The document discusses biodegradation and bioremediation. It defines biodegradation as nature's way of breaking down organic matter using microorganisms. Biodegradation can occur aerobically or anaerobically. Bioremediation uses microorganisms to transform hazardous contaminants into less harmful byproducts and is used to treat contaminated sites. There are two types of bioremediation - in situ, which treats contamination on site, and ex situ, which physically extracts contaminated media. Ex situ techniques include solid phase methods like landfarming and biopiling, and slurry phase treatment in bioreactors. Bioremediation has advantages of being relatively low cost and having general public acceptance.
•Introduction of bioremediation: Bioremediation refers to the process of using microorganisms to remove the environmental pollutants i.e. toxic wastes found in soil, water, air etc.
•In situ bioremediation:
It involves a direct approach for the microbial
degradation of xenobiotics at the sites of pollution
(soil, ground water).
•Types of in situ bioremediation:
Natural attenuation.
Engineered in situ bioremediation.
- Bioventing, biosparging, bioslurping,
phytoremediation.
•Ex situ bioremediation:
Waste or toxic pollutants can be collected from the polluted sites and bioremediation can be carried out at a designated place or site.
• Types of ex situ bioremediation
Land farming, windrow, biopiles, bioreactors.
•Microorganisms use in bioremediation:
A number of naturally occurring marine microbes
such as Pseudomonas sp. is capable of degrading oil and other hydrocarbons.
•Factors affecting bioremediation:
Nutrient availability, moisture content, pH, temperature, contaminant availability.
•References:
Satyanarayana U. Biotechnology. BOOKS AND ALLIED (P) Ltd.
Sharma P.D. Environmental Microbiology. RASTOGI PUBLICATIONS.
Gupta P.K. Biotechnology and Genomics. RASTOGI PUBLICATIONS.
Dubey R.C. A Textbook of Biotechnology. S Chand And Company Ltd.
Dubey R.C. A Textbook of Microbiology. S Chand And Company Ltd.
Willey/Sherwood/Woolverton. Prescott’s Microbiology. McGRAW-HILL INTERNATIONAL EDITION.
www.sciencedirect.com/bioremediation.
This ppt contains all types of Microbial Bioremediation methods . Everyone can understand clearly . Explaining with neat pictures and animation . Useful for presentation about Microbes in bioremediation . At last it contains a small animated video which helps to get clear view .
• Bioremediation – process of cleaning up environmental sites contaminated with chemical pollutants by using living organisms to degrade hazardous materials into less toxic substances
•Introduction of bioremediation: Bioremediation refers to the process of using microorganisms to remove the environmental pollutants i.e. toxic wastes found in soil, water, air etc.
•In situ bioremediation:
It involves a direct approach for the microbial
degradation of xenobiotics at the sites of pollution
(soil, ground water).
•Types of in situ bioremediation:
Natural attenuation.
Engineered in situ bioremediation.
- Bioventing, biosparging, bioslurping,
phytoremediation.
•Ex situ bioremediation:
Waste or toxic pollutants can be collected from the polluted sites and bioremediation can be carried out at a designated place or site.
• Types of ex situ bioremediation
Land farming, windrow, biopiles, bioreactors.
•Microorganisms use in bioremediation:
A number of naturally occurring marine microbes
such as Pseudomonas sp. is capable of degrading oil and other hydrocarbons.
•Factors affecting bioremediation:
Nutrient availability, moisture content, pH, temperature, contaminant availability.
•References:
Satyanarayana U. Biotechnology. BOOKS AND ALLIED (P) Ltd.
Sharma P.D. Environmental Microbiology. RASTOGI PUBLICATIONS.
Gupta P.K. Biotechnology and Genomics. RASTOGI PUBLICATIONS.
Dubey R.C. A Textbook of Biotechnology. S Chand And Company Ltd.
Dubey R.C. A Textbook of Microbiology. S Chand And Company Ltd.
Willey/Sherwood/Woolverton. Prescott’s Microbiology. McGRAW-HILL INTERNATIONAL EDITION.
www.sciencedirect.com/bioremediation.
This ppt contains all types of Microbial Bioremediation methods . Everyone can understand clearly . Explaining with neat pictures and animation . Useful for presentation about Microbes in bioremediation . At last it contains a small animated video which helps to get clear view .
• Bioremediation – process of cleaning up environmental sites contaminated with chemical pollutants by using living organisms to degrade hazardous materials into less toxic substances
Hydrocarbon are major constituents of crude oil and petroleum. They can be biodegraded by naturally-occurring microorganisms in freshwater and marine environments under a variety of aerobic and anaerobic conditions. The ability of microorganisms - bacteria, archaea, fungi, or algae - to break down hydrocarbons is the basis for natural and enhanced bioremediation. To promote biodegradation, amendments such as nitrogen and phosphorous fertilizer are often added to stimulate microbial growth and metabolism
Introduction
Type of pesticides
Advantage & disadvantages of pesticides
Degradation of pesticide
Microbial degradation of pesticides
Mode of microbial metabolism of pesticides
Strategies for biodegradation
Approaches for biodegradation of pesticide
Chemical reaction leading biodegradation of pesticide
Metabolism of pesticides by MO
Metabolism of DDT
Environmental Microbiology: Microbial degradation of recalcitrant compoundsTejaswini Petkar
A brief presentation on 'Microbial degradation of recalcitrant compounds'- their classes,their sources, the microorganisms involved and their modes of degradation,
A pesticide can be defined as any substance or mixture of substances intended for preventing, destroying, repelling, or mitigating any pest.
Pesticides like insecticides, herbicides, fungicides, and various other substances are used to control or inhibit plant diseases and insect pests.
The positive aspect of application of pesticides renders enhanced crop/food productivity and drastic reduction of vector-borne diseases.
However excessive use of these chemicals leads to the microbial imbalance, environmental pollution and health hazards.
Due to these problems, development of technologies that guarantee their elimination in a safe, efficient and economical way is important.
IntroductionDefinitionPescidesType of pesticidesFate of pesticides in environmentBiodegradation of pesticides in soil Criteria for biodegradation
Strategies for biodegradationDifferent approaches of biodegradationChemical reaction leading to biodegradationChanging the spectrum of toxicityExample of biodegradationAdvantageDisadvantage
Chlorinated benzenes, including chlorobenzene (CB) and 1,2-dichlorobenzene (DCB) are widely used as chemical intermediates and solvents
across industry. Soil contaminated with these compounds was treated in a pilot-scale trial in 6m3 cells. Air was drawn through each cell and
exhausted via an activated carbon (GAC) filter system. The trial objective was to stimulate native microflora with nutrients and varying levels
of organic amendments (0%, 12% and 35%). Initial soil DCB concentrations varied from <1 /><5% of the chlorinated benzenes were removed by volatilization
and 90% removed by biodegradation. Laboratory shake flask trials confirmed that the soils in the pilot-scale treatment contained a microbial
consortium capable of mineralizing CB and DCB. This consortium was capable of mineralizing both CB and DCB with up to 50% of carbon added
as chlorinated benzene substrate being recovered as CO2 and up to 44% of organic chlorine being released as chloride ion in mineralization tests,
further confirming these chlorinated benzenes were biodegraded. The study confirms that vented ex-situ biotreatment processes for chlorinated
benzenes can be achieved without excessive losses from volatilization and that naturally occurring microflora can be readily stimulated with aeration
and nutrients.
Hydrocarbon are major constituents of crude oil and petroleum. They can be biodegraded by naturally-occurring microorganisms in freshwater and marine environments under a variety of aerobic and anaerobic conditions. The ability of microorganisms - bacteria, archaea, fungi, or algae - to break down hydrocarbons is the basis for natural and enhanced bioremediation. To promote biodegradation, amendments such as nitrogen and phosphorous fertilizer are often added to stimulate microbial growth and metabolism
Introduction
Type of pesticides
Advantage & disadvantages of pesticides
Degradation of pesticide
Microbial degradation of pesticides
Mode of microbial metabolism of pesticides
Strategies for biodegradation
Approaches for biodegradation of pesticide
Chemical reaction leading biodegradation of pesticide
Metabolism of pesticides by MO
Metabolism of DDT
Environmental Microbiology: Microbial degradation of recalcitrant compoundsTejaswini Petkar
A brief presentation on 'Microbial degradation of recalcitrant compounds'- their classes,their sources, the microorganisms involved and their modes of degradation,
A pesticide can be defined as any substance or mixture of substances intended for preventing, destroying, repelling, or mitigating any pest.
Pesticides like insecticides, herbicides, fungicides, and various other substances are used to control or inhibit plant diseases and insect pests.
The positive aspect of application of pesticides renders enhanced crop/food productivity and drastic reduction of vector-borne diseases.
However excessive use of these chemicals leads to the microbial imbalance, environmental pollution and health hazards.
Due to these problems, development of technologies that guarantee their elimination in a safe, efficient and economical way is important.
IntroductionDefinitionPescidesType of pesticidesFate of pesticides in environmentBiodegradation of pesticides in soil Criteria for biodegradation
Strategies for biodegradationDifferent approaches of biodegradationChemical reaction leading to biodegradationChanging the spectrum of toxicityExample of biodegradationAdvantageDisadvantage
Chlorinated benzenes, including chlorobenzene (CB) and 1,2-dichlorobenzene (DCB) are widely used as chemical intermediates and solvents
across industry. Soil contaminated with these compounds was treated in a pilot-scale trial in 6m3 cells. Air was drawn through each cell and
exhausted via an activated carbon (GAC) filter system. The trial objective was to stimulate native microflora with nutrients and varying levels
of organic amendments (0%, 12% and 35%). Initial soil DCB concentrations varied from <1 /><5% of the chlorinated benzenes were removed by volatilization
and 90% removed by biodegradation. Laboratory shake flask trials confirmed that the soils in the pilot-scale treatment contained a microbial
consortium capable of mineralizing CB and DCB. This consortium was capable of mineralizing both CB and DCB with up to 50% of carbon added
as chlorinated benzene substrate being recovered as CO2 and up to 44% of organic chlorine being released as chloride ion in mineralization tests,
further confirming these chlorinated benzenes were biodegraded. The study confirms that vented ex-situ biotreatment processes for chlorinated
benzenes can be achieved without excessive losses from volatilization and that naturally occurring microflora can be readily stimulated with aeration
and nutrients.
Bioremediation is the use of microorganisms (e.g., bacteria, fungi), plants (termed phytoremediation), or biological enzymes to achieve treatment of hazardous waste. Treatment can target a variety of media (wastewater, groundwater, soil/sludge, gas) with several possible objectives (e.g., mineralization of organic compounds, immobilzation of contaminants). In situ bioremediation (ISB) is the application of bioremediation in the subsurface – as compared to ex situ bioremediation, which applies to media readily accessible aboveground (e.g., in treatment cells/soil piles or bioreactors). In situ bioremediation may be applied in the unsaturated/vadoze zone (e.g., bioventing) or in saturated soils and groundwater (Sharma S. 2012).
A Biosensor is a device for the detection of an analyte that combines a biological component with a physio-chemical detector component.
Download: https://www.topicsforseminar.com/2014/10/biosensors-ppt.html
Biosensor is the Talk of The Day. It made possible, the conversion of yesteryear's cumbersome experiments to an easier, faster all the while improving its sensitivity and specificity. This article will help you to gain an acquaintance about it, its properties, etc.
A detailed presentation on current hot emerging topic BIOREMEDIATION explaining the process and the needs with advantages and disadvantages of the same
Bioremediation
Bioremediation refers to the use of either naturally occurring or
deliberately introduced microorganisms to consume and break down
environmental pollutants, in order to clean a polluted site.
The process of bioremediation enhances the rate of the natural
microbial degradation of contaminants by supplementing the
indigenous microorganisms (bacteria or fungi) with nutrients, carbon
sources, or electron donors (biostimulation, biorestoration) or by
adding an enriched culture of microorganisms that have specific
characteristics that allow them to degrade the desired contaminant at
a quicker rate (bioaugmentation).
It is a cleaning process that degrades dangerous contaminants using
naturally existing microbes. These bacteria may consume and
degrade organic chemicals as a source of food and energy, degrade
organic substances that are dangerous to living creatures, including
humans, and degrade the organic pollutants into inert products.
Because the bacteria already exist in nature, they offer no pollution
concern
Bioremediation is the use of
microorganisms or microbial processes
to detoxify and degrade environmental
contaminants.
Microorganisms have been used for the
routine treatment and transformation
of waste products for several decades
Bioremediation strategies rely on
having the correct microorganisms in
the right location at the right time in the
right environment for degradation to
occur. The appropriate microorganisms
are bacteria and fungi that have the
physiological and metabolic
competence to breakdown pollutants
Objective of Bioremediation
The objective of bioremediation is to decrease pollutant levels to
undetectable, nontoxic, or acceptable levels, i.e., within regulatory
limits, or, ideally, to totally mineralize organopollutants to carbon
dioxide
BIOREMEDIATION AND THEIR IMPORTANCE IN ENVIRONMENT
PROTECTION
Bioremediation is defined as ‘the process of using microorganisms to remove
the environmental pollutants where microbes serve as scavengers’.
• The removal of organic wastes by microbes leads to environmental clean-up.
The other names/terms used for bioremediation are biotreatment,
bioreclamation, and biorestoration.
• The term “Xenobiotics” (xenos means foreign) refers to the unnatural, foreign
and synthetic chemicals, such as pesticides, herbicides, refrigerants, solvents
and other organic compounds.
• The microbial degradation of xenobiotics also helps in reducing the
environmental pollution. Pseudomonas which is a soil microorganism
effectively degrades xenobiotics.
• Different strains of Pseudomonas that are capable of detoxifying more than
100 organic compounds (e.g. phenols, biphenyls, organophosphates,
naphthalene, etc.) have been identified.
• Some other microbial strains are also known to have the capacity to degrade
xenobiotics such as Mycobacterium, Alcaligenes, Norcardia, etc.
Factors affecting biodegradation
The factors that affect the
biodegradation are:
• the chemical nature of
xenobiotics,
• the conc
Willie Nelson Net Worth: A Journey Through Music, Movies, and Business Venturesgreendigital
Willie Nelson is a name that resonates within the world of music and entertainment. Known for his unique voice, and masterful guitar skills. and an extraordinary career spanning several decades. Nelson has become a legend in the country music scene. But, his influence extends far beyond the realm of music. with ventures in acting, writing, activism, and business. This comprehensive article delves into Willie Nelson net worth. exploring the various facets of his career that have contributed to his large fortune.
Follow us on: Pinterest
Introduction
Willie Nelson net worth is a testament to his enduring influence and success in many fields. Born on April 29, 1933, in Abbott, Texas. Nelson's journey from a humble beginning to becoming one of the most iconic figures in American music is nothing short of inspirational. His net worth, which estimated to be around $25 million as of 2024. reflects a career that is as diverse as it is prolific.
Early Life and Musical Beginnings
Humble Origins
Willie Hugh Nelson was born during the Great Depression. a time of significant economic hardship in the United States. Raised by his grandparents. Nelson found solace and inspiration in music from an early age. His grandmother taught him to play the guitar. setting the stage for what would become an illustrious career.
First Steps in Music
Nelson's initial foray into the music industry was fraught with challenges. He moved to Nashville, Tennessee, to pursue his dreams, but success did not come . Working as a songwriter, Nelson penned hits for other artists. which helped him gain a foothold in the competitive music scene. His songwriting skills contributed to his early earnings. laying the foundation for his net worth.
Rise to Stardom
Breakthrough Albums
The 1970s marked a turning point in Willie Nelson's career. His albums "Shotgun Willie" (1973), "Red Headed Stranger" (1975). and "Stardust" (1978) received critical acclaim and commercial success. These albums not only solidified his position in the country music genre. but also introduced his music to a broader audience. The success of these albums played a crucial role in boosting Willie Nelson net worth.
Iconic Songs
Willie Nelson net worth is also attributed to his extensive catalog of hit songs. Tracks like "Blue Eyes Crying in the Rain," "On the Road Again," and "Always on My Mind" have become timeless classics. These songs have not only earned Nelson large royalties but have also ensured his continued relevance in the music industry.
Acting and Film Career
Hollywood Ventures
In addition to his music career, Willie Nelson has also made a mark in Hollywood. His distinctive personality and on-screen presence have landed him roles in several films and television shows. Notable appearances include roles in "The Electric Horseman" (1979), "Honeysuckle Rose" (1980), and "Barbarosa" (1982). These acting gigs have added a significant amount to Willie Nelson net worth.
Television Appearances
Nelson's char
WRI’s brand new “Food Service Playbook for Promoting Sustainable Food Choices” gives food service operators the very latest strategies for creating dining environments that empower consumers to choose sustainable, plant-rich dishes. This research builds off our first guide for food service, now with industry experience and insights from nearly 350 academic trials.
Prevalence of Toxoplasma gondii infection in domestic animals in District Ban...Open Access Research Paper
Toxoplasma gondii is an intracellular zoonotic protozoan parasite, infect both humans and animals population worldwide. It can also cause abortion and inborn disease in humans and livestock population. In the present study total of 313 domestic animals were screened for Toxoplasma gondii infection. Of which 45 cows, 55 buffalos, 68 goats, 60 sheep and 85 shaver chicken were tested. Among these 40 (88.88%) cows were negative and 05 (11.12%) were positive. Similarly 55 (92.72%) buffalos were negative and 04 (07.28%) were positive. In goats 68 (98.52%) were negative and 01 (01.48%) was recorded positive. In sheep and shaver chicken the infection were not recorded.
UNDERSTANDING WHAT GREEN WASHING IS!.pdfJulietMogola
Many companies today use green washing to lure the public into thinking they are conserving the environment but in real sense they are doing more harm. There have been such several cases from very big companies here in Kenya and also globally. This ranges from various sectors from manufacturing and goes to consumer products. Educating people on greenwashing will enable people to make better choices based on their analysis and not on what they see on marketing sites.
Characterization and the Kinetics of drying at the drying oven and with micro...Open Access Research Paper
The objective of this work is to contribute to valorization de Nephelium lappaceum by the characterization of kinetics of drying of seeds of Nephelium lappaceum. The seeds were dehydrated until a constant mass respectively in a drying oven and a microwawe oven. The temperatures and the powers of drying are respectively: 50, 60 and 70°C and 140, 280 and 420 W. The results show that the curves of drying of seeds of Nephelium lappaceum do not present a phase of constant kinetics. The coefficients of diffusion vary between 2.09.10-8 to 2.98. 10-8m-2/s in the interval of 50°C at 70°C and between 4.83×10-07 at 9.04×10-07 m-8/s for the powers going of 140 W with 420 W the relation between Arrhenius and a value of energy of activation of 16.49 kJ. mol-1 expressed the effect of the temperature on effective diffusivity.
Climate Change All over the World .pptxsairaanwer024
Climate change refers to significant and lasting changes in the average weather patterns over periods ranging from decades to millions of years. It encompasses both global warming driven by human emissions of greenhouse gases and the resulting large-scale shifts in weather patterns. While climate change is a natural phenomenon, human activities, particularly since the Industrial Revolution, have accelerated its pace and intensity
Artificial Reefs by Kuddle Life Foundation - May 2024punit537210
Situated in Pondicherry, India, Kuddle Life Foundation is a charitable, non-profit and non-governmental organization (NGO) dedicated to improving the living standards of coastal communities and simultaneously placing a strong emphasis on the protection of marine ecosystems.
One of the key areas we work in is Artificial Reefs. This presentation captures our journey so far and our learnings. We hope you get as excited about marine conservation and artificial reefs as we are.
Please visit our website: https://kuddlelife.org
Our Instagram channel:
@kuddlelifefoundation
Our Linkedin Page:
https://www.linkedin.com/company/kuddlelifefoundation/
and write to us if you have any questions:
info@kuddlelife.org
"Understanding the Carbon Cycle: Processes, Human Impacts, and Strategies for...MMariSelvam4
The carbon cycle is a critical component of Earth's environmental system, governing the movement and transformation of carbon through various reservoirs, including the atmosphere, oceans, soil, and living organisms. This complex cycle involves several key processes such as photosynthesis, respiration, decomposition, and carbon sequestration, each contributing to the regulation of carbon levels on the planet.
Human activities, particularly fossil fuel combustion and deforestation, have significantly altered the natural carbon cycle, leading to increased atmospheric carbon dioxide concentrations and driving climate change. Understanding the intricacies of the carbon cycle is essential for assessing the impacts of these changes and developing effective mitigation strategies.
By studying the carbon cycle, scientists can identify carbon sources and sinks, measure carbon fluxes, and predict future trends. This knowledge is crucial for crafting policies aimed at reducing carbon emissions, enhancing carbon storage, and promoting sustainable practices. The carbon cycle's interplay with climate systems, ecosystems, and human activities underscores its importance in maintaining a stable and healthy planet.
In-depth exploration of the carbon cycle reveals the delicate balance required to sustain life and the urgent need to address anthropogenic influences. Through research, education, and policy, we can work towards restoring equilibrium in the carbon cycle and ensuring a sustainable future for generations to come.
2. BiodegradationBiodegradation
Biodegradation is nature's way of recycling wastes or breaking down organic matter
into nutrients that can be used by other organisms. "Degradation" means decay and
“Bio" means that the decay is carried out by a huge assortment of bacteria, fungi,
insects, worms and other organisms that eat dead material and recycle it into new
forms.
The US EPA defines biodegradation as “A process by which microorganisms
transform or alter (through metabolic or enzymatic action) the structure of chemicals
introduced into the environment”.
Biodegradation is a process by which organic materials are changed through
chemical processes from complex molecules into simpler molecules.
Example: Banana peel being reduced from cellulose to H2O, CO2 and humus in a
compost pile.
Biodegradation is a waste management & recycling system that degrades everything
from yard waste to crude oil. This process helps to keep our planet clean and
healthy.
3. Where does biodegradation take place?
Biodegradation can take place with O2 (aerobically) or without O2
(anaerobically). Aerobic respiration is a process in which micro-
organisms such as bacteria and fungi convert carbon into energy and
produce CO2, H2O and humus (biomass) as waste products.
Aerobic respiration is a fast and efficient source of energy and an
effective means to biodegrade waste matter.
Anaerobic biodegradation, called anaerobic fermentation, is a
complex process by which microorganisms convert carbon into
energy and produce CO2, Methane and humus as waste products.
4. Composting is a good example of aerobic biodegradation, which is
widely used to divert municipal wastes such as yard trimmings from
landfills. Some cities have large industrial composters that are able
to accept food wastes and some paper and plastic items.
Anaerobic biodegradation is often used to treat municipal sewage, as
it is extremely efficient at reducing known pathogens in human and
animal waste. This process produces methane as a waste gas this is
captured and utilized for energy production.
Example
5. Type Of Biodegradation
There are basically two generalized categories of biodegradation.
Mineralization, also referred to as bio-mineralization. Mineralization
is the process by which microorganisms work on organic compounds
and by a chemical process, reduce them to inorganic material such as
H2O, CO2 and also possibly other such inorganic compounds.
Mineralization involves total degradation of the organic matter.
6. The second category is called biotransformation. Biotransformation
essentially differs from mineralization in that the organic matter is
not degraded totally. While a part of it is degraded, another part is
converted into other smaller chain organic compounds.
This raises two possibilities: The converted smaller chain organic
compounds may be either toxic or non toxic. In the case of the
pesticide Dichloro Diphenyl Trichloroethane (DDT), the
biotransformation yields an even more toxic compound. Another
example of biotransformation is the fermentation process, in which
sugar, a long chain organic compound, is transformed into ethanol.
7. Conventional Methods Of Remediation
Dig up and remove it to a landfill
Risk of excavation, handling and transport of hazardous material Very
expensive to find another land to finally dispose these materials
Cap and Contain
Maintain it in the same land but isolate it, Only an interim solution
Requires monitoring and maintenance of isolation barriers for a long
time.
Products are not converted into harmless products. Stay as a threat!
Is there a better approach?
8. Better Approaches
Better approaches are; To destroy them completely, if possible OR
Transform them in to harmless substances.
Methods already in use;
High temperature incineration, Chemical decomposition like dechlorination, UV
oxidation
But, are they effective?
Yes, But only upto some extent
Drawbacks
Technological complexity, expensive for small scale application, Lack of public
acceptance, especially in case incineration as more toxic compounds are generates,
materials may be released from imperfect incineration- Cause undesirable
imbalance in the atmosphere. Ex. Ozone depletion, Fall back on earth and pollute
some other environment, Dioxin production due to burning of plastics – leads to
cancer and may increase exposure to contaminants, for both workers and nearby
residents.
9. What is Bioremediation?
Using subsurface microorganisms to transform hazardous
contaminants into relatively harmless byproducts, such as ethene and
water.
Bioremediation is the intentional use of biological degradation
procedures to remove or reduce the concentration of environmental
pollutants from sites where they have been released.
The concentrations of pollutants are reduced to levels, acceptable to
site owners and/or regulatory agencies.
11. In-Situ Bioremediation
In situ bioremediation involves the treatment of the contamination on
site. In case of soil contamination, in-situ bioremediation involves
the addition of mineral nutrients.
These nutrients increase the degradation ability of the
microorganisms that are already present in the soil.
Sometimes new microorganisms are added to the contaminated area.
Microorganisms can sometimes be genetically engineered to degrade
specific contaminants. An example of a microorganism that has been
genetically engineered is Pseudomonas fluorescens HK44. These
genetically engineered microorganisms can be designed for the
conditions at the site.
12. Approaches
Which approach is taken, depends upon the relationship between
the type of contamination and the type(s) of microorganisms
already present at the contamination site.
For example; if the microorganisms already present are appropriate
to break down the type of contamination, we only need to "feed"
these microorganisms by the addition of fertilizers, nutrients,
oxygen, phosphorus, etc.
13. Methods for supplying O2
Two methods are used for supplying O2 to the microorganisms.
Bioventing: This consists of blowing air from the atmosphere into the
contaminated soil.
First, injection wells must be dug into the contaminated soil. How
many wells, how close together they go, how deep they are dug, all
depends on the factors affecting the rate of degradation (type of
contamination, type of soil, nutrient levels, concentration of
contaminants). Once all of the injection wells are dug, an air blower
is used to control the supply of air to the microorganisms.
These injection wells can also be used to add nitrogen and
phosphorus, maximizing the rate of degradation.
14. Hydrogen Peroxide (H2O2) Injection: In cases where the
contamination has already reached the groundwater,
bioventing will not be very successful so H2O2 injection is
used.
Its function is similar to bioventing, using the H2O2
instead of air blowers to deliver oxygen to the
microorganisms. If the soil is shallow (the groundwater is
fairly close to the surface) the H2O2 can be administered
through sprinkler systems.
If the groundwater is fairly deep beneath the surface,
injection wells are used.
15. Ex Situ Bioremediation
Ex situ bioremediation involves the physical extraction of the
contaminated media to another location for treatment. If the
contaminants are just in the soil, the contaminated soil is excavated
and transported for treatment. If the contamination has reached the
groundwater, it must be pumped and any contaminated soil must also
be removed.
There should ideally be no remaining contaminants, but usually
a minimal amount of contaminants is remaining in the contaminated
site. If minimal contaminants do remain in the soil, they can likely
be broken down by the naturally occurring microorganisms already
present at the site.
16. Types Of Ex-Situ Bioremediation
Two main types of ex-situ bioremediation.
Solid Phase: Solid phase treatment consists of placing the excavated
materials into an above ground enclosure. Inside this enclosure, the
contaminated soil is spread over a treatment bed. This treatment bed
usually has some kind of built-in aeration system. Using this system,
cleanup crews are able to control the nutrients, moisture, heat, oxygen
and pH. This allows them to maximize the efficiency of the
bioremediation.
The soil can also be tilled like farmland, helping to provide oxygen
and enable additional aerobic biodegradation of the contamination.
Solid phase treatment is especially effective if the contaminants are
fuel hydrocarbons. However, it require a lot of space and sometimes it
cannot be used for that very reason.
17. Types of solid phase
bioremediation techniques
There are three solid phase bioremediation techniques.
They are:
Landfarming
Biopiling
Composting.
18. Landfarming
Landfarming is the most simple of the three types of solid phase
bioremediation.
It involves the excavation and spreading of the contaminated soils onto
a lined bed (pad). The soil is usually spread so that it is about 18 inches
thick all around.
The bed typically has a collection system, to collect any leachate that
may seep through the contaminated soil.
Leachate is a solution containing contaminants that are picked up
through the leaching of soil.
Generally, a high molecular weight, heavily nitrated and chlorinated
compounds tend to slow down the rate of contaminant degradation
19. The soil is tilled and turned over repeatedly to allow aeration.
Controlling the frequency of aeration enables the cleanup crews to
control the amount of oxygen that is involved in the degradation
process.
They also control the moisture content of the soil by irrigation and
spraying.
They are able to control the pH of the soil on the bed by adding
crushed limestone. This crushed limestone helps to form a buffer.
Usually, these beds are in an enclosure. This prevents any inclement
weather from affecting the degradation of the contaminants. It also
helps to contain any evaporated contaminants.
20. Biopiling
The contaminated soil is excavated and put into pills. These piles are
usually 2-3 m in height and are placed over an aeration system.
This system pulls air through piles of contaminated soil by means of a
vacuum pump. This movement of air not only provides O2 to the
microorganisms but also pulls some of the contaminants out of the soil as
it passes through soil.
Optimal bioremediation conditions are maintained by controlling
moisture and nutrient levels. Another form of control is the placement of
the piles into enclosures. This prevents unwanted weather changes and
helps to control any temperature changes.
These piles also require space but they do not need as much space as
landfarming. It is a short term technology that usually only operates for a
few weeks or a few months.
21. 3. Composting
Composting involves first the excavation of the contaminated soil
then a bulking agent is added to the contaminated soil, which is
known as compost material.
Bulking agents includes; hay, straw and corn cobs. These make it
much easier to maintain the maximum rate of degradation of the
contaminants.
The bulking agents allow the cleanup crews to easily control the
amount of water and air that are available to the microorganisms
involved in the degradation reaction.
There are three methods of composting that are used.
22. Static pile composting: This involves the formation of piles &
aerating them by means of a blower or a vacuum pump.
Mechanically agitated in-vessel composting: This involves the
compost material being placed in a vessel. Here, it undergoes mixing
and aeration.
Windrow composting: This method involves placing the compost
material into windrows (long piles as in a farmer's field). This
windrows are then mixed up thoroughly by tractors and other such
equipment.
Windrow composting is the most common method, because it is the most
cost-effective method.
23. Slurry Phase
The contaminated soil is excavated from the site as completely as
possible and put into large tanks known as bioreactors.
These bioreactors are used to mix the contaminants and
microorganisms.
This mixing process keeps the microorganisms in constant contact
with the contaminants. Water, oxygen and nutrients are also added.
Since the cleanup crews have complete control of the conditions in
the bioreactor, they can adjust things until they achieve the optimal
conditions for the degradation of the contaminants.
Since the degradation can be kept at or very close to optimal
conditions, it does not take very long time to break down the
contaminants.
24.
25. Advantage & Disadvantage
Advantages
In fact, slurry phase bioremediation is much faster than many other bioremediation
techniques.
It is very useful in cases in which the contaminants need to be broken down very
quickly.
Another advantage to slurry phase bioremediation is the fact that it can be a
permanent solution to the problem.
Disadvantage
The rate of treatment is limited by the size of the bioreactor. That is, if a small
bioreactor is being used, the rate of degradation will be very slow.
Additional treatment and disposal of the waste water is required. These additional
requirements increases the cost. They are part of the reason that slurry phase
bioremediation has a high operating cost as well as a fairly high capital cost.
26. Bioremediation makes effective better approach possible. Either by
destroying or render them harmless using natural biological activity.
Advantages
Relatively low cost
Low technology techniques
Generally has general public acceptance
Can often be carried out on site, no excavation, no transport.
Drawbacks
May not be effective on all contaminants
Time duration – relatively long
Expertise required to design and implement, although not technically
complex.
27. Biological oxygen demand (BOD)
BOD measure of the quantity of oxygen consumed by
microorganisms during the decomposition of organic matter.
BOD is the most commonly used parameter for determining the
oxygen demand on the receiving water of a municipal or industrial
discharge.
BOD can also be used to evaluate the efficiency of treatment
processes and is an indirect measure of biodegradable organic
compounds in water.
28. Classification
BOD can be Classified into two parts-
Carbonaceous oxygen demand
Nitrogenous oxygen demand.
Carbonaceous oxygen demand
Result of the breakdown of organic molecules such a cellulose and sugars into carbon
dioxide and water
Nitrogenous oxygen demand
Result of the breakdown of proteins.
Proteins contain sugars linked to nitrogen.
After the nitrogen is "broken off" a sugar molecule, it is usually in the form of
ammonia, which is readily converted to nitrate in the environment.
The conversion of ammonia to nitrate requires more than 4 times the amount of O2
as the conversion of an equal amount of sugar to CO2 and water.
29. Methods for BOD measurement
The rate of O2 uptake by microbes in sample at 20ºC and over a
period of 5 days in dark, can be measured by two widely used
methods
Dilution method
Manometric method
Dilution method
It is standard method conducted by placing portions of the sample
into bottles and then completely filled with dilution water which
contains a known amount of dissolved oxygen, freed of air bubbles,
sealed and allowed to stand for five days at a controlled temperature
of 20°C (68 °F) in the dark. After five-days, the remaining dissolved
oxygen is measured.
30. Manometric method
Measurement of BOD is easier.
Oxygen consumed is measured directly rather than with chemical
analysis.
Sample is kept in a sealed container fitted with a pressure sensor A
substance that absorbs CO2 (typically lithium hydroxide) is added in
the container above the sample level.
Stored in conditions identical to the dilution method
The pressure inside the container decreases because CO2 is absorbed.
From the drop of pressure, the sensor electronics computes and
displays the consumed quantity of oxygen.
Advantages:
Simplicity, direct reading of BOD value, continuous display of BOD
31. Chemical Oxygen Demand
In environmental chemistry, COD test is commonly used to
indirectly measure the amount of organic compounds in water.
COD test predicts the O2 requirement of the effluent and is used for
monitoring and control of discharges and for assessing treatment
plant performance.
Using potassium dichromate:
Potassium dichromate a strong oxidizing agent under acidic
conditions. Acidity is usually achieved by the addition of H2SO4.
In the process of oxidizing the organic substances, potassium
dichromate is reduced, forming Cr3+
.
The amount of Cr3+
is determined after oxidization is complete and is
used as an indirect measure of the organic contents of the water
sample.
32. BLANK: it is important that no outside organic material be accidentally added to
the sample to be measured
To control this, blank sample is used
Blank is created by adding all reagents (acid & oxidizing agent) to a volume of
distilled water
COD is measured for both and the two are compared
COD of blank - COD of sample
An excess amount of potassium dichromate (or any oxidizing agent) must be
present
Once oxidation is complete, the amount of excess potassium dichromate must be
measured to ensure that the amount of Cr3+
can be determined with accuracy
To do so, the excess potassium dichromate is titrated with ferrous ammonium
sulfate (FAS) until all of the excess oxidizing agent has been reduced to Cr3+
.
33. The oxidation-reduction indicator Ferroin is added during this
titration step
The Ferroin indicator changes color from blue-green to reddish-
brown, once dichromate is reduced
Calculations
COD = 8000(b-s)n / sample volume
where b is the volume of FAS used in the blank sample, s is the
volume of FAS in the original sample, and n is the normality of FAS
COD = (C/FW)(RMO)(32)
Where C = Concentration of oxidizable compound, FW = Formula
weight of the oxidizable compound, RMO = Ratio of the # of moles
of O2 to # of moles of oxidizable compound in their reaction to CO2,
water and ammonia