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Phases of growth
Lag phase, exponential phase, stationary phase, death phase
Stationary Phase
Equal rate of growth and death
Exponential Phase
High growth rate
Oligotrophic
low nutrient
Copiotrophic
High nutrient
Dormant cells
Viable but low growth rate
VBNC
sub-lethally injured but still viable, cannot be cultured.
Anaerobic metabolism
synthesis of cell constituents and metabolites
Catabolic metabolism
Breakdown of cell constituents and metabolites
Biodegradation
Breakdown of organic pollutants by microbes.
Mineralisation
Oxidation of contaminants into co2 and water.
5 Factors of microbial degradation
Enzyme, bioavailability, toxicity of pollutant, env. conditions, contaminant structure.
Xenobiotic
Foreign chemical substance in the bilogical system, includes pollutants, pharmaceuticals etc.
Momooxygenase
Catalyst for oxidation of methane and trichloroethane
Co-metabolism
Partial oxidation due to the action of non-specific enzyme.
Bioavailability
Portion of pollutant that a microbe can utilise.
Controlling factors of bioavailability
Sorption and solubility
Bioavailability
Can be enhanced by bio-surfactants.
Toxicity
Leads to disruption in membrane integrity.
QSAR Model
quantitative-structure activity relationship
C:N ratio of xenobiotic
20:1 or lower
C:N ratio for microbes
5:1 or 10:1
degree of branching
Less bioavailability
Vadose zone
Initial low population
High electronegativity
Difficult of biodegrade
Aliphatic
Industrial solvent waste and petroleum industry, less branching
Toxic for microbes
<C8
Waxy substances, low solubility, low bioavailability
>C16
Saturated aliphatics
Oil reserves underground do not degrade.
C10 to C18
Readily degraded in aerobic conditions.
Addition of fumarate
Degradation in molecules of high mol. weight (metabolic intermediate)
Mono and distributed aliphatics.
Degrade more easily under aerobic condition
Highly halogenated aliphatics
Degrade more easily under anaerobic condition.
Treatment of halogenated aliphatic hydrocarbon
Anaerobic to remove Cl, aerobic to degrade the HC.
Co-oxidation
oxidation of two compounds where degradation of one compound depends on the first.
Metals in the environment
Cannot be degraded easily, persistent, valance state and bioavailibility can be altered microbially, serious threat.
Three classes of metals
Metals, Metalloids, Heavy Metals
Toxicity of metals
depends on speciation
Metals in environment
Mining, nuclear processing, landfills, electronics etc.
4 was by with meals enter the environment
precipitation, sorption, bioavailability, volatility.
Total metal concentration
bioavailable + non-bioavailable fraction
Speciation of metals
Soil conditions and microbes
hH-Eh diagram
Shows the range in which chemical species are stable, whether mineral is at equilibrium with its surroundings or subject to chemical transformation.
Factors of speciation and bioavailability
Metal chemistry, CEC, redox potential, pH
High CEC
large no. of particles to bind to the particles’ surface, low toxicity.
Low CEC
Less no. of particles to bind to the particles’ surface, high toxicity.
Oxidising environment (800-0mV)
Soluble cations
Reducing environment (0- -400mV)
Metals will precipitate
High pH
Low bioavailability
low pH
Free ions, increase solubility, increase bioavailability.
Soil washing
Addition of acids and chelates like EDTA, moves metal contaminants into water
Excavation
Problem- this metal removal leads to exposure to oxygen.
Soil incineration
Problem- this metal removal destroys the soil.
Metal immobilisation
Increase pH and add organics
Organics in metal immobilisation
increase electrostatic attraction and sorption.