This document discusses remediation of oil contaminated sites. It begins by outlining various sources of land and water contamination including oil spills, industrial activities, and agriculture. The effects of oil contamination include environmental damage, health impacts, and agricultural effects. The document then examines several remediation techniques including physicochemical methods like soil washing, soil vapor extraction and solidification/stabilization. Thermal methods such as thermal desorption and incineration and biological techniques including bioremediation, land farming and phytoremediation are also discussed. Key factors to consider when selecting a remediation method include site characteristics, soil properties, and contaminant type and concentration. In conclusion, the document emphasizes the importance of preventing sp
This document discusses in situ soil vapor extraction (SVE) for remediating volatile organic compounds (VOCs) in the vadose zone. SVE works by placing extraction wells around contaminated soil to induce airflow and evaporate VOCs from the soil into the wells. Key factors that influence SVE's effectiveness include soil properties like permeability, porosity, and moisture content. The document also introduces in situ air sparging, which injects air below the water table to strip and transport contaminants upward for collection by SVE. Both techniques are cost-effective for treating VOCs but require consideration of soil characteristics and monitoring to prevent contaminant migration.
The document summarizes a seminar presentation on fly ash utilization and disposal. Fly ash is a byproduct of coal combustion in power plants. It can be utilized in construction materials like concrete and bricks to replace resources like cement, clay, and sand. It can also be used to reclaim land or stabilize soil. However, much of the fly ash currently produced worldwide is disposed of in landfills or ash ponds, which can pollute air, water, and soil if not properly managed. The presentation discusses the composition, types, production, uses, disposal methods, and environmental impacts of fly ash.
This document discusses modern methods for recovering metals from effluents, specifically ion exchange chromatography and electrodialysis. Ion exchange chromatography separates ions and polar molecules using an ion exchange resin that retains analytes based on their charge. Electrodialysis uses an applied electric potential to transport ions through ion exchange membranes from a dilute solution to a concentrated brine solution. Both methods are effective at separating and recovering metal ions from industrial wastewater effluents.
This document outlines a pre-thesis presentation on using a sequential batch reactor (SBR) to treat dairy wastewater. It includes an introduction to SBR technology, the objectives of studying this wastewater treatment method, a proposed methodology, and a work plan. The presentation covers dairy wastewater characteristics, the phases of SBR treatment, operational parameters, expected efficiency improvements over activated sludge processes, advantages and limitations of SBR, and conclusions from the literature review.
This document discusses methods for treating landfill leachate. Leachate is produced as water percolates through waste in a landfill. It contains high levels of organic and inorganic contaminants. The main goals of leachate treatment are to reduce environmental impacts and meet regulatory discharge standards. Common treatment methods include biological processes like aerobic and anaerobic treatment, as well as physical/chemical processes such as coagulation, flocculation, adsorption, and membrane filtration. Often, a combination of treatment methods is needed to sufficiently reduce contaminants in leachate before discharge or reuse.
The document discusses various aspects of anaerobic wastewater treatment processes. It provides information on the types and characteristics of anaerobic reactors including UASB and EGSB reactors. It also describes the formation of anaerobic granular sludge, which allows high biomass retention and efficient COD removal. Additionally, it compares the kinetics, environmental factors, and advantages of anaerobic versus aerobic wastewater treatment processes.
The document discusses advanced oxidation processes (AOPs) which use hydroxyl radicals to oxidize organic compounds that cannot be degraded through biological or conventional water treatment processes. It describes various AOP technologies that generate hydroxyl radicals including ozone/UV, hydrogen peroxide/UV, Fenton reactions, photocatalysis, and ultrasound-assisted processes. Factors that influence AOP performance such as pH, presence of carbonates or natural organic matter are also summarized.
Activated Sludge Process and biological Wastewater treatment systemKalpesh Dankhara
The document discusses biological wastewater treatment, specifically for removing biochemical oxygen demand (BOD) and nitrogen. It covers the types of pollutants found in wastewater, biological treatment methods, microorganisms involved, and the activated sludge process. Key aspects of the activated sludge process discussed include aeration basins, clarifiers, mixed liquor suspended solids, food to mass ratio, recycle and waste sludge streams, and sludge retention time.
This document discusses in situ soil vapor extraction (SVE) for remediating volatile organic compounds (VOCs) in the vadose zone. SVE works by placing extraction wells around contaminated soil to induce airflow and evaporate VOCs from the soil into the wells. Key factors that influence SVE's effectiveness include soil properties like permeability, porosity, and moisture content. The document also introduces in situ air sparging, which injects air below the water table to strip and transport contaminants upward for collection by SVE. Both techniques are cost-effective for treating VOCs but require consideration of soil characteristics and monitoring to prevent contaminant migration.
The document summarizes a seminar presentation on fly ash utilization and disposal. Fly ash is a byproduct of coal combustion in power plants. It can be utilized in construction materials like concrete and bricks to replace resources like cement, clay, and sand. It can also be used to reclaim land or stabilize soil. However, much of the fly ash currently produced worldwide is disposed of in landfills or ash ponds, which can pollute air, water, and soil if not properly managed. The presentation discusses the composition, types, production, uses, disposal methods, and environmental impacts of fly ash.
This document discusses modern methods for recovering metals from effluents, specifically ion exchange chromatography and electrodialysis. Ion exchange chromatography separates ions and polar molecules using an ion exchange resin that retains analytes based on their charge. Electrodialysis uses an applied electric potential to transport ions through ion exchange membranes from a dilute solution to a concentrated brine solution. Both methods are effective at separating and recovering metal ions from industrial wastewater effluents.
This document outlines a pre-thesis presentation on using a sequential batch reactor (SBR) to treat dairy wastewater. It includes an introduction to SBR technology, the objectives of studying this wastewater treatment method, a proposed methodology, and a work plan. The presentation covers dairy wastewater characteristics, the phases of SBR treatment, operational parameters, expected efficiency improvements over activated sludge processes, advantages and limitations of SBR, and conclusions from the literature review.
This document discusses methods for treating landfill leachate. Leachate is produced as water percolates through waste in a landfill. It contains high levels of organic and inorganic contaminants. The main goals of leachate treatment are to reduce environmental impacts and meet regulatory discharge standards. Common treatment methods include biological processes like aerobic and anaerobic treatment, as well as physical/chemical processes such as coagulation, flocculation, adsorption, and membrane filtration. Often, a combination of treatment methods is needed to sufficiently reduce contaminants in leachate before discharge or reuse.
The document discusses various aspects of anaerobic wastewater treatment processes. It provides information on the types and characteristics of anaerobic reactors including UASB and EGSB reactors. It also describes the formation of anaerobic granular sludge, which allows high biomass retention and efficient COD removal. Additionally, it compares the kinetics, environmental factors, and advantages of anaerobic versus aerobic wastewater treatment processes.
The document discusses advanced oxidation processes (AOPs) which use hydroxyl radicals to oxidize organic compounds that cannot be degraded through biological or conventional water treatment processes. It describes various AOP technologies that generate hydroxyl radicals including ozone/UV, hydrogen peroxide/UV, Fenton reactions, photocatalysis, and ultrasound-assisted processes. Factors that influence AOP performance such as pH, presence of carbonates or natural organic matter are also summarized.
Activated Sludge Process and biological Wastewater treatment systemKalpesh Dankhara
The document discusses biological wastewater treatment, specifically for removing biochemical oxygen demand (BOD) and nitrogen. It covers the types of pollutants found in wastewater, biological treatment methods, microorganisms involved, and the activated sludge process. Key aspects of the activated sludge process discussed include aeration basins, clarifiers, mixed liquor suspended solids, food to mass ratio, recycle and waste sludge streams, and sludge retention time.
The document discusses environmental impact assessment (EIA) and its integration with environmental management systems (EMS). It provides background on EIA, including its origins in the National Environmental Policy Act of 1969, the tiered approach to assessments, and methods used in EIA like impact prediction and evaluation of alternatives. EIA aims to anticipate impacts of new projects at the planning stage, while EMS helps manage ongoing environmental impacts during construction and operation. The two tools are complementary and their integration can strengthen environmental protection.
This document summarizes several advanced oxidation processes (AOPs) and their effectiveness in treating wastewater. It discusses processes like Fenton, H2O2/UV, photocatalytic oxidation, supercritical water oxidation, ozone/UV, and ozone/H2O2/UV. It explains the chemical reactions involved in each process and factors that affect them. The document also summarizes biological wastewater treatment methods, focusing on suspended growth systems like sequencing batch reactors. The AOPs can mineralize toxic organic compounds, and combining them with biological treatment allows complete biodegradation.
This document discusses sludge processing and disposal. It defines sludge as organic matter that settles in sedimentation tanks during wastewater treatment. Left untreated, sludge decomposition causes foul odors and pollution. The document outlines various sludge treatment processes including thickening to reduce moisture, anaerobic and aerobic digestion to reduce volume and pathogens, and dewatering through methods like drying beds and centrifugation. The main objectives of sludge treatment are digesting organic matter, destroying pathogens, and achieving safe and odor-free disposal, such as through incineration, application to agricultural land, or ocean disposal.
The document discusses soil contamination, its causes from both natural and human activities, and various techniques for soil remediation. It describes how soil can become contaminated from accidental spills, mining, agriculture, transportation, dumping, and landfills. Common soil remediation techniques mentioned include bioremediation, thermal desorption, encapsulation, chemical oxidation, stabilization, soil washing, and soil disposal. The document concludes by recommending banning plastic bags, increasing recycling and plantation programs, and raising awareness to reduce soil contamination.
The document discusses sequencing batch reactors (SBRs) for wastewater treatment. SBRs perform the stages of treatment - equalization, biological treatment, and clarification - sequentially in a single tank. Key advantages are that SBRs require less space than traditional systems using separate tanks for each stage, and can achieve high removal rates of various pollutants. The SBR process involves repeated fill, react, settle, decant, and idle phases in the single tank reactor.
This document discusses phytoremediation, which uses plants to remove contaminants from soil, water, or sediment. It describes various phytoremediation processes like phytoextraction, rhizofiltration, phytostabilization, and phytotransformation. Case studies examine using water hyacinth and duckweed to remove heavy metals like cadmium and zinc from wastewater. While low-cost and environmentally friendly, phytoremediation has disadvantages like slow cleanup times and potential for contaminants to enter the food chain. Overall, phytoremediation can play a role in remediating contaminated sites in an ecological and sustainable manner.
The document discusses the effects of leachate recirculation and supplemental water addition on methane production and waste decomposition in simulated landfill reactors. Three reactors were used - a control reactor without leachate recirculation and two experimental reactors, one with leachate recirculation and one with leachate recirculation and supplemental water. The results showed that leachate recirculation increased methane production and accelerated waste stabilization compared to the control. Supplemental water addition further improved methane yields and allowed the reactor to enter methanogenesis earlier. Starting leachate recirculation after stabilization was also found to produce more methane than starting before stabilization.
Biorestoration deals with restoring or bringing back to an original or near original state using living micro-organisms. Nature has a built in check and balance system in everything it does. If there is too much or too little of something nature will use various life forms to try to re-establish a balance
This document presents information on upflow anaerobic sludge blanket (UASB) reactors. It discusses that the UASB technology was developed in the 1970s to treat industrial and sewage wastewater using anaerobic digestion. The key factors affecting UASB reactor performance are identified as organic loading rate, nutrients, hydraulic retention time, volatile fatty acids, operational temperature, and operational pH. Advantages of UASB reactors include high efficiency, simplicity, flexibility, low space and energy requirements, and low sludge production, while disadvantages include low pathogen/nutrient removal, long start-up times, potential for odors, and need for post-treatment.
The document discusses adsorption as a wastewater treatment method. It covers the classification of adsorption, common adsorbent materials like activated carbon, and applications of adsorption such as in water and wastewater treatment plants. Recent developments discussed include using modified adsorbents like nano-based materials and biomass-derived carbons, which can have enhanced adsorption capabilities compared to traditional adsorbents. The conclusion emphasizes that adsorption is a relatively affordable treatment option and that further research on green technologies could make safer water access more sustainable.
Solidification and Stabilisation (S/S) treatment of waste involves mixing cement into contaminated media or waste to immobilise contaminants within the treated material. The waste become more solid thereby lowering the solubility of toxic contaminants in the waste. In some cases, such as in stabilisation, the toxicity of the hazardous constituent(s) is lowered.
Stabilisation and Solidification has frequently been used for the treatment and immobilisation of soils and sludges containing one or more contaminants. Although there is no standard method of S/S application, selecting an appropriate binder is crucial to a successful treatment program. A well structured testing program guided by an understanding of the mechanisms involved in S/S system will reduce uncertainty in the selection process.
The document discusses industrial wastewater effluents and their treatment. It describes various sources and characteristics of industrial wastewater, as well as the pollutants commonly found in it. The objectives of industrial wastewater treatment are to allow safe disposal without harming the environment. Common treatment methods include preliminary, primary, secondary and tertiary treatments using various units and processes like screening, sedimentation, and biological processes. Both advantages and disadvantages of wastewater treatment systems are provided.
Presentation can help you to understand concept, principle engineering and important factors of landfilling such as component, requirement, microbial activity, landfill gas and leachate generation
Biofiltration is a pollution control technique that uses a bioreactor containing living material to biologically degrade pollutants in waste water, surface runoff, or contaminated air. It is a green process that uses small amounts of power compared to thermal or catalytic control units. There are different types of biofilters based on layout, support media used, and shape. The biofiltration process involves contaminated air passing through a moist filter medium that provides conditions for microorganisms to absorb and degrade the contaminants into carbon dioxide through a combination of adsorption, absorption, and microbial degradation. Major considerations for the filter medium include its ability to retain moisture and microbes, provide a large surface area, retain nutrients, and allow low resistance air
Adsorption is the process by which atoms or molecules from a gas, liquid or dissolved solid adhere to a surface. There are two main types - physical adsorption (physisorption) which involves weak van der Waals forces, and chemical adsorption (chemisorption) which involves stronger chemical bonds. Adsorption is affected by factors like temperature, pressure, surface area and characteristics of the adsorbent and adsorbate. Common commercial adsorbents include activated carbon, silica gel and zeolites. Adsorption isotherms like the Langmuir and Freundlich models describe the distribution of solute between phases at equilibrium. Adsorption has many applications including
Membrane bioreactors for wastewater treatmentwwwtwastewater
Membrane bioreactor (MBR) is the combination of a membrane filtration process with a suspended growth bioreactor. It is a very advanced technology and is now widely used
for municipal and industrial wastewater treatment.
Lecture note of Industrial Waste Treatment (Elective -III) as per syllabus of Solapur university for BE Civil
Prepared by
Prof S S Jahagirdar,
Associate Professor,
N K ORchid College of Engg and Tech,
Solapur
This paper was presented on the 8th November 2012 at an SCI conference on Processing Lignocellulosic Biomass. The conference was held at the UK's Centre for Process Innovation (CPI) at the Wilton Centre, Redcar, UK. The main focus of the event was on the UK role for biomass conversion, and the business and commericial implications of the technologies being developed.
Lecture Notes of Environmental Engg-II as per solapur university syllabus of TE Civil,
Prepared by
Prof S S Jahagirdar,
Associate Professor,
N K Orchid college of Engg and Technology,
Solapur
Environmental biotechnology uses biological processes to protect and restore the environment. Bioremediation uses microorganisms to degrade pollutants in air, water, and soil into less harmful substances. It can be used to treat wastewater, industrial effluents, drinking water, land, soil, air, and solid waste. Genetic engineering creates environmentally friendly alternatives by modifying microorganisms using recombinant DNA technology. Biotechnology shows potential to contribute to environmental remediation and protection.
Bioremediation is the use of either naturally occurring or deliberately introduced microorganisms to consume and break down environmental pollutants, in order to clean a polluted site.
and today we need our environment to be clean & lovable to stay healthy and secure future.
This document provides an overview of bioremediation and phytoremediation. It defines bioremediation as using biological organisms like microbes and plants to treat contaminated soil and water. The document discusses the history of bioremediation and categorizes different bioremediation techniques. It also outlines the pros and cons of various in-situ and ex-situ bioremediation methods like bioventing, bioaugmentation, biostimulation, biosparging, land farming and composting. Finally, it introduces the concept of phytoremediation and notes that it involves using plants to remediate environmental contaminants.
The document discusses environmental impact assessment (EIA) and its integration with environmental management systems (EMS). It provides background on EIA, including its origins in the National Environmental Policy Act of 1969, the tiered approach to assessments, and methods used in EIA like impact prediction and evaluation of alternatives. EIA aims to anticipate impacts of new projects at the planning stage, while EMS helps manage ongoing environmental impacts during construction and operation. The two tools are complementary and their integration can strengthen environmental protection.
This document summarizes several advanced oxidation processes (AOPs) and their effectiveness in treating wastewater. It discusses processes like Fenton, H2O2/UV, photocatalytic oxidation, supercritical water oxidation, ozone/UV, and ozone/H2O2/UV. It explains the chemical reactions involved in each process and factors that affect them. The document also summarizes biological wastewater treatment methods, focusing on suspended growth systems like sequencing batch reactors. The AOPs can mineralize toxic organic compounds, and combining them with biological treatment allows complete biodegradation.
This document discusses sludge processing and disposal. It defines sludge as organic matter that settles in sedimentation tanks during wastewater treatment. Left untreated, sludge decomposition causes foul odors and pollution. The document outlines various sludge treatment processes including thickening to reduce moisture, anaerobic and aerobic digestion to reduce volume and pathogens, and dewatering through methods like drying beds and centrifugation. The main objectives of sludge treatment are digesting organic matter, destroying pathogens, and achieving safe and odor-free disposal, such as through incineration, application to agricultural land, or ocean disposal.
The document discusses soil contamination, its causes from both natural and human activities, and various techniques for soil remediation. It describes how soil can become contaminated from accidental spills, mining, agriculture, transportation, dumping, and landfills. Common soil remediation techniques mentioned include bioremediation, thermal desorption, encapsulation, chemical oxidation, stabilization, soil washing, and soil disposal. The document concludes by recommending banning plastic bags, increasing recycling and plantation programs, and raising awareness to reduce soil contamination.
The document discusses sequencing batch reactors (SBRs) for wastewater treatment. SBRs perform the stages of treatment - equalization, biological treatment, and clarification - sequentially in a single tank. Key advantages are that SBRs require less space than traditional systems using separate tanks for each stage, and can achieve high removal rates of various pollutants. The SBR process involves repeated fill, react, settle, decant, and idle phases in the single tank reactor.
This document discusses phytoremediation, which uses plants to remove contaminants from soil, water, or sediment. It describes various phytoremediation processes like phytoextraction, rhizofiltration, phytostabilization, and phytotransformation. Case studies examine using water hyacinth and duckweed to remove heavy metals like cadmium and zinc from wastewater. While low-cost and environmentally friendly, phytoremediation has disadvantages like slow cleanup times and potential for contaminants to enter the food chain. Overall, phytoremediation can play a role in remediating contaminated sites in an ecological and sustainable manner.
The document discusses the effects of leachate recirculation and supplemental water addition on methane production and waste decomposition in simulated landfill reactors. Three reactors were used - a control reactor without leachate recirculation and two experimental reactors, one with leachate recirculation and one with leachate recirculation and supplemental water. The results showed that leachate recirculation increased methane production and accelerated waste stabilization compared to the control. Supplemental water addition further improved methane yields and allowed the reactor to enter methanogenesis earlier. Starting leachate recirculation after stabilization was also found to produce more methane than starting before stabilization.
Biorestoration deals with restoring or bringing back to an original or near original state using living micro-organisms. Nature has a built in check and balance system in everything it does. If there is too much or too little of something nature will use various life forms to try to re-establish a balance
This document presents information on upflow anaerobic sludge blanket (UASB) reactors. It discusses that the UASB technology was developed in the 1970s to treat industrial and sewage wastewater using anaerobic digestion. The key factors affecting UASB reactor performance are identified as organic loading rate, nutrients, hydraulic retention time, volatile fatty acids, operational temperature, and operational pH. Advantages of UASB reactors include high efficiency, simplicity, flexibility, low space and energy requirements, and low sludge production, while disadvantages include low pathogen/nutrient removal, long start-up times, potential for odors, and need for post-treatment.
The document discusses adsorption as a wastewater treatment method. It covers the classification of adsorption, common adsorbent materials like activated carbon, and applications of adsorption such as in water and wastewater treatment plants. Recent developments discussed include using modified adsorbents like nano-based materials and biomass-derived carbons, which can have enhanced adsorption capabilities compared to traditional adsorbents. The conclusion emphasizes that adsorption is a relatively affordable treatment option and that further research on green technologies could make safer water access more sustainable.
Solidification and Stabilisation (S/S) treatment of waste involves mixing cement into contaminated media or waste to immobilise contaminants within the treated material. The waste become more solid thereby lowering the solubility of toxic contaminants in the waste. In some cases, such as in stabilisation, the toxicity of the hazardous constituent(s) is lowered.
Stabilisation and Solidification has frequently been used for the treatment and immobilisation of soils and sludges containing one or more contaminants. Although there is no standard method of S/S application, selecting an appropriate binder is crucial to a successful treatment program. A well structured testing program guided by an understanding of the mechanisms involved in S/S system will reduce uncertainty in the selection process.
The document discusses industrial wastewater effluents and their treatment. It describes various sources and characteristics of industrial wastewater, as well as the pollutants commonly found in it. The objectives of industrial wastewater treatment are to allow safe disposal without harming the environment. Common treatment methods include preliminary, primary, secondary and tertiary treatments using various units and processes like screening, sedimentation, and biological processes. Both advantages and disadvantages of wastewater treatment systems are provided.
Presentation can help you to understand concept, principle engineering and important factors of landfilling such as component, requirement, microbial activity, landfill gas and leachate generation
Biofiltration is a pollution control technique that uses a bioreactor containing living material to biologically degrade pollutants in waste water, surface runoff, or contaminated air. It is a green process that uses small amounts of power compared to thermal or catalytic control units. There are different types of biofilters based on layout, support media used, and shape. The biofiltration process involves contaminated air passing through a moist filter medium that provides conditions for microorganisms to absorb and degrade the contaminants into carbon dioxide through a combination of adsorption, absorption, and microbial degradation. Major considerations for the filter medium include its ability to retain moisture and microbes, provide a large surface area, retain nutrients, and allow low resistance air
Adsorption is the process by which atoms or molecules from a gas, liquid or dissolved solid adhere to a surface. There are two main types - physical adsorption (physisorption) which involves weak van der Waals forces, and chemical adsorption (chemisorption) which involves stronger chemical bonds. Adsorption is affected by factors like temperature, pressure, surface area and characteristics of the adsorbent and adsorbate. Common commercial adsorbents include activated carbon, silica gel and zeolites. Adsorption isotherms like the Langmuir and Freundlich models describe the distribution of solute between phases at equilibrium. Adsorption has many applications including
Membrane bioreactors for wastewater treatmentwwwtwastewater
Membrane bioreactor (MBR) is the combination of a membrane filtration process with a suspended growth bioreactor. It is a very advanced technology and is now widely used
for municipal and industrial wastewater treatment.
Lecture note of Industrial Waste Treatment (Elective -III) as per syllabus of Solapur university for BE Civil
Prepared by
Prof S S Jahagirdar,
Associate Professor,
N K ORchid College of Engg and Tech,
Solapur
This paper was presented on the 8th November 2012 at an SCI conference on Processing Lignocellulosic Biomass. The conference was held at the UK's Centre for Process Innovation (CPI) at the Wilton Centre, Redcar, UK. The main focus of the event was on the UK role for biomass conversion, and the business and commericial implications of the technologies being developed.
Lecture Notes of Environmental Engg-II as per solapur university syllabus of TE Civil,
Prepared by
Prof S S Jahagirdar,
Associate Professor,
N K Orchid college of Engg and Technology,
Solapur
Environmental biotechnology uses biological processes to protect and restore the environment. Bioremediation uses microorganisms to degrade pollutants in air, water, and soil into less harmful substances. It can be used to treat wastewater, industrial effluents, drinking water, land, soil, air, and solid waste. Genetic engineering creates environmentally friendly alternatives by modifying microorganisms using recombinant DNA technology. Biotechnology shows potential to contribute to environmental remediation and protection.
Bioremediation is the use of either naturally occurring or deliberately introduced microorganisms to consume and break down environmental pollutants, in order to clean a polluted site.
and today we need our environment to be clean & lovable to stay healthy and secure future.
This document provides an overview of bioremediation and phytoremediation. It defines bioremediation as using biological organisms like microbes and plants to treat contaminated soil and water. The document discusses the history of bioremediation and categorizes different bioremediation techniques. It also outlines the pros and cons of various in-situ and ex-situ bioremediation methods like bioventing, bioaugmentation, biostimulation, biosparging, land farming and composting. Finally, it introduces the concept of phytoremediation and notes that it involves using plants to remediate environmental contaminants.
This document discusses the composting process and management. It describes composting as a controlled, aerobic, biological process for biodegrading organic matter. The document outlines different composting systems including open-air piles and windrows, boxes or trenches, and bioreactors. It also discusses composting as a microbiological, chemical, and physical process, describing the succession of microbial populations involved and optimal temperature ranges for degradation. Proper management is important to maximize degradation while avoiding odor issues or contamination.
A detailed presentation on current hot emerging topic BIOREMEDIATION explaining the process and the needs with advantages and disadvantages of the same
This document discusses bioremediation, which uses microorganisms to remove pollution from soil, water, and air. There are two types of bioremediation - in situ, which treats pollution at the site, and ex situ, which treats pollution off site. In situ bioremediation can be intrinsic, using native microbes, or engineered, by adding nutrients or microbes. Ex situ involves removing contaminated material and treating it through methods like slurry phase bioremediation, which mixes soil and water, or solid phase bioremediation using land farming or piles. Bioremediation is effective but performance is difficult to evaluate and volatile organic compounds remain challenging to degrade.
This document provides an overview of bioremediation presented by Md. Shoyeb. It defines bioremediation as using organisms or their enzymes to return polluted environments to their original condition. The mechanisms, principles, strategies (in situ and ex situ), types (bioventing, biosparging, bioaugmentation), advantages and disadvantages are summarized. Key contaminants amenable to bioremediation are identified along with persistent pollutants that are difficult to degrade.
The document discusses a project thesis submitted by two students, Jariwala Jenil and Joshi Riddhi, to the Department of Biotechnology at V.V.P. Engineering College in fulfillment of the requirements for a Bachelor of Engineering degree. The thesis examines the biodegradation of an oil contaminated site through isolation of microorganisms from contaminated soil and analyzing their ability to degrade various types of oil through growth measurements and degradation calculations. The students conducted the work under the supervision of Dr. Krishna Joshi to fulfill their degree requirements.
This document provides an overview of bioremediation of hydrocarbon pollution. It discusses various techniques used for hydrocarbon pollution removal and their disadvantages. It then describes bioremediation as a natural process that uses microorganisms to degrade hydrocarbons into less toxic forms. The document outlines different bioremediation strategies like bioaugmentation and biostimulation and notes advantages such as low cost and generating non-toxic byproducts. It also discusses using genetically engineered microorganisms and phytoremediation using plants. In conclusion, the document emphasizes the need for understanding biodegradation mechanisms to transform pollutants in less toxic forms using microorganisms and plants.
Bioremediation uses microorganisms to remove or break down environmental pollutants. There are different types including biostimulation, which involves adding nutrients to stimulate microbes, and bioaugmentation, which involves adding microbes. Bioremediation can be used to treat a variety of pollutants including hydrocarbons from oil spills. It involves optimizing soil conditions like moisture, aeration, and pH to promote microbial activity. Bioremediation offers a natural, low-cost approach to cleanup, but may take a long time and not work for all contaminants.
This document discusses various types of bioremediation techniques used to clean up contaminated soil and groundwater. It defines bioremediation as using living microorganisms to degrade environmental pollutants or prevent pollution. The two main types of bioremediation are in situ, which treats contaminants in place, and ex situ, which involves removing contaminated material to be treated elsewhere. Specific techniques discussed include bioaugmentation, bioslurping, biosparging, natural attenuation, bioventing, and biostimulation. The advantages and limitations of bioremediation are also summarized.
This document discusses bioremediation of BTEX (benzene, toluene, ethylbenzene, and xylenes) compounds. It provides background on what BTEX are, how they enter the environment, their health effects, and what bioremediation is. It then describes different bioremediation techniques for BTEX including in situ bioremediation approaches like intrinsic and engineered bioremediation. Key factors that affect bioremediation success like nutrients, moisture, temperature, and electron acceptors are explained. Advantages and disadvantages of in situ bioremediation are summarized. The role of different microbes and electron acceptors in the biodegradation process is also outlined.
This document summarizes chemical pollution of soil. It defines soil pollution and describes natural and man-made causes such as urbanization, agriculture, and garbage. It discusses chemical pollution from toxic, flammable, and explosive chemicals used in activities. Methods to handle chemical pollution include reducing chemical use, managing chemicals carefully, and using bioremediation. Bioremediation techniques like phytoremediation use plants to degrade contaminants. Organoclays can also immobilize soil contaminants. The document provides examples of polluted organic compounds and discusses in-situ and ex-situ methods to control chemical pollution in soil.
The International Journal of Engineering & Science is aimed at providing a platform for researchers, engineers, scientists, or educators to publish their original research results, to exchange new ideas, to disseminate information in innovative designs, engineering experiences and technological skills. It is also the Journal's objective to promote engineering and technology education. All papers submitted to the Journal will be blind peer-reviewed. Only original articles will be published.
The papers for publication in The International Journal of Engineering& Science are selected through rigorous peer reviews to ensure originality, timeliness, relevance, and readability.
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BIOTECHNOLOGICAL APPROACHES TOWARDS WATER WASTE MANAGEMENT saadmughal1271
This document discusses various biotechnological approaches for wastewater treatment, including engineered biosorbents for heavy metal removal, displaying metal binding peptides on microorganisms, and designing strains for enhanced biodegradation. It describes common wastewater treatment processes like the trickling filter, activated sludge process, and anaerobic digestion. Finally, it discusses using these biotechnological methods to treat wastewater from textile and desiccated coconut industries.
LABORATORY STUDIES ON THE BIOREMEDIATION OF SOIL CONTAMINATED BY DIESEL IAEME Publication
The most widely used energy and fuel resources are hydrocarbons such as crude oil and petroleum distillates. The accidental discharge of these petroleum products contribute in making hydrocarbons the most common environmental pollutants. Bioremediation helps to destroy or render harmless various contaminants using natural biological activity. The present study utilizes the potential of bioremediation to remediate soil contaminated with diesel. Eight bioreactors were used for the study, out of which four bioreactors were maintained at optimum environmental conditions and the remaining four were kept without any maintenance to serve as control bioreactors. Contaminated soil was prepared by mixing fresh soil and diesel so as to attain 10% TPH concentrations by weight of soil. Each bioreactor was filled with 3 kg of contaminated soil.
The document discusses various methods of bioremediation and biodegradation to remediate contaminated soil and groundwater. It defines bioremediation as using biological organisms such as bacteria and fungi to solve environmental problems through technological innovation. Biodegradation is the natural breakdown of materials by microorganisms. The document then describes various in situ and ex situ bioremediation techniques in detail, including bioventing, biosparging, bioslurping, phytoremediation, land farming, biopiles, and windrows. The key factors in selecting a bioremediation method are the contaminants present, their accessibility to microbes, and any environmental conditions that could inhibit microbial activity.
Biogas Generation and Factors Affecting Global WarmingIRJET Journal
This document discusses biogas generation and its role in reducing global warming. It begins by introducing biogas as a mixture of methane and carbon dioxide produced through anaerobic digestion of organic waste. This process reduces pollution and global warming by converting methane into energy. The document then discusses the factors that affect biogas production, including temperature, retention time in digesters, and types of digestion systems. Maintaining the optimal temperature range in digesters and sufficient retention time are important for efficient biogas generation through anaerobic digestion.
Bioremediation of petroleum hydrocarbons in contaminated soilH Almasi
The document discusses bioremediation of petroleum hydrocarbons in contaminated soil. It defines total petroleum hydrocarbons (TPH) as a measure of various chemicals found in crude oil and petroleum products. Bioremediation uses microorganisms like bacteria, fungi, and plants to break down harmful contaminants into less toxic forms. There are two main approaches: bioaugmentation, which adds degrading organisms, and biostimulation, which adds nutrients to stimulate microbial activity. The document also describes different types of bioremediation techniques, including in situ and ex situ methods, and provides examples like biosparging, bioventing, and biopiles.
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3. SITE CONTAMINATION
Land Contamination - Environmental Problem
Contaminants Accumulate -Toxic to Biological Systems
Treatment and disposal of hazardous wastes carefully
controlled
Hydrocarbon contamination of land and water is serious
issue since the discovery of oil
6. OIL CONTAMINATION
Every year, about 1.7 to 8.8 million metric tons of oil is
released into the environment
Crude oil released to land or marine environment is
immediately subject to a variety of physical, chemical and
biological changes
Removal of the hydrocarbon from soil and from water
surface is an essential practice to prevent site
contamination
Any remained portion of crude oil in the ground acts as a
permanent source of contamination
7. EFFECTS1. ENVIRONMENTAL EFFECTS
Oil contamination creates hazards to the local
environment
water, soil and air have been severely tainted by petroleum
pollutants
As a result, wildlife, livestock, and humans have been
sickened
Oil contamination has adversely affected the lives of many
people living in areas near oil exploration sites
8. EFFECTS(cont.)2. HEALTH EFFECTS
One of the largest problems caused by the oil waste is
pollution seeping into the water supply of the
communities in the area
People have gotten horrible rashes and sores on their skin
from bathing in water that is severely contaminated by oil
People who live near oil pits, have been struck with cancer
of the stomach, rectum, skin, soft tissue, kidney, cervix,
and lymph nodes
9. EFFECTS(cont.)
3. AGRICULTURAL EFFECTS
serious damage on the physiological, anatomical and
growth performance of plants, soil components and aquatic
ecosystems
Sustainable use of agricultural soil on which plants depend
is absolutely necessary for agricultural productivity
creates unsatisfactory conditions for plant growth probably
due to insufficient aeration of the soil
Oil readily penetrates the pore space of terrestrial
vegetation following any spill with heavier friction which
may block the pores and this subsequently impedes
photosynthesis and other physiological processes in plant
10. REMEDIATION
Remediation means the management of the site in order to
prevent damage to human health or the environment and
restoring all or part of the site to a useful purpose
There are physical, chemical, thermal and biological
techniques available for treating contaminated sites
All these techniques can be successfully applied if the
physicochemical properties of pollutants and soil particles
are well understood before selecting any method
11. PHYSICO-CHEMICAL
METHODS
1.SOIL WASHING
Ex-situ remediation technique
Washing the soil with a liquid,scrubbing the soil
Separation of contaminated fines and wash water from
cleaned course grained soil
Important factor affecting this process is the percentage of
fines in the soil
13. PHYSICO-CHEMICAL
METHODS
(cont.)
2. SOIL VAPOUR EXTRACTION
Also known as soil venting or vacuum extraction
Involves installation of vertical or horizontal wells in the
area of contamination
removes volatile and semi-volatile contaminants from the
unsaturated zone by applying a vacuum connected to a
series of wells
15. PHYSICO-CHEMICAL
METHODS
(cont.)
3. SOLIDIFICATION/ STABILIZATION
“Solidification” refers to a process in which materials are
added to the waste to produce an immobile mass
“Stabilization” refers to converting a waste to a more
chemically stable form
Method always includes use of physicochemical reaction
to transform the contaminants to a less toxic form
16. PHYSICO-CHEMICAL
METHODS
(cont.)
encapsulates hazardous waste into a solid material of high
structural integrity
2 Types:
Asphalt Batching:incorporates petroleum-laden soils into
hot asphalt mixtures as a partial substitute for stone
aggregate
Vitrification:uses a powerful source of energy to ‘melt’
soil or other earthen materials at extremely high
temperatures, immobilizing most inorganics and
destroying organic pollutants by pyrolysis
17. PHYSICO-CHEMICAL
METHODS
(cont.)
4. AIR SPARGING
Air sparging is a process during which air is injected into
the saturated zone below or within the areas of
contamination
Most effective at sites with homogeneous, high-
permeability soils and unconfined aquifers contaminated
with VOCs
the injected air rises through the formation, it may
volatilize and remove adsorbed volatile organic
compounds (VOC) in soils within the saturated zone as
well as strip dissolved contaminants from groundwater
19. THERMAL METHODS
1.THERMAL DESORPTION
The process desorbs (physically separates) organics from
the soil without decomposition
desorption removes organic contaminants from soil, by
heating them in a machine called a “thermal desorber” to
evaporate the contaminants
21. THERMAL METHODS(cont.)
2. INCINERATION
The main goal of incineration is to heat the contaminated
media to temperatures between 870 and 1,200 0C
Volatilizing and burning halogenated organic compounds
and other compounds that are difficult to remove
works best for soils with low water content
23. THERMAL METHODS(cont.)
3. STEAM INJECTION
In situ thermal treatment method
Steam at high temperature and compressed air are injected
into the contaminated soil
temperature of the injected steam should be higher than
the boiling points 220 °C of the volatile compounds
24. BIOLOGICAL METHODS
1.BIOREMEDIATION
Technique utilizes the natural biological activity of
microorganisms to transform the toxic components into
less toxic metabolites
requires the addition of nitrate or sulphate fertilizers to
aid the decomposition of hydrocarbon compounds
Downsides of bioremediation are:
(1) Restricted to petroleum components that are microbial
degradable
(2) Process take long times for completion
26. BIOLOGICAL METHODS (cont.)
2. LAND FARMING
Is an above-ground remediation technology that reduces the
concentration of petroleum
Bacteria selected for breaking down hydrocarbon are added to
the soil to achieve speedy degradation.
Lighter petroleum hydrocarbons tend to be removed by
evaporation during aeration processes and degraded by
microbial respiration.
Heavier petroleum hydrocarbons do not evaporate during
aeration but are broken down by microorganisms present in the
soil at the treatment site.
27. BIOLOGICAL METHODS (cont.)
3. BIOPILES
piling of petroleum-contaminated soils into piles or heaps
and then simulating aerobic microbial activity by aeration
and the addition of minerals, nutrients, and moisture
Soil characteristics play a major role in the success of bio
piles include texture, permeability, moisture content, and
bulk density
31. BIOLOGICAL METHODS (cont.)
5. BIOVENTING
Process injects air into the contaminated media at a rate
designed to:
• Maximize in situ biodegradation
• Minimize off-gassing of volatilized contaminants to the
atmosphere
Degrades less volatile organic contaminants
Allows for the treatment of less permeable soils have
studied the optimized performance and effectiveness of in
situ bioventing.
33. BIOLOGICAL METHODS (cont.)
6. BIOSLURPING
New in situ remediation technology
Combines elements of bioventing and vacuum-enhanced
pumping to recover free product from the groundwater
and soil
Vacuum extraction removes free product along with some
groundwater
The reduction in the amount of extracted groundwater and
the ability to extract soil–gas at concentrations minimizes
storage, treatment, and disposal costs, thus reducing
project costs
35. FACTORS TO CONSIDER WHEN SELECTING A
REMEDIATION TECHNIQUE
1. SITE CHARACTERISTICS
Site topography
Site surface and subsurface structures and utilities
Site size
Depth to groundwater and flow direction
36. FACTORS TO CONSIDER WHEN SELECTING A
REMEDIATION TECHNIQUE(cont.)
2. SOIL CHARACTERISTICS
Grain size
Total organic carbon
Soil pH
Soil moisture
Soil temperature
Soil permeability
37. FACTORS TO CONSIDER WHEN SELECTING A
REMEDIATION TECHNIQUE(cont.)
3. CONTAMINANT CHARACTERISTICS
Extent of contamination
Contaminant concentration
Depth of contaminant
Contaminant biodegradability
Contaminant volatility
38. CONCLUSION
Over the years, many remediation methods have been
developed and applied.
Remediation of oil contaminated environments is difficult
because petroleum is a complex mixture of chemical
compounds
There exists some chemical and biological methods to control
oil spills, frequently applied are chemical methods because the
chemical remediation of oil spills is faster if compared to
bioremediation.
Bioremediation is getting worldwide attention, as it can be
more cost-effective and it can selectively degrade the pollutants
without damaging the site
39. CONCLUSION(cont.)
Removal efficiency depends on the type of oil, type of soil,
weather conditions, penetration depth, and sensitivity of the
location and the toxicity of the chemicals.
Site characteristics, soil characteristics, and contaminant
characteristics should be considered for selecting the most
suitable remedial method.
As there is no universal method can be generally applied to
completely remove the oil from contaminated sites, thus, the
preventing oil spills or leakages should be the first concern.
If oil spills or leakages occur, response should be taken
immediately to minimize the potential environmental
consequences.
40. REFERENCES
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Malaya, Kuala Lumpur, Malaysia,” Remediation of Contaminated Sites”.
Dike Bu,Yong-Gook Jung & Agbo KC(2013),Department of Civil Engineering,
Federal University of Technology, Owerri, Nigeria, Africa, Journal of Civil &
Environmental Engineering, ”Remediation of Used Oil Contaminated Soil: A soil
washing treatment approach”.
Faisal I. Khan & Tahir Husain(2004), Faculty of Engineering and Applied
Science, Memorial University of Newfoundland, St John’s NL, Canada ,Journal of
Environmental Management 71 (2004) 95–122, “An overview and analysis of site
remediation technologies”.
Mohammed M Amro(2004), Petroleum Engineering Department, King Saud
University, P.O. Box 800, Riyadh 11421, Saudi Arabia, International Conf. on Water
Resources & Arid Environment ,“Treatment Techniques of Oil Contaminated Soil
and Water Aquifers”.
Uchechukwu E. Ezeji & Sylvia O. Anyadoh(2007), Department of Biotechnology,
Federal University of Technology, Owerri, Nigeria, Terrestrial and Aquatic
Environmental Toxicology,”Clean up of Crude oil contaminated soil”.