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1. Aerobic vs Anaerobic Biodegradation
| Condition | Major Electron Acceptor | Typical End Products |
|---|---|---|
| Aerobic | O2 | CO2, H2O, biomass |
| Nitrate reduction | NO3− | N2, N2O and other reduced products |
| Sulfate reduction | SO42− | H2S / HS− |
| Methanogenesis | CO2 in hydrogenotrophic methanogenesis | CH4 |
2. Biodegradation vs Bioremediation
| Parameter | Biodegradation | Bioremediation |
|---|---|---|
| Meaning | Biological transformation or breakdown of compounds. | Application of biological processes to remove, transform or detoxify contaminants. |
| Occurrence | Can occur naturally or under engineered conditions. | Usually deliberately applied or managed for pollution control. |
| Purpose | May be part of natural nutrient/carbon cycling. | Primarily environmental cleanup or contaminant control. |
| Examples | Microbial degradation of hydrocarbons. | Biostimulation, bioaugmentation and treatment of contaminated soil/water. |
3. Electron-Acceptor Sequence
During progressive anaerobic respiration, microorganisms generally use electron acceptors according to their energetic favourability and availability. A commonly taught sequence is:
4. Recalcitrant Compounds
Recalcitrant compounds are substances that resist biological degradation because of their chemical structure, low bioavailability, toxicity, strong chemical bonds or other environmental factors.
(a) Resist microbial degradation
(b) Are always easily degraded
(c) Are exclusively synthetic
(d) Always act as nutrients
5. Co-metabolism
Co-metabolism occurs when a microorganism transforms a compound that does not provide sufficient energy or carbon for growth, while the microorganism is growing on another primary substrate.
(a) Transformation of a secondary compound during growth on a primary substrate, without significant growth benefit from the secondary compound
(b) Symbiotic degradation only
(c) Sequential degradation only
(d) Competitive inhibition
6. Aerobic Biodegradation of Aromatic Compounds
Aerobic degradation of aromatic compounds such as benzene commonly begins with oxygenation of the aromatic ring. Depending on the pathway, monooxygenases or dioxygenases may participate in the initial oxidation.
(a) Monooxygenases or dioxygenases
(b) Reductases only
(c) Hydrolases only
(d) Lyases only
7. Lignin Biodegradation
Lignin is a complex aromatic biopolymer and is particularly resistant to degradation. White-rot fungi are especially important lignin degraders.
Major ligninolytic enzymes include:
- Lignin peroxidase (LiP)
- Manganese peroxidase (MnP)
- Laccase
(a) White-rot fungi
(b) Algae only
(c) Viruses
(d) Protozoa only
8. Reductive Dechlorination
Under anaerobic conditions, chlorinated ethenes can undergo reductive dechlorination, in which chlorine atoms are removed and replaced by hydrogen.
where:
- PCE = Tetrachloroethene
- TCE = Trichloroethene
- DCE = Dichloroethene
- VC = Vinyl chloride
(a) Reductive dechlorination
(b) Oxidative hydroxylation
(c) Hydrolysis only
(d) Polymerization
9. Petroleum Hydrocarbon Biodegradation
Petroleum contains several classes of hydrocarbons and non-hydrocarbon fractions. In general, saturated hydrocarbons are often more readily biodegraded than many high-molecular-weight aromatic and polar fractions.
Resins and asphaltenes are generally among the more recalcitrant petroleum fractions.
(a) Resins and asphaltenes
(b) Low-molecular-weight alkanes
(c) Simple volatile hydrocarbons
(d) Methane
10. Plastic Biodegradation
(a) Some microorganisms can degrade or modify certain polymers under appropriate conditions, but biodegradability varies greatly among plastics.
(b) All plastics are rapidly degraded by ordinary soil bacteria.
(c) Ideonella sakaiensis is primarily known for polyethylene degradation.
(d) Plastic degradation never involves enzymes.
11. Mineralization
Mineralization refers to the conversion of organic compounds into simpler inorganic products through biological processes. The exact products depend on whether the environment is aerobic or anaerobic.
| Condition | Representative Products |
|---|---|
| Aerobic | CO2 + H2O + inorganic ions + biomass |
| Anaerobic | CO2, CH4, H2S and other reduced products, depending on the pathway |
(a) Biological conversion of organic compounds into simpler inorganic products and associated end products
(b) Adsorption of pollutants onto soil
(c) Physical evaporation of pollutants
(d) Polymerization of organic molecules
12. Methanogenesis
In hydrogenotrophic methanogenesis, carbon dioxide acts as an electron acceptor and is reduced to methane:
(a) CO2
(b) O2
(c) NO3−
(d) SO42−
13. Co-metabolic Degradation of TCE
Methanotrophs can transform trichloroethylene (TCE) co-metabolically. Methane serves as the primary growth substrate, while TCE transformation is associated with enzymes such as methane monooxygenase.
(a) Methane
(b) Glucose
(c) Lactate
(d) Ethanol
14. Biodegradation and Half-Life
For a first-order degradation process:
Therefore, a shorter half-life indicates a faster disappearance rate under the specified conditions.
(a) More rapidly biodegradable aerobically
(b) More rapidly biodegradable anaerobically
(c) Equally rapidly degraded
(d) Necessarily non-biodegradable
15. Important Exam Facts
| Topic | Key Fact |
|---|---|
| Biodegradation | Biological transformation/breakdown of compounds. |
| Bioremediation | Application of biological processes for contaminant treatment. |
| Aerobic mineralization | Commonly produces CO₂ and H₂O plus biomass/inorganic products. |
| Methanogenesis | Hydrogenotrophic pathway reduces CO₂ to CH₄. |
| Recalcitrance | Resistance to biological degradation. |
| Co-metabolism | Transformation of a secondary compound while growing on a primary substrate. |
| Benzene oxidation | Oxygenases such as monooxygenases/dioxygenases may initiate degradation. |
| Lignin | White-rot fungi are major degraders; LiP, MnP and laccase are important enzymes. |
| PCE degradation | PCE → TCE → DCE → VC → ethene can occur through reductive dechlorination. |
| PET | Ideonella sakaiensis is associated with PET degradation. |
| Petroleum recalcitrance | Resins and asphaltenes are among the more resistant fractions. |
| Half-life | For first-order degradation, shorter t1/2 means faster disappearance. |
16. Golden Revision Points
- Biodegradation ≠ always complete mineralization. Partial transformation may occur.
- Mineralization means conversion toward inorganic end products; the exact products depend on environmental conditions.
- O2 is generally the most energetically favourable terminal electron acceptor among the common respiratory acceptors.
- CO2 → CH4 is characteristic of hydrogenotrophic methanogenesis.
- White-rot fungi are especially important in lignin degradation.
- LiP + MnP + laccase are important ligninolytic enzymes.
- Co-metabolism means transformation of a compound that does not significantly support growth while another substrate supports growth.
- Ideonella sakaiensis → PET, not polyethylene.
- PCE → TCE → DCE → VC → ethene is associated with reductive dechlorination under suitable anaerobic conditions.
- Shorter half-life → faster disappearance under comparable conditions.