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Main aims of wastewater treatment
Ensure water quality to protect public health
Potential common source of infectious diseases
Prevent pollutants including chemicals from industry, endocrine disrupting chemicals, disinfection by-products
Eutrophication
biological process where a body of water becomes excessively enriched with nutrients, like nitrogen and phosphorous, causing a rapid increase in algae and aquatic plant growth, known as an algal bloom.
Activated Sludge
Pre-treatment: Screens & grit chambers remove debris; solids settle as primary sludge.
Aeration Tank: Microbes feed on suspended organic matter, form flocs; biological oxidation → CO₂, H₂O, microbial biomass.
Secondary Clarifier: Flocs settle → activated sludge; clarified effluent discharged.
Sludge Return: Part of settled sludge returned to aeration tank → maintains high microbial concentration.
Waste Sludge: Excess sludge removed → thickened, digested (anaerobic/aerobic), dewatered, then disposed or reused.
FLOCS
Filamentous bacteria matrix
Micro-colonies of bacteria and inorganic particles
Embedded in gel-like exocellular polymeric substances = glue holding it all together
Complex heterogenous structures
Floc structure and shape determines how successfully the solids phase separate from the liquid phase in secondary clarifier, ultimately determines success of the process
FISH = (Fluorescent in Situ Hybridization)
FISH uses fluorescent probes to identify specific genetic material in flocs.
Probes bind to DNA or RNA, visualising different bacteria and their arrangement.
Combined with PHA or polyP staining, it identifies phosphorus-removing bacteria in activated sludge.
Role of Protozoa
Heterotrophs → require organic carbon
Feed on bacteria → control bacterial numbers, reduce turbidity
Functions:
Predators: regulate bacterial populations in suspension & flocs
Indicators: type & abundance reflect system performance
Floc support: attach to flocs, secrete EPS → bind particles, improve sludge–water separation
How is N removed from wastewater in activated sludge process?
Inorganic forms of N = NH4 / NH3 = toxic to aquatic organisms, NH4 + NO3- contribute to ozone depletion + greenhouse gas effect
Need to be removed and converted to N2 :
Sequential process of NITRIFICATION, followed by DENITRIFICATIOn
NITRIFICATION
Process where reduced N compounds like NH3 are oxidised via nitrite -> nitrate to supply energy (ATP) for bacterial growth
Provides very little energy so these are slow growing organisms - need long residence time in the system
Bacteria that carry out ammonia oxidation are called = nitroso bacteria
Bacteria that oxidise nitrite to nitrate are called nitro bacteria
Ammonia-Oxidising Bacteria (AOB / Nitroso-bacteria) OVERVIEW
Traits: Gram–, aerobic chemolithoautotrophs (β- or γ-Proteobacteria).
Energy source: Oxidation of ammonia → Nitrite
Carbon source: Inorganic carbon (CO₂).
Occurs: In aerobic zones (aeration tanks).
Ammonia Oxidising Bacteria Process : 1. Ammonia oxidation
AMMONIA + OXYGEN + H -> HYDROXYLAMINE + WATER
Enzyme: Ammonia monooxygenase (cell membrane)
Oxygen source: Molecular O₂
No ATP produced
Ammonia Oxidising Bacteria Process : 2. Hydroxylamine oxidation
HYDROXYLAMINE + OXYGEN -> NITRITE + WATER + ATP
Enzyme: Hydroxylamine oxido-reductase (periplasm)
Oxygen source: Water
ATP produced
Energy released AOB usedto fix CO₂ → biomass.
2. Nitrite-Oxidising Bacteria (NOB / Nitro-bacteria)
Traits: Gram–, chemoautotrophic (α-, γ-, or δ-Proteobacteria).
Energy source: Oxidation of nitrite.
Carbon source: Inorganic CO₂ (can use organics when available).
Process:
NITROGEN DIOXIDE + OXYGEN → NITRATE
Enzyme: Nitrite oxido-reductase (cell membrane)
Low energy yield → slow growth
Complex ATP production system adapts to conditions.
3. Nitrifiers in Activated Sludge
Nitroso (AOB):
Form clusters of 100s of cells.
Community composition depends on treatment plant type and operating conditions.
Dominant species examples:
Nitrosomonas: Common; species diversity varies (1–5 spp./plant).
Nitrosococcus: Found in high-ammonia systems.
Nitrosospira: Rare in sludge (adapted to low-NH₃ environments).
Nitro (NOB):
Also form clusters, located adjacent to AOB clusters.
Syntrophy:
AOB produce nitrite (energy source for NOB).
NOB remove toxic nitrite from AOB cells.
Mutual benefit allows efficient nitrification.
DENITRIFICATION
Definition: Reduction of nitrate (NO₃⁻) and/or nitrite (NO₂⁻) to gaseous nitrogen compounds (NO, N₂O, N₂).
Sequence:
Nitrate -> Nitrite -> Nitric Oxide -> Nitrous Oxide -> Dinitrogen
Carried out by: Chemoorganoheterotrophic microbes via anaerobic respiration.
Products: Escape as gases to atmosphere.
Incomplete reduction (NO, N₂O) = air pollutants & greenhouse gases.
Complete reduction to N₂ = desired end product.
Anoxic zone: No O₂ but high NO₃⁻.
Organic carbon source: Needed as electron donor (e.g. methanol, acetate).
Energy source: From oxidation of organic carbon (heterotrophic process)
ANAMMOX (Anaerobic Ammonia Oxidation)
Reaction: Ammonia + Nitrite → Dinitrogen + H2O
Nitrite converted to dinitrogen gas using ammonia as the electron donor
No need for oxygen for denitrification, cheap
Carried out by: Planctomycetes (anaerobic, chemolithoautotrophs).
Location: Inside anammoxosome (special intracellular compartment).
Membrane: Contains unique ladderane lipids to protect from toxic intermediates (e.g. hydrazine
Nitritre oxidised → NO (by nitrite reductase).
Reduce NO + Oxidise Ammonia → Hydrazine (by hydrazine hydrolase).
Hydrazine Oxidised → N2 (by hydrazine oxidoreductase, similar to AOB enzyme).
No oxygen or organic carbon needed → cost-effective.
FISH = (Fluorescent in Situ Hybridization)
Technique that uses fluorescently labelled DNA/RNA probes that bind to cUses fluorescently labelled DNA/RNA probes that bind to rRNA (e.g. 16S rRNA).
Identifies and visualises specific microbes and their arrangement in flocs using fluorescence microscopy.
In Wastewater Treatment:
Detects nitrifiers, denitrifiers, filamentous and P-removing bacteria.
Tracks population changes and process health (e.g. sludge bulking).
Shows spatial organisation in flocs/biofilms (nitrifiers at surface, denitrifiers deeper).
Combined with PHA/polyP stains to identify phosphorus-removing microbes.
Microautoradiography (MAR)
Uses radioactively labelled substrates to show which microbes are metabolically active (taking up and using compounds).
In Wastewater Treatment:
Identifies active bacteria in situ.
Reveals which groups use C, N, or P compounds.
Confirms if microbes detected by FISH are functionally active (e.g. AOB/NOB fixing C during nitrification).
Models of alternating Anaerobic:Aerobic zones to achieve enhanced biological phosphorous reduction - CHEMICAL
(Lime or Alum)
Process: Chemicals react with dissolved phosphate → form insoluble compounds → removed with sludge.
Lime : Raises pH → calcium ions from lime react with P → insoluble calcium phosphate compound
Alum : Al ions act as coagulant binding with phosphate → insoluble aluminium phosphate complexes.
Advantages =
Disadvantages: Expensive, increases sludge volume and salinity, reduced bio-available P
Chemical P Reduction Advantages and Disadvantages
Advantages = low initial cost, dose flexibility, improved clarifier performance
Disadvantages: Expensive, increases sludge volume and salinity, reduced bio-available P
Models of alternating Anaerobic:Aerobic zones to achieve enhanced biological phosphorous reduction EBPR - MICROBIOLOGICAL ACTIVATED SLUDGE
1. Anaerobic Zone (no O₂ or NO₃⁻):
PAOs break down poly-P → energy → use VFAs (e.g. acetate) → PHB
Phosphate released into liquid.
Biomass stains for PHB, not poly-P.
2. Aerobic Zone (O₂ present):
PAOs oxidise stored PHB as carbon → energy + reducing power.
Uptake phosphate from liquid → rebuild poly-P.
Biomass stains for poly-P, not PHB.
P removed when sludge (biosolids) is wasted.
3. Anoxic Zone (optional):
Supports denitrification using stored carbon (PHB).
Key Microbe:
Candidatus Accumulibacter (Rhodocyclus-like)
EBFR Plants Often Fail
Glycogen Accumulating Organisms (GAOs)
outcompeted by non-PAO bacteria = GAO, for substrates in anaerobic zones.
Anaerobic: GAO Assimilate acetate → synthesize PHB.
Aerobic: Use PHB → regenerate glycogen, no poly-P accumulation.
Cannot be stained for glycogen in bacterial cells → not identifiable by microscopy.
Major GAOs:
Gammaproteobacteria: Candidatus Competibacter phosphatis, large oval cells
Alphaproteobacteria: Defluvicoccus-related, tetrad-forming
EBFR Advantages and Disadvantages
Advantages = lower long term costs, only biosolids produced, higher reduction of P achievable
Disadvantages = high initial costs, high energy costs, larger foot-print
Indicator Organisms
Not pathogenic but signal faecal contamination → possible pathogen presence
Qualities =
Not able to replicate freely in environment/correlate with pathogen presence
Be native to intestine of warm blooded animals
Present at higher conc than pathogens
Resistant to environmental stress
Rapidly detected by simple methods
Why are coliforms used to detect water contamination rather than directly quantifying pathogens?
Present in intestines of warm-blooded animals like many pathogens → indicate faecal contamination.
Pathogens are hard to detect: low numbers, intermittent, diverse, expensive.
Advantages of coliforms:
Fast, easy, reliable detection
Grow on simple media
Short incubation
Quantitative tests available
Non-pathogenic
Cryptosporidum
Detection:
Methods: FITC-antibody staining, PCR, cell culture
Limitations: expensive, cannot distinguish viable vs dead, or human-pathogenic vs non-pathogenic
Low infective dose: 10–30 cysts
Resistance & Treatment Challenges:
Difficult to remove via conventional treatment (coagulation, flocculation, sedimentation, filtration)
Chlorine-resistant: cysts have thick protective walls
Effective methods: boiling, UV, ozone, enhanced filtration
Therapy: no reliable drug; usually self-limiting in healthy adults
Nitazoxanide FDA-approved in US
Management: boil water alerts, shutdown of water treatment plant
Modern Control Measures:
Enhanced filtration: physical removal
UV disinfection: DNA damage
Ozone: chemical inactivation
Monitoring: FISH / immunofluorescence assays
Cryptosporidum Case Study 1 1994 North QLD
1994 Child Day Care Outbreak – North Qld
Event: November 1994, diarrhoea outbreak in nursery
Cases: 7/8 infants affected; Cryptosporidium cysts found in faeces
Exposure: Only boiled water; no pool or pets → transmission via faecal–oral route (hands, nappies, surfaces)
Features aiding transmission:
Low infectious dose (10 cysts)
Environmentally resistant cysts
Prolonged shedding
Control measures:
Exclude infected children
Strict hygiene (gloves, dedicated nappy areas)
Disinfect surfaces and toys
Duration: Diarrhoea ≥7 days
Cryptosporidium Case Study 2 Milwaukee 1993
400,000 illnesses caused, 70 deaths
Stool samples positive for cryptosporidum
Source not identified, possibly increased flows in rivers supplying lake michigan carrying cysts from livestock/human waste
Turbidity of source water had deteriorated
Treatment plant operation
Different Approaches to Disinfection - CHLORINE
Used extensively as primary + secondary disinfectants
Dissociates in water to form hypochlorous acid (very effective) and hypochlorite ion (less effective)
Effective against bacteria + giardia, moderately effective against viruses, not effective against cryptosporidium
Affected by turbidity (should be <1NTU), and pH
Different Approaches to Disinfection - ULTRAVIOLET
Increasingly used in tertiary/recycled water systems across Aus
UV light damages microbial DNA/RNA preventing replication
Effective against bacteria, viruses, giardia, cryptosporidium
Rapid treatment
Different Approaches to Disinfection - OZONE (O3)
Powerful oxidising gas generated on site using electrical discharge
Destroys cell walls, oxidises enzymes/nucleic acids
Effective against bacteria, giardia, viruses, cryptosporidium
More powerful oxidant than chlorine
Different Approaches to Disinfection - Ideal Disinfectant
Stable + easily measured residual
Produce no unacceptable by-products
Be easily generated, safe to handle, suitable for widespread use
Be cost effective
Waterborne Pathogens - E. Coli
Gram neg rod, normal flora of GIT
Enterotoxigenic, enteropathogenic, enteroinvasive, enterohaemorrhagic
faecal/oral transmission
Travellers diarrhea
Waterborne Pathogens - Legionella Pneumophila
Pneumonia + respiratory failure
Aerosol, aquatic reservoir
More resistant than E. coli to chlorine and other environment antagonists
Legionnaires disease
Fever, pneumonia, diarrhea, death
Waterborne Pathogens - Salmonella
All serotypes pathogenic to humans
Mild gastroenteritis to severe illness/death
S. typhi, S. paratyphi, S. enteritidis
Food-borne (beef/poultry) or faecal/oral
Typhoid fever = bacterial infection caused by ingested food/water contaminated with S. typhi
Headaches, nausea, loss of appetite, liver damage
DALY for Estimating Disease Impact
DALY = Disability Adjusted Life Year, estimates disease impact by combining years of healthy life lost from premature death and years of healthy life lost from disability
Food Poisoning vs Infection
Poisoning = disease from ingestion of foods, water, or products containing PREFORMED microbial toxins
Infection = ingestion of pathogen-contaminated food followed by growth of pathogen in host
Food Preservation Methods - Refrigeration
Low temp, slow microbial growth/spoilage
Many microorganisms particularly bacteria grow at fridge temp
In freezer slow growth still occurs in pockets of liquid water trapped within frozen food
-20 degrees = expensive, affects food appearance/consistency/taste
Heat Treatment
Reduce bacteria load, sterilise food products
Useful for liquids and high moisture foods
Pasteurisation = not sterilise liquid but reduce microbial number and eliminate pathogens
UHT = Ultra High Temp processing, almost sterilise foods
Canning = sterilise foods, require processing in sealed container at correct temp and time
Moisture Treatment
Drying = physically removing water or adding solutes such as salt/sugar
Prevent bacteria growth
Spoilage can still occur, especially from fungi
Food Preservation Methods - Chemicals
Antimicrobial chemicals = organic acids, nitrites, sulfites, sulfur dioxide, propionate, benzoate, antibiotics
Target cell wall, cell membrane, enzymes, genes
Enhance or preserve food texture, colour, freshness, flavour
Nitrites
Used in cured meat, bacon, hot dogs, ham
Nitrosomyoglobin makes cured meat pink
Inhibits c. botulinum, e.Coli
Antioxidant
Contribute to flavour, texture
Nitrite reacts with amines from meat protein -> nitrosamines (carcinogens)
Sodium erythrobate or isoascorbate inhibit nitrosamine formation
Sulfites
Sulfur dioxide/salts used since ancient times
Used primarily in fruit/veg
Antimicrobial activity = pH
Bacteriocins
Antimicrobial proteins made by bacteria
Bactericidal to a closely related group of bacteria
Do not kill bacteria that produce them
Nisin = LAB bacteriocin, nisin A/nisin Z, added to milk, cheese, sauces, salad dressings
Target cell membrane of sensitive bacteria, disrupt by making pores
Applications in foods = add LAB to produce bacteriocin or add bacteriocin
Radiation
Ionising radiation including X-rays, gamma rays
DNA destruction by ions/reactive molecules
Ionising radiation is effective means for reducing microbial contamination
Food preservation methods - Fermentation
Food preservation via microbial metabolism producing preservative chemicals
Destroys toxins & undesirable components
Types of Microbes:
Organic acid bacteria → lactic acid
Yeast → alcohol
Metabolism:
Anaerobic catabolism: organic compounds act as both electron donors & acceptors → redox balance without external electron acceptors
Homofermentative bacteria: produce only lactic acid
Heterofermentative bacteria: produce lactic acid + ethanol + CO₂ + acetic acid → flavour
Energy & Redox:
ATP/ADP: ATP = energy for cell; ADP → ATP stores energy
NAD⁺/NADH: coenzymes cycle electrons in redox reactions
Glycolysis:
Glucose → ATP + fermentation products
ATP = primary benefit for microbes; products = “waste” for them, but food/beverage products for humans
Other Fermentations:
Without glycolysis:
Clostridium ferments amino acids, purines, pyrimidines
Some anaerobes ferment aromatic compounds
Fermentation in Food Production - Swiss Cheese
Propionobacterium freudenreichii
Convert L-lactic acid to carbon dioxide -> holes
Convert citric acid to glutamic acid -> natural flavour enhancer
Fermentation in Food Production - Yoghurt
Streptococcus thermopulius, Lactobacillus bulgaricus
Concentrate milk by 25% using vacuum dehydrator
Add milk solids
Heat mixture to 90 degrees for 30-90 mins
Cool mixture to 45 degrees
Add starter culture, incubate for 3-5 hours
Fermentation in food production - Vegetables
Lactic acid bacteria (e.g. Lactobacillus brevis, plantarum) and yeasts
Mainly rely on indigenous microbiota
Salt = help creates anaerobic conditions, has selective effect on vegetables natural microbiota
Higher salt concentrations favour homofermentative species, accelerating fermentation
Fermentation in food production - Meat
Lactic acid bacteria (mainly Lactobacillus such as curvatus), coagulase negative cocci (staphylococcus such as xylosus, saprophyticus, equorum)
Fermented meats = dry and semidry fermented sausages, salami, ham
Nitrites added to inhibit clostridium botulinum, convert myblobin to nitrosomyoglobin to give pink colour of cured meat
Fermentable sugars added as meat does not contain much fermentable carbohydrate
Fermentation - Bread
Saccharomyces cerevisiae
Produce carbon dioxide that makes bread rise
Produce amylase to break down starch to more fermentable glucose
Fermentation - Beer
S. cerevisiae used for ales = grow on top of fermentation mix (top fermentation)
S. carlsbergensis used for lagers = settle at bottom (bottom fermentation)
Fermentation - Wine
S. cerevisae or Saccharomyces bayanus
White wine = 1-2 weeks at 18 degrees
Red wine = 1 week at 20-30 degrees to extract red colour
Fermentation products = ethanol, carbon dioxide, glycerol (smooths taste + imparts viscosity), esters and aldehydes (flavour compounds)
Aging = white wine usually none, red wine 1-2 years in barrel for flavour development