song<#LINE#>45-52<#LINE#>9.ISCA-IRJEvS-2013-177.pdf<#LINE#>State Key Laboratory of Biogeology and Environmental Geology, China University of Geosciences, Wuhan 430074, CHINA @ School of Civil and Environmental Engineering, and National “International Cooperation Base on Environment and Energy”, University of Science and Technology Beijing, Beijing 100084, P.R. CHINA @ Chemistry Department, Fourah Bay College, University of Sierra Leone, Freetown, SIERRA LEONE<#LINE#>6/8/2013<#LINE#>11/8/2013<#LINE#>Microbial degradation of phthalate esters has been proffered as one the most effective processes of remediating environmental media polluted by these ubiquitous compounds in the environment. A number of previous studies have shown Bacillus subtilis among a host of other soil bacteria to metabolize phthalates, however, the reported toxicity of phthalates to microbial life especially at certain levels of pollution could be a deterrent to this process. The nature of interaction between a pollutant and a bacterium depends on both the chemical properties of the pollutant and the metabolic characteristics of the bacterium. This work seeks to investigate the susceptibility of B. subtilis as a model soil microbe to the toxic effects of two lower molecular weight phthalate congeners (Dimethyl phthalate, DMP and Diethyl phthalate, DEP) using a combination of methods that examine the metabolic heat response and morphological changes of the bacterial cells in different dose of the phthalates both aqueous media. Microcalorimetry assessment suggests the phthalates stimulated growth and metabolic activities of the bacteria at doses between 50-100g/mL but however produced inhibitory effects at higher doses. The half inhibitory dose index (ID50) obtained from the metabolic heat response shows that DMP is relatively more toxic to the bacterium than DEP which is attributed to the slightly higher solubility of DMP permitting its easier mobility across cell membrane. Scanning electron microscopic images of cells incubated at different doses of the phthalates show that both DMP and DEP impeded the bacterial growth and reproductive process especially at doses 200g/mL. Comparing these results to previous studies, lower molecular weight phthalates show relatively higher toxicity to B. subtilis than their higher molecular weight congeners. These evidences show that within certain low doses, phthalates can serve as carbon or energy sources to microbes by stimulating their metabolic activities but beyond certain limits, can exhibit their toxic effects by inhibiting microbial growth. <#LINE#> @ @ Cartwright C.D., Thompson I.P. and Burns R.G., Degradation and impact of phthalate plasticizers on soil microbial communities, Environ. Toxicol. Chem., 19, 1253-1261 (2000b) @No $ @ @ Shen O., Du G., Sun H., Wu W., Jiang Y., Song L. and Wang X., Comparison of in vitro hormone activities of selected phthalates using reporter gene assays, Toxicol. Lett.,191(1), 9-14 (2009) @No $ @ @ Vamsee-Krishna C. and Phale P. S., Bacterial degradation of phthalate isomers and their esters, Indian J. Microbiol., 48 (1), 19-34 (2008) @No $ @ @ Naseem A., Malik N., Firoj H., Singh A.K., Patel D.K., Khan A.R., and Masihur R., Heavy metal assessment of leachates of some plastic toys purchased from different districts of UP, India, Int. Res J.Environ. Sci.,1(4), 32-36 (2012) @No $ @ @ Vats S., Singh R.K., Tyagi P., Phthalates-A priority pollutant, Int. J. Adv. Biol. Res., 3(1), 1-8 (2013) @No $ @ @ Rael L.T., Bar-Or R., Ambruso D.R., Mains C.W., Slone D.S., Craun M.L. and Bar-Or D., Phthalate esters used as plasticizers in packed red blood cell storage bags may lead to progressive toxin exposure and the release of pro-inflammatory cytokines, Oxid. Med. Cell Longev., , 166–171 (2009) @No $ @ @ Hu X.Y., Wen B., Shan Q.X., Survey of phthalate pollution in arable soils in China, J. Environ. Monit., , 649-653 (2003) @No $ @ @ Bauer M.J. and Herrmann R., Estimation of the environmental contamination by phthalic acid esters leaching from house-hood wastes, Sci. Total Environ., 208, 49-57 (1997) @No $ @ @ Giam C.S., Atlas E., Powers M.A. and Leonard J.E., Phthalic acid esters. In: Hutzinger, O. (Ed.), The Handbook of Environmental Chemistry, Part C. Springer- Verlag, , 66–142 (1982) @No $ @ @ Schulz C.O., Assessing human health risks from exposure to di(2-ethylhexyl) phthalate (DEHP) and related phthalates: scientific issues, Drug Metab. Rev., 21, 111–120 (1989) @No $ @ @ Nielsen E. and Larsen P.B., Toxicological evaluation and limit values for DEHP and phthalates, other thanDEHP. Environ. Rev. Danish Environmental Protection Agency, Copenhagen, Denmark, (1996) @No $ @ @ Staples C.A., Peterson D.R., Parkerton T.F. and Adams W.J., The environmental fate of phthalate esters; a literature review, Chemosphere, 35, 667–749 (1997) @No $ @ @ Wu X., Wang Y., Liang R., Dai Q., Jin D., Chao W., Biodegradation of an endocrine-disruptingchemical di-n-butyl phthalate by newly isolated Agrobacterium sp. and the biochemical pathway. Process Biochem.,46, 1090-1094 (2011) @No $ @ @ Kleerebezem R., Hulshoff Pol L.W. and Lettinga G., Anaerobic Degradation of Phthalate Isomers by Methanogenic Consortia, Appl. Environ. Microbiol.,65, 1152–1160 (1999) @No $ @ @ Yuan S. Y., Liu C., Liao C. S. and Chang B. V., Occurrence and microbial degradation of phthalate esters in Taiwan river sediments, Chemosphere, 49, 1295-1299 (2002) @No $ @ @ Copley S.D., Evolution of efficient pathways for degradation of anthropogenic chemicals, Nat. Chem. Biol., , 559-566 (2009) @No $ @ @ Okamoto Y., Toda C., Ueda K., Hashizume K. and Kojima N. Transesterification in the microbial degradation of phthalate esters, J. Health Sci., 57(3), 293-299 (2011) @No $ @ @ Wu M.H., Lu N., Hu G., Ma J., Tang L., Wang L., Fu H.Y., Kinetics and mechanisms studies on dimethyl phthalate degradation in aqueous solutions by pulse radiolysis and electron beam radiolysis, Radiat. Phys.Chem., 80, 420-425 (2011) @No $ @ @ GroupE.F. Jr), Environmental fate and aquatic toxicology studies on phthalate esters, Environ. Health Perspect.65, 337–340 (1986) @No $ @ @ Liu Y., Guan Y., Yang Z., Cai Z., Mizuno T., Tsuno H., Zhu W. and Zhang X., Toxicity of seven phthalate esters to embryonic development of the abalone Haliotisdiversicolorsupertexta, Ecotoxicol.,18(3), 293-303 (2009) @No $ @ @ Jones A.E., Kahn R.H., Groves J.T. and Napier E.A. (Jr), Phthalate Ester Toxicity in Human Cell Cultures, Toxicol. Appl. Pharmacol., 31, 283-289 (1975) @No $ @ @ Lyche J.L., Gutleb A.C., Bergman A., Eriksen G.S., Murk A.J., Ropstad E., Saunders M. and Skaare J.U., Reproductive and developmental toxicity of phthalates. J. Toxicol. Environ. Health B Crit. Rev.,, 225-249 (2009) @No $ @ @ Navacharoen A., Vangnai A.S. Biodegradation of diethyl phthalate by an organic-solvent-tolerant Bacillus subtilisstrain 3C3 and effect of phthalate ester coexistence. Int. Biodeter. Biodegr., 65, 818-826 (2011) @No $ @ @ Patil N.K., Veeranagouda Y., Vijaykumar M.H., AnandNayak S. and Karegoudar T.B., Enhanced and potential degradation of o-phthalate by Bacillus sp. Immobilized in alginate and polyurethane, Int. Biodeter. Biodegr., 57, 82-87 (2006) @No $ @ @ Park J., KimM., Yoon J., Kobayashi F., Iwasaka Y., Hong C., Min J. and Kim Y., Biodegradation of diisodecyl phthalate (DIDP) by Bacillus sp. SB-007, J. Basic Microbiol., 49, S31-S35 (2009) @No $ @ @ Chen H., Yao J., Wang F., Choi M.M.F., Bramanti E. and Zaray G., Study on the toxic effects of diphenol compounds on soil microbial activity by a combination of methods, J. Hazard. Mater., 167, 846–851 (2009) @No $ @ @ Critter S.A.M., Freitas S. S. and Airoldi C.A., Calorimetry versus respirometry for the monitoring of microbial activity in a tropical soil, Appl. Soil Ecol., 18, 217–227 (2001) @No $ @ @ Backman P., Bastos M., Briggner L.E., Hägg S., Hallén D., Lönnbro P., Nilsson S.O., Olofsson G., Schön A., Suurkuusk J., Teixeira C. and Wadsö I., A system of microcalorimeters, Pure Appl. Chem., 66, 375–382 (1994) @No $ @ @ Prado A.G.S. and Airoldi C., Microcalorimetry of the degradation of the herbicide 2,4-D via the microbial population on a typical Brazilian red Latosol soil, Thermochim. Acta,371, 169–174 (2001) @No $ @ @ Critter S.A.M., Freitas S.S. and Airoldi C.A., Comparison between microorganism counting and calorimetric method applied to tropical soils, Thermochim. Acta, 394, 133–144 (2002) @No $ @ @ Sandy E.H., YaoJ., ZhengS., Gogra A.B., Chen H., Zheng H., YormahT.B.R., Zaray G., Ceccanti B. and Choi M.M.F., A comparative cytotoxicity study of isomeric alkylphthalates to metabolically variant bacteria, J. Hazard. Mater., 182 (1-3), 631-639(2010) @No $ @ @ Bais H.P., Fall R. and Vivanco J.M., Biocontrol of Bacillus subtilis against infection of Arabidopsis roots by Pseudomonas syringae is facilitated by biofilm formation and surfactin production, Plant Physiol., 34, 307-319 (2004) @No $ @ @ Gavala H.N., Alastriste-Mondrayon F., Iranpour R. and Ahing B.K., Biodegradation of phthalate esters during the mesophilic anaerobic digestion of sludge, Chemosphere, 4, 673-682 (2003) @No <#LINE#>Study of Uptake of Pb and Cd by Three Nutritionally Important Indian Vegetables Grown in Artificially Contaminated Soils of Mumbai, India<#LINE#>S.S.@Rangnekar,S.K.@Sahu,G.G.@Pandit,V.B.@Gaikwad<#LINE#>53-59<#LINE#>10.ISCA-IRJEvS-2013-181.pdf<#LINE#>Department of Environmental Studies, SIWS College, Wadala, Mumbai, MS, INDIA Environmental Assessment Division, Bhabha Atomic Research Centre (BARC), Trombay, Mumbai, MS, INDIA Board of Colleges and Teachers Development, Pune University, Pune, MS, INDIA<#LINE#>11/8/2013<#LINE#>22nd/8/2013<#LINE#>The ability of nutritionally important vegetable species as heavy metal accumulators was assessed. The root, stem and leaf content of the two metals lead and cadmium in the three plant varieties Spinach (Spinaciaoleracea), Fenugreek (Trigonellafoenum-graecum) and Red Amaranth (Amaranthuscruentus) was determined using pot experiments. Metal analysis was done using AAS. The metal concentration in different tissues varied according to plant part, type of metal, soil properties, morphological differences in plants, physiological differences in terms of heavy metal content, omission, increased uptake, foliarabsorption, etc. Highest metal concentration was reported in roots of all three plant varieties. Red Amaranth and Spinach showed higher tendency to accumulate lead and cadmium respectively. Among the two metals, Pb was accumulated more than Cd indicating plant affinity towards Pb. Transfer factor index also gave supporting values. None of the transfer factor exceeded 1 showing that none of the three species are hyperaccumulators. But they are certainly accumulating metals in its tissues. The root to shoot translocation factors concluded that metals are getting retained in roots and minimum levels are getting transferred in shoot parts. This indicates that roots which are insignificant for dietary intake of humans contain maximum quantities of heavy metal. Whereas the leaves that are nutritionally important for humans accumulate low levels of metals. Lead concentration in leaves of Red Amaranth and Spinach exceeded Indian standards. While lead concentration in Fenugreek and cadmium concentration in all the three vegetables was detected to be within the prescribed limits. This shows that elevated levels of Cd in soil may not add it significantly in human food chain but the same for Pb may raise its concentration in plants thereby increasing its toxicity. <#LINE#> @ @ Wong C.S.C., Li X.D., Zhang G., Qi S.H. and Peng X.Z., Atmospheric depositions of heavy metals in the Pearl River Delta, China. Atmos. Env., 37, 767–776 (2003) @No $ @ @ Khillare P.S., Balachandran S. and Meena B.R., Spatial and temporal variation of heavy metals in atmospheric aerosols of Delhi, Environmental Monitoring and Assessment, 90, 1–21 (2004) @No $ @ @ Lokeshappa B., Shivpuri K., Tripathi V. and Dikshit A. K., Assessment of Toxic Metals in Agricultural Produce, Food and Public Health, ), 24-29 (2012) @No $ @ @ Gratao P. L., Vara Prasad M. M., Cardoso P. F., Lea P. J., and Azevedo R. A., Phytoremediation: Green technology for the clean-up of toxic metals in the environment, Brazilian Journal of plant physiology, 17), 53 – 64, 2005) @No $ @ @ Chaney R.L., Malik M., Li Y.M., Brown S.L., Brewer E.P., Angle J.S. and Baker, A.J.M., Phytoremediation of soil metals, Environ. 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A, Lalmatia, Dhaka-1207, BANGLADESH<#LINE#>13/8/2013<#LINE#>21/8/2013<#LINE#>This article provides a long run perspective of climate change impacts mainly due to CO emission and subsequent rise of temperature on food security in Bangladesh. The trends of changes in food demand and production was estimated considering five different climatic scenarios (A, B, C, D and E) based on Intergovernmental Panel on Climate Change (IPCC). These scenarios were accounted from the base year of 2008 to 2050, 2070 and 2100. Based on these scenarios the probable yield of winter rice variety BR3 was estimated for the year 2050, 2070 and 2100 using Decision Support System for Agrotechnology Transfer (DSSAT) model. The outcome of DSSAT model reveals that if the present trend of the population expansion and economic development continues, the future food security situation would be aggravated by the end of this century. Besides, the study suggests that the condition of future food security would be more vulnerable under the five climatic changes scenarios. It was estimated that the shortage of rice might be 58 million tons, 55 million tons and 48 million tons for scenarios C, D and E respectively which might lead to the expansion of food seeking (attributed to rice) community up to 45.90%, 43.85% and 38.25% by the year 2100. Furthermore, study suggests some policy recommendations to meet the challenges of future food security under climatic variability considering the gap between demand and supply. <#LINE#> @ @ IPCC, Synthesis Report, Contribution of Working Groups I, II and III to the Fourth Assessment Report of IPCC. Intergovernmental Panel on Climate Change, Cambridge University Press, Cambridge, UK (2007) @No $ @ @ Basak J.K., Rahman M.M., Das R., Rahman T. and Ali M.A., Assessment of changes in temperature and precipitation patterns in Bangladesh. 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Manag.,34(4), 487-498 (2004) @No <#LINE#>Study of Physio-Chemical properties and microbial analysis of lakes in and around Coimbatore, Tamil Nadu, India<#LINE#>A.@Manivannan,M.@Jerald,Chandaran@Rashmi,R.T.@Narendhirakannan<#LINE#>68-71<#LINE#>12.ISCA-IRJEvS-2013-186.pdf<#LINE#>*Department of Biotechnology, School of Biotechnology and Health Sciences, Karunya University, Karunya Nagar, Coimbatore – 641 114, Tamil Nadu, INDIA @ Founder and Chair person, National Health and Environmental Research, Coimbatore Tamil Nadu, INDIA<#LINE#>15/8/2013<#LINE#>31/8/2013<#LINE#>This study was aimed to screen the water quality of five lakes (Ranganathapuram Lake, Chinthamani Lake, Vedapatti Lake, Pannimadai Lake, Vallan Lake) in and around Coimbatore city, Tamil Nadu, India. The study was conducted based on their water source, phytoplankton community and origin of pollution such as utilisation by human and animals. In this study the odour, colour, pH, alkalinity, BOD and COD of water samples from five lakes along with the inorganic and organic contents viz chloride, iron, calcium, sulphite, arsenic and alkalinity was analysed. Further, pathogens such as Klebisella sp., Streptococcus sp., Shigella sp., Salmonella sp., Vibrio sp., Citrobacter sp., Enterobacter sp., and Pseudomonas sp. which are water borne pathogens were isolated. The results of this study reveal the status of wetlands quality it may helpful to protect the water resources and create awareness about the water pollution among the people living around the lakes. <#LINE#> @ @ Jin X.C., Liu H.L., Tu Q.Y., Zhang Z.S. and Zhu X.A., Eutrophication of lakes in China, Chinese Res. Acad. of Environ. Sci.,36 (1), 291-297 (1990) @No $ @ @ Gray A.V. and Wang L.i., Case study on water quality modelling of Dianchi lake South west China, Water sci. 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Freshwater Biological Association. Titus Wilson & Sons, Amblesie. 121p. (Scientific Publication n, 36). (1978) @No $ @ @ Tasneem Gul Kazi, Muhammad Balal Arain, Jameel Ahmed Baig, Muhammad Khan Jamali, Hassan Imran Afridi, Nusrat Jalbani, Raja Adil Sarfraz, Abdul Qadir Sha and Abdul Niaz., The correlation of arsenic levels in drinking water with the biological samples of skin disorders, Sci. of the Total Environ.,407(3), 1019-1026 (2009) @No $ @ @ Skoulikidis N.T., Bertahas I., and Koussouris T., The environmental state of freshwater resources in Greece (rivers and lakes), Environ. Geo., 36, 1–2 (1998) @No $ @ @ Chandra R, Nishadh K.A. and Azeez P.A., Monitoring water quality of Coimbatore wetlands, Tamil Nadu, India. Environ. Monit. Assess.,64, 1007-1066 (2009) @No $ @ @ Sunkad B.N. and Patel H.S., Water quality assessment of Fort lake of Belgaum (Karnataka) with special reference to zooplankton, J. Environ. Biol., 25, 99–102 (2004) @No $ @ @ Health Canada one of the nine most common food products causing severe adverse reactions (1996) @No $ @ @ World Health Organization Guidelines for drinking-water quality third ed recommendations. Geneva:World Health Organization (2004) @No $ @ @ Tu C. and Ma L.Q., Effects of Arsenic concentration and forms on Arsenic uptake by Water Hyacinth, J. Environ. Qual.31, 641-647 (2002) @No <#LINE#>Assessing the prospective of Jatropha curcas in Reclamation of Sodic Soil<#LINE#>Anamika@Srivastava<#LINE#>72-75<#LINE#>13.ISCA-IRJEvS-2013-189.pdf<#LINE#> Babu Banarsi Das University, Faizabad Road, Lucknow, UP, INDIA<#LINE#>24/8/2013<#LINE#>7/9/2013<#LINE#>Uttar Pradesh, India has more than 1.2 million hectares of salt affected soil. Out of which mostly are sodic soil. Gypsum, a chemical amendment for sodic soil is widely used for reclamation. This paper discusses application of Jatropha curcas for reclamation of sodic soil. Without applying any chemical amendment, Jatropha was planted on soil having an exchangeable sodium percentage (ESP) of 51 and pH 11.9. The result indicates that plantation of Jatropha reduces ESP, pH and Na significantly and increases soil organic carbon and exchangeable Ca. It could deduce that Jatropha mainly works upon the principle of increased CO partial pressure existing. The interaction of roots and micros, the respiration probably amplifies the solubility of calcites and improves soil physical properties because of the vertical growth of taproot. It is concluded that Jatropha is efficient for sodic soil reclamation but takes a longer duration, because plant requires time for stabilization. Presently, at partial reclamation, other crops can be planted along with Jatropha to diversify the waste land use. <#LINE#> @ @ Velayutham V., Status of land resources in India. 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International conference on Sustainable management of land, Feb. 9-14, 15-21 (2005) @No $ @ @ Afridi M.M.R.K., Afaq W., Samiullah S.H. and Parvaiz M.A., Effect of nitrogen, phosphorous and potasssium on the growth and yield of fennel (Foeniculum vulgare Mill), Agric. Sci.Prog., , 63-73 (1983) @No $ @ @ Qadir A., Potassium and sodium contents of shoot and laminae of rice cultivars and their sodicity tolerance, J. Plant Nutr, 18, 2281-2290 (1995) @No $ @ @ Garg V.K. and Srivastava S.C., Varietal differences in sugarbeet yield and quality due to soil exchangeable sodium, J. Ind. Soc. Soil Sci., 34, 572-576 (1986) @No $ @ @ Singh S.B. and Singh M.V., Effect of exchangeable sodium on growth, yield and mineral composition of Barley varieties, J. Ind. Soc. Soil Sci.,38, 135-138 (1990) @No $ @ @ Bhatnagar C.P. and Yadav J.S.P., Effects of varying levels of alkali on growth and nutrient uptake of barley, Agrochem. Talat., 29, 447-455 (1980) @No <#LINE#>Emphasizing the Quality of Some Selected Ground Water Samples of Kanyakumari District, India Using Quality Index Assessment<#LINE#>N.K.@Amaliya,P.Kumar@Sugirtha<#LINE#>76-82<#LINE#>14.ISCA-IRJEvS-2013-200.pdf<#LINE#> Chemistry Research Centre, Women’s Christian College, Nagercoil–629001, INDIA<#LINE#>10/9/2013<#LINE#>17/9/2013<#LINE#>The Quality Index assessment method is used to monitor the pollution status of water samples by integrating the water quality variables. The aim of this work is to monitor the pollution level of ground water samples from different places of kanyakumari district. For calculating the Quality Index the following18 water quality variables such as EC, TDS, DO, TH,pH, alkalinity, calcium, sodium, magnesium, sulphate, phosphate, potassium, chloride, fluoride, manganese and nitrate have been considered. The different ground water samples of Kanyakumari district have quality index values ranging from 8.45 to 162.3. In this present work the status of water quality is found to be good for consumption and other purposes except Kalkulam bore well water sample. <#LINE#> @ @ Yadav Janeshwar, Pathak R.K. and Khan Eliyas., Analysis of Water Quality Using Physico-Chemical Parameters, Satak Reservoir in Khargone District, Madhya Pradesh, India, Int. Res. J. Environment Sci.,2(1), 9-11 (2013) @No $ @ @ Mushini Venkata Subba Rao, Vaddi Dhilleswara Rao and Bethapudi Samuel Anand Andrews., Assessment of Quality of Drinking Water at Srikurmam in Srikakulam District, Andhra Pradesh, India, I. Res. J. Environment Sci.,1(2), 13-20 (2012) @No $ @ @ Mangukiya Rupal, Bhattacharya Tanushree and Chakraborty Sukalyan.,Quality Characterization of Groundwater using Water Quality Index in Surat city, Gujarat, India, I. Res. J. Environment Sci.,1(4), 14-23 (2012) @No $ @ @ Yogendra K. and E.T. 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Conf. on water pollution research, Jerusalem., (6), 787-797(1972) @No @Short Communication <#LINE#>Studies on Isolation and Identification of Active Microorganisms during Degradation of Polyethylene / Starch Film<#LINE#>Prabhat@Sharma,S.@Bhattacharyya,Vishal@Verma,R.K.@Kalyan,Vijai@Kumar,K.N.@Pandey,M.@Singh<#LINE#>83-85<#LINE#>15.ISCA-IRJEvS-2013-062.pdf<#LINE#>Central Institute of Plastics Engineering and Technology, Lucknow, INDIA @ Department of Microbiology, KGMU, Lucknow, INDIA<#LINE#>14/3/2013<#LINE#>17/5/2013<#LINE#>Low density polyethylene is a vital cause of environmental pollution. It occurs by choking sewer line through mishandling thus posing an everlasting ecological threat. Biodegradable plastics are eco-friendly; they accumulate great potential applications in various industries. Biodegradable polymers degrade upon disposal by the action of active microorganisms in the soil. The result of degradation can be interpreted with physical changes through biological force. Microbial degradation of plastics convert polymer into oligomers and monomers. This microbial degradation may be based on aerobic and anaerobic metabolisms. The main objective of present study is to isolate and identify the microorganisms from soil during biodegradation testing of polyethylene/starch film. The isolation is been carried out through soil serial dilution method. An isolated microorganism is cultivated in culture media. After growth of microorganisms at 37 C identification of microorganisms was carried out by macroscopic/microscopic examination. During identification it is found that bacteria (Pseudomonas spp, Streptococcus spp, Staphylococcus spp, Micrococcus spp and Moraxella spp etc), fungi (Aspergillus niger, Aspergillus glaucus etc), and Actinomycetes are present on the surface of polyethylene/starch film. Surface morphology of polyethylene/starch film has been analyzed by scanning electron microscopy (SEM) before and after degradation. 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