Not degradable/Recalcitrant (Uranium, Mercury, DDT)
Remediate
To solve a problem
To right a wrong
Bio
Living organisms
Bio-Remediate
To use biological organisms to solve an environmental problem
Steps in the degradation of organic wastes
Minor change in a molecule
Fragmentation
Mineralization
Factors affecting bioremediation
Energy source
Electron acceptor
Moisture
pH
Nutrients
Temperature
Absence of toxicity
Removal of metabolites
Absence of competitive organisms
Procaryotic and eucaryotic cells
The most important groups to bioremediation are bacteria and fungi
Types of cells
Procaryotic
Eucaryotic
Organisms
Bacteria
Blue-green bacteria or cyanobacteria
Plants
Animals
Rotifers
Protozoa
Fungi
Most algae
Aerobic
Where oxygen in some form is added to the treatment environment
Anaerobic
Where nitrate, iron, or other electron acceptor is added to the treatment environment
Aerobic conditions
Molecular oxygen provides the electron acceptor for the oxidation of organic compounds
Organic carbon is used for energy and growth and this includes methane but not carbon dioxide
Anaerobic conditions
Anaerobic bacteria live and grow in the presence of reduced compounds and with either the total absence of molecular oxygen or its greatly reduced concentration
Compounds which can serve as terminal electron acceptors for anaerobes are: carbon dioxide, nitrate, sulfate, iron, humates and glucose (producing lactic acid and ethanol)
Cometabolism
The transformation of a non-growth compound when an organism is growing on another substrate and deriving its carbon and energy from the second substrate. The first compound is "accidentally" transformed and provides no benefit to the organism.
Types of compounds that can be treated biologically
Petroleum Hydrocarbons (Gasoline, Diesel Fuel, Gasoline Additives such as MTBE)
Inorganics via Reduction to a Lower Valence Causing Precipitation (Uranium, Technicium, Sulfur and Sulfuric Acid, Ammonia or Nitrate/Nitrite)
Microorganisms destroy organic contaminants in the course of using the chemicals for their own growth and reproduction
For degradation it is necessary that bacteria and the contaminants be in contact
The availability of contaminants is necessary for degradation
Types of in situ bioremediation
Intrinsic bioremediation
Accelerated bioremediation
Intrinsic bioremediation
Uses microorganisms already present in the environment to biodegrade harmful contaminants. No human intervention involved.
Accelerated bioremediation
Substrate or nutrients are added to the environment to help break down the toxic spill by making the microorganisms grow more rapidly. Microorganisms are usually indigenous, but occasionally very efficient ones are additionally added.
Biosparging
Involves the injectionofairunderpressurebelowthewatertabletoincrease groundwater oxygen concentrations and enhance the rate of biological degradation of contaminants by naturally occurring bacteria. Increases the mixing in the saturated zone and thereby increases the contact between soil and groundwater.
Bioventing
The most common in situ treatment and involves supplying air and nutrients through wells to contaminated soil to stimulate the indigenous bacteria.
Types of ex situ bioremediation
Land farming
Composting
Biopiles
Bioreactors
Anaerobic processes
Types of phytoremediation
Phytoextraction or phytoaccumulation
Phytodegradation or phytotransformation
Phytostabilization
Rhizodegradation
Rhizofiltration
Bioaugmentation
The addition of naturally occurring microbes to sites. Sites can be treated with high concentrations of specific microbes. Costs little money, time and disruption. Simple testing done for biocompatibility and biodegradation efficiency.
Biostimulation
The use of indigenous microbes. The modification of the site to promote the growth of native microbes already present. Depends on necessary native microbial and organic material to be present. Costs little time and money. Testing appropriate microbes can be difficult and complex.
Accelerated bioremediation
Adding substrate or nutrients to the environment to help break down the toxic spill by making the microorganisms grow more rapidly
Microorganisms in accelerated bioremediation
Usually indigenous, but occasionally very efficient at degrading a certain contaminant are additionally added
Biosparging
Injection of air under pressure below the water table to increase groundwater oxygen concentrations and enhance the rate of biological degradation of contaminants by naturally occurring bacteria
Biosparging
Increases the mixing in the saturated zone and thereby increases the contact between soil and groundwater