ENVIROMENTAL POLLUTION

Slides:



Advertisements
Similar presentations
Advanced Sampling and Data Analysis for Source Attribution of Ambient Particulate Arsenic and Other Air Toxics Metals in St. Louis Missouri Department.
Advertisements

Concentartion of metals in the rivers of south part of Primorie, Russia. V. M. Shulkin, N. N. Bogdanova Pacific Geographical Institute RAS, Vladivostok.
WATER DEPTH, VEGETATION, AND POLLUTANT REMOVAL IN A CONSTRUCTED WETLAND TREATING AQUACULTURE EFFLUENT Brian E. Dyson, Kim D. Jones, Ron Rosati* Department.
GEO-ELECTRIC INVESTIGATION OF UNDERGROUND LEACHATE DISTRIBUTION AT A CLOSED LANDFILL IN SOUTHWESTERN ONTARIO, CANADA Joshi, Siddharth 1, Yang, Jianwen.
The percentage of particles in various size ranges is determined and data can be displayed as a particle size distribution, or cumulative size distribution.
Magnetic Field Characteristics of a Magneto-Biosensor Detection coil. John Eveness 1, Janice Kiely 2, Peter Hawkins 1, Richard Luxton 1. 1 Faculty of Applied.
Information from stream sediments Measurement of concentration of metals present (as solids) in sediment Gives information on: 1.Background levels of contamination.
PETROLEUM GEOSCIENCE PROGRAM Offered by GEOPHYSICS GEOPHYSICS DEPARTMENT IN COROPORATION WITH GEOLOGY, PHYSICS, CHEMISTRY, AND MATHEMATICS DEPARTMENTS.
Integrated Approach for Assessing the Characteristic of Groundwater Recharge in Basin Scale Hsin-Fu Yeh*, Cheng-Haw Lee, Kuo-Chin Hsu Department of Resources.
Heavy metals (Pb, Cd and Zn) levels in roadside soils in Nairobi County.
NORMALISATION METHOD FOR EVALUATION OF METAL CONTAMINATION OF SOIL József PROKISCH, Ildikó SZEGVÁRI, Éva SZÉLES, Béla KOVÁCS, Zoltán GYŐRI University of.
An Analysis of the Pollutant Loads and Hydrological Condition for Water Quality Improvement for the Weihe River For implementing water resources management.
Empirical Understanding of Traffic Data Influencing Roadway PM 2.5 Emission Estimate Roadway PM 2.5 Emission Estimate Investigators: Justin Cox, Zachary.
Conclusions Geophysical Methods for Road Construction and Maintenance Hedi Rasul 1&2, Caroline Karlsson 1, Imran A. Jamali 1, Robert Earon 1, Bo Olofsson.
Cosmogenic Dating.  A group of isotopic methods of age determination based on accumulation of certain nuclides, which are produced only in the top few.
” Particulates „ Characterisation of Exhaust Particulate Emissions from Road Vehicles Key Action KA2:Sustainable Mobility and Intermodality Task 2.2:Infrastructures.
Mineral Exploration Tel: (07) Fax: (07)
Results from the SMEAR III urban measurement station
Chapter 15 Environmental Health, Pollution and Toxicology.
Bernd Heits AQ-Workshop Bucharest, July 2008 Planning of ambient air quality measurements General rules The guideline is an application aid to.
Elemental composition of Tibetan Plateau top soils and its effect on evaluating atmospheric pollution transport Chaoliu Li, Shichang Kang, Qianggong Zhang,
SUBMICRON AEROSOL PARTICLES IN A SMALL SETTLEMENT NEAR HIGHWAY J. HOVORKA, Z. STAŇKOVÁ Institute for Environmental.
Part A. Nitrogen dioxide, as measured by monitoring stations Additional file 1. Histograms of the distributions of air pollution indicators Number of subjects.
WATER QUALITY MONITORING: THE PANHAMNDLE W.R.L. MASAMBA, HOORC, P/Bag 285, Maun Presented at the Water Workshop, Xakanaka DWA Camp, 20 Nov
PARTICLE EMISSIONS FROM TYRE AND BRAKE WEAR OPEN QUESTIONS Sustainable Transport Unit Institute for Energy and Transport Joint Research Centre 8 January.
Sediments Toxicity of the rivers draining Ibadan Metropolis Southwestern, Nigeria. 1 Ajibade, O.M and 2 Abimbola, A.F. 1 Department of Earth Sciences,
An air quality information system for cities with complex terrain based on high resolution NWP Viel Ødegaard, r&d department.
August 1999PM Data Analysis Workbook: Characterizing PM23 Spatial Patterns Urban spatial patterns: explore PM concentrations in urban settings. Urban/Rural.
Intelligent Traffic Environmental System (ITES-AIR)
OUTLINE Introduction Background information HypothesisMethodsResultsDiscussionConclusion.
Jericho Project Air Quality Assessment. TOPICS METHODOLOGY EMISSION SOURCES RESULTS AND ASSESSMENT MITIGATION AND MONITORING CONCLUSION.
Introduction The ongoing development in the third world countries has led to understanding the repercussions of environmental hazards that are prevailing.
Gennaro Cioffi. Field evidence for rapid downstream fining of river gravels through selective transport Ferguson, R.I, Hoey, T., Wathen, S. and Werrity,
PM Methods Update and Network Design Presentation for WESTAR San Diego, CA September 2005 Peter Tsirigotis Director Emissions, Monitoring, and Analysis.
Continuous wavelet transform of function f(t) at time relative to wavelet kernel at frequency scale f: "Multiscale reconstruction of shallow marine sediments.
Bartłomiej Pietras Institute of Geography; Pedagogical University,ul. Podchorążych 2, Kraków; Introduction The problem of air.
Materials: LI-COR LAI-2200 Plant Canopy Analyzer FV2200 software Excel Rstudio Methods and Study Site: LAI measurements using an indirect, optical method.
Branka Bračič Železnik 1, Barbara Čenčur Curk 2 THE INFLUENCE OF CLIMATE VARIATIONS ON NATURAL BACKGROUND OF NITRATE IN PERCOLATED WATER 1 Public Water.
WLTP-DHC Analysis of in-use driving behaviour data, influence of different parameters By Heinz Steven
Exposure to air pollution in the transport microenvironment: how important is short-term exposure to high concentrations, and what are the determinants.
Earthquake Site Characterization in Metropolitan Vancouver Frederick Jackson Supervisor – Dr. Sheri Molnar.
N Engl J Med Jun 29;376(26): doi: 10
FISHERIES POSTER SESSION
SMOKE-MOVES Processing
Role of Plants in Mitigation of Environmental Impact During Construction Phase of Building Projects: A Case Study of Curaj Campus. Binita Kumari1, K.C.Sharma2.
REPLAC THIS BOX WITH YOUR ORGANIZATION’S
PIXE measurements of heavy metals of Tsunami sediment samples
Air quality and potential health hazards of radioactive materials and heavy metals associated with contaminated dusts in Amman, Jordan. By: Hadeel Al Dwaikat.
EXPOSURE OF CHILDREN TO ULTRAFINE PARTICLES AROUND AN URBAN INTERSECTION S Kaur, M J Nieuwenhuijsen & R Colvile Environmental Processes & Systems Research.
Introduction to Scientific Method
Carbon Cycling in Perennial Biofuel Management Systems
Trakya University Department of Biology EDIRNE TURKEY
HEAVY METAL SOLUBILITY AND MOBILITY IN HUMUS LAYERS IMPACTED BY COPPER INDUSTRY IN SOUTH - WEST POLAND Agnieszka Medyńska-Juraszek, Cezary Kabała Institute.
Exposure to Air Pollution James Tate and Paul Seakins
5. WEIGHT VOLUME RELATIONSHIPS
Atmospheric Corrosion
E.V. Lukina, K.W. Freeman,K.J. Wynn, W.E. Thomason, G.V. Johnson,
Representative Measurements – AQ-Workshop Bucharest, July 2008
Imaging Structural Proteins
in US East Coast Using SMAT-CE Software
Pollution from Diesel Generators – Gurugram
Impact of Land use on Air pollution in Austin
Models of the Earth Earth Science Chapter 3.
EMEP Case study: Assessment of HM pollution levels with fine spatial resolution in Belarus, Poland and UK Ilia Ilyin, Olga Rozovskaya, Oleg Travnikov.
EMEP case studies on HMs: State of the art
Contributions to total changes in emissions of ozone precursors
HIGHWAY DESIGN PROCESS & ROUTE LOCATION
Comparison of ozone profiles from Broadmeadows and Macquarie Island,
Soil organic carbon (SOC) can significantly influence key soil functional properties and improve soil quality by increasing water holding capacity, reducing.
WORK OF THE UNITED KINGDOM AIR QUALITY EXPERT GROUP (AQEG)
Presentation transcript:

ENVIROMENTAL POLLUTION THE MAGNETIC SUSCEPTIBILITY (MS) MAPPING OF ROAD DUST FROM KOLKATA CITY TO INFER THE DEGREE OF ENVIROMENTAL POLLUTION Rimjhim Maity, Punyotoya Paul, Debesh Gain, Supriya Mondal, Shashwat Kumar Singh Department of Geological Sciences, Jadavpur University, Kolkata 700 032, India *Presenting Author: rimjhimmaity@gmail.com Abstract pollution mapping (2D and 3D on the basis of magnetic susceptibility using MS2B. to infer the degree of environmental pollution on the basis of frequency dependent susceptibility values for some specific areas. Pollution of road dusts is significantly reducing environmental quality. The pollutants of most concern are heavy metals and organic contaminants. Road sides in metropolitan cities like Kolkata are commonly polluted by particulate matter derived mostly from emission of traffic: motor vehicles, abrasion of tiers, brake linings, dispersion of construction material, etc. The magnetic proxies can be used as indicator for environmental pollution. The aims of our study are to trace the distribution and concentration of contaminants in road dust along major roads and highways of Kolkata city carrying appreciable traffic by using magnetic parameters. The frequency dependent susceptibility measurements are used to detect the presence of ultrafine (<0.03μm) superparamagnetic ferri-magnetic minerals and are roughly inferred the degree of pollution on the basis of the fact ‘The higher the MS, the lower the FDS (Frequency Dependent Susceptibility), the more seriously the Road dust may be polluted’. Clearly enhanced values of the MS, varies from 100 to 150 x10-8 SI, were found on the roadsides which are about 10 times greater than the areas which are not influenced by traffic emissions (about 20–30 x10-8 SI). The distribution of the susceptibility values of all sites represent polluted areas strongly influenced by traffic frequency, constructional hazards, meteorological conditions and other factors. Results Magnetic Susceptibility Data A single profile was measured in order to qualitatively determine the degree of magnetic pollution along a road with high traffic frequency. The highest susceptibility value is 155.783 x 10-8 m3/kg for (L-21) and the lowest value is 9.19 x 10-8 m3 /kg for (L-44). MAPPING The whole mapping is carried out between the latitude 22.502⁰N-22.604⁰N and longitude 88.302⁰E-88.444⁰E.In order to highlight the trend of susceptibility vs. Position of road junctions, all 50 profiles measured for the high resolution mapping are plotted in Map:4.1 and Map:4.2. And Map:4.3 shows 3D mapping of original data shows high and low peaks. GRAPH BETWEEN Xfd AND %Xfd The graph shows the trend of %Xfd values with respect to Xfd value which is generally showing no specific trend. But, it is clear that the places of high susceptibility values having low %Xfd value than the places of low susceptibility values. Another part is that the maximum %Xfd value is 3.01 means that the all samples have very low concentration of superparamagnetic minerals(<10%). Fig. 3: 3D susceptibility mapping shows high and low peak. Fig.4: Graph shows the trend of %Xfd values with respect to Xfd values. Discussion The highest MS value is measured from L-21 and lowest value from L-44. The data analysis to detect the degree of pollution, we selected some major areas having high and low MS values and carried out susceptibility measurements for dual frequency susceptibility. All data includes that dust of low susceptibility like L-44, have FDS values are >1.5% but high susceptibility area like L-21 have FDS value<1.5%.It can be deduced that if pollutants are present in dust, its MS will increase and FDS will drop. We can also infer that, taking earlier references, maximum studied areas having FDS value<3% means the concentration of super paramagnetic grains are very less(<10%) which indicates that the dust samples having high susceptibility are because of pollutants present in them. Introduction Pollution studies aim to identify areas of high pollution levels and method to reduce daily exposure to these harmful particles. However, many techniques currently in use are time-consuming, expensive and therefore spatially limited than magnetic techniques. So, magnetic susceptibility as a proxy for pollutant loading. Kolkata, a city in the eastern part of India, is one of the most polluted metropolises city of India. This study is carried out to assess the roadside dust at 50 major roads and crossings. The magnetic susceptibility is used as a magnetic proxy for the susceptibility mapping to infer the environment pollution.. Conclusions Methods and Material Fig. 1: Histogram showing Mass Susceptibility values of all locations. Areas which are not affected by anthropogenic input are characterized by low and stable susceptibility values. A magnetite-like phase was found to be responsible for the enhancement of the magnetic susceptibility of the road dust. Summarizing the susceptibility results, dust samples in the investigated road sides are clearly influenced by anthropogenic emissions up to a distance of 5 m from the road and down to a depth of half a meter. The most striking result of this investigation is that our data demonstrate the potential of magnetic susceptibility mapping for the study of environmental pollution. Our results show that the pollutants in road dust have different magnetic properties from the sediments and the unpolluted soils. We can conclude that, the study of magnetic susceptibility and frequency-dependent susceptibility can serve as a convenient and effective method for the detection of environmental pollution. The field work concerns the main roads and crossings of metro city Kolkata. Area covers approximately 185km2 with 5.2 million residents and dust samples are collected during spring season, from areas which have high traffic circulation for magnetic studies. Samples were collected from the road crossings. In the laboratory, samples were dried at room temperature and the samples from each site were put into 6 standard identical plastic cubical boxes which are pre weighted (8 cm3) for magnetic analysis. Then, all the samples were subjected to measure under low frequency using Bartington Susceptibility Meter (MS2B) put into the dual frequency (0.48 and 4.8 kHz) for susceptibility (k) measurements in CGS unit. This study mainly consists of following objectives: tracing the distributions and concentrations of magnetic contaminations along major roads and highways of Metro city Kolkata. Fig. 2: Contour map showing detailed susceptibility results for all sampling sites. Contact References Rimjhim Maity Department of Geological Sciences, Jadavpur University, Kolkata. Email: chatterjeesaurodeep@gmail.com Phone: +918902792746 1.Dearing, J., 1994. Environmental magnetic susceptibility. Bartington Instruments, Witney, Oxon, England, 104 pp. 2.Strzyszcz, Z., 1993. Magnetic susceptibility of soils in the areas influenced by industrial emissions. Soil Monitoring, Monte Verita. Birkha¨user, Basel, pp. 255–269. 3.Versteeg, J.K., Morris, W.A., Rukavina, N.A., 1995. The utility of magnetic properties as a proxy for mapping contamination in Hamilton Harbour sediment. J. Great Lakes Res. 21, 71–83. 4.Versteeg, J.K., Morris, W.A., Rukavina, N.A., 1996. Distribution of contaminated sediment in Hamilton Harbour as mapped by magnetic susceptibility. Geoscience Canada 22 (4), 145–151.