6 - Harnessing the Power of Microbes Flashcards

1
Q

Processes microbes are responsible for

A
  • Primary Production
  • Decomposition
  • Fixing nitrogen
  • Methane production
  • Industrial processes
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2
Q

Great Atlantic Sargassum belt

A
  • On land it decomposes and emits toxic gases
  • Decomposition processes are aerobic and anaerobic
  • Consumes O2 via aerobic respiration
  • Creates anoxic areas (O2 does not penetrate underneath)
  • Anaerobic decomposition generates H2S gas and NH3
  • Gases have human health impacts
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3
Q

Industrial processes microbes are involved in

A
  • Mining (assist in extracting metals from low grade ores)
  • Bioremediation (degrade environmental contaminants)
  • Wastewater treatment (render water safe)
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4
Q

Microbial leaching

A
  • Process of concentrating metals in low-grade ore using microbes (useful when concentrations of metal are low)
  • Minerals that are most readily oxidised are most amenable to microbial leaching (e.g. iron)
  • May also be used for uranium and gold bioleaching
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5
Q

Process for copper leaching

A
  1. Low grade ore is dumped in a large pile
  2. Dilute sulfuric acid (pH 2; rich in Fe3+) percolated through the pile
  3. Resulting liquid is rich in dissolved metals of interest
  4. Liquid transported to precipitation plant
  5. Metal is precipitated and purified
  6. Liquid recycled and returned to top of pile
  7. Rinse and repeat
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6
Q

Low grade ore

A

Rocks with low concentration of ore of interest

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7
Q

Two reactions that involve microbes in microbial leaching

A
  • Acidothiobacillus ferooxidans oxidises the sulfide in CuS to SO4
    2-, releases Cu2+
  • Spontaneous oxidation of sulfide in CuS by Fe3+ (Fe3+ is generated by the bacterial oxidation of Fe2+ by different bacteria)
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8
Q

Composition of microbial community changing with
temperature in microbial leaching

A
  • A. ferrooxidans: mesophile, outcompeted when >30°C
  • Leptospirillum ferrooxidans: mildly thermophilic ~40°C
  • Archaea (e.g. Sulfolobus) dominate at 60-80°C:
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9
Q

Acid mine drainage

A
  • Caused by same microbial processes as bioleaching, but where mining operations are not done correctly
  • Exposed sulfur rich ore + water + o2 + microbes
  • Results from oxidation of sulfide minerals (bacterial or spontaneous)
  • Problem in abandoned mines
  • Acidic water leaches into surrounding waterways
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10
Q

Two important reactions in acid mine drainage

A
  • initiator: development of acidic conditions (SO4
    2- + H+)
  • propagation: FeS2 is oxidised; leads to more H2
    SO4
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11
Q

Bioremediation

A
  • Use of microbes to clean up or detoxify contaminants (e.g. petrol, herbicide)
  • For natural materials, often achieved by stimulating activities of indigenous microorganisms
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12
Q

Three outcomes for the pollutant molecule in bioremediation

A
  • Minor change in molecule
  • Fragmentation
  • Complete mineralisation (organic –> inorganic)
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13
Q

Bioremediation of hydrocarbons

A
  • Organic pollutants
  • Microbes have already been exposed to, or have been in contact with these compounds
  • Have naturally evolved ways to degrade them
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14
Q

Petroleum degradation

A
  • Rich source of organic carbon
  • Can be completely degraded to CO2
  • Readily degraded by microbes where water and air are also present
  • Degraded in both oxic and anoxic conditions
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15
Q

Oxic degradation of petroleum

A
  • Oxygenase enzymes are important
  • Allows degradation on a reasonable time scale
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16
Q

Anoxic degradation of petroleum

A

Very slow rate

17
Q

Large petroleum spills

A
  • Volatile compounds evaporate
  • non-volatile compounds remain (80% or more are oxidised within one year)
  • Branched-chain and polycyclic hydrocarbons remain longer (difficult to biodegrade)
  • Oil that gets into sediments is degraded very slowly with long term environmental impacts
18
Q

Oil oxidising microbes

A
  • Develop rapidly on oil films and slicks
  • Bacteria attach to oil droplets and decompose the oil
  • Some bacteria grow only on hydrocarbons
  • Some bacteria produce detergent that breaks up oil
19
Q

Factors that influence the rate of degradation of petroleum

A
  • Temperature
  • Nutrients (N + P)
  • Predation
  • Release of biosurfactants
20
Q

Xenobiotics

A
  • Compounds not seen by microbes before
  • Still organic compounds (contain C), just completely artificial
  • Have chemical bonds that are “foreign” to microbes and therefore degraded very slowly if at all
  • Highly chlorinated compounds are the most resistant to microbial degradation
  • Some are co metabolised
21
Q

Examples of xenobiotics

A

Pesticides, dyes, chlorinated solvents, munitions, PCBs

22
Q

Co-metabolism

A
  • Two substrates degraded simultaneously
  • e.g. pesticide (secondary substrate) degraded only when organic matter (primary
    substrate) is present
  • Sometimes co-metabolism generates toxic metabolites which kills the microbes
23
Q

DDT

A
  • Highly chlorinated
  • Organochloride
  • Developed as a pesticide in the 1940s
  • Bioaccumulates
24
Q

Aerobic dechlorination

A

Catalysed by dioxygenase enzyme

25
Q

Reductive dehalogenation

A
  • Occurs in anoxic environment
  • Uses chlorinated organic compound as electron acceptor
  • Hydrogenolysis
  • Dihaloelimination
  • Yields organic compounds that can enter the citric acid cycle
26
Q

Hydrogenolysis

A

Halogen atom replaced by hydrogen

27
Q

Dihaloelimination

A

Two halogen atoms removed from adjacent carbon atoms, double bond formed between carbon atoms

28
Q

Plastics

A
  • Polymers, most xenobiotics
  • Polyethylene (plastic shopping bags) and polystyrene have carbon-carbon backbones (challenging to degrade)
29
Q

PET (pol(ethyleneterephthalate)

A
  • Contains ester bonds
  • Enzymes exist that degrade these bonds
30
Q

Ideonella sakaiensis

A
  • Gram negative organism discovered in 2016
  • Isolated from a consortium
  • Uses two enzymes to degrade PET (PETase, MHETase)
31
Q

Wastewater health risks

A
  • chemical intoxication / poisoning
  • Spread of disease (cholera, hepatitis A)
32
Q

Wastewater treatment uses

A
  • Physical and chemical methods, and
  • Industrial scale use of microbes
33
Q

BOD

A
  • Biological oxygen demand
  • Efficiency of nutrient removal expressed as BOD
  • Relative amount of dissolved O2 consumed by microbes to completely oxidise the organic matter
34
Q

COD

A
  • Chemical oxygen demand
  • Measures everything that can be chemically oxidised
35
Q

Primary wastewater treatment

A
  • Physical separation methods
  • Water passes through gates and screens
  • Solids allowed to settle and effluent from top removed for further treatment
36
Q

Anaerobic secondary treatment

A
  • Used for wastewater containing large quantities of
    insoluble organic matter (high BOD)
  • Anaerobes digest suspended insoluble solids into soluble
    components
  • These are fermented to fatty acids, H2, Co2
  • Fatty acids fermented by syntrophic bacteria to acetate, CO2, H2
  • Used by methanogens to make CH4, CO2
  • CH4 burned or used as power
37
Q

Aerobic secondary treatment

A
  • Used for wastewater with low levels of organic
    matter (low BOD)
  • Uses oxidative degradation reactions
  • Wastewater is mixed and aerated in large tanks
  • Masses of bacteria called flocs form in water
38
Q

Flocs

A
  • Oxidation of organic matter occurs on the floc as it is
    mixed and exposed to air
  • Wastewater then pumped into holding tank, flocs
    settle
  • Some of the settled flocs (activated sludge) returned to the aerator (as “inoculum”)
39
Q

Floc properties

A
  • Oxic, anoxic, anaerobic zones
  • Range of different microbial processes
  • Range of metabolites produced