Microbiology Revision

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52 Terms

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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

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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.

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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.

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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

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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.

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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

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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

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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

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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).

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Ammonia Oxidising Bacteria Process : 1. Ammonia oxidation

  1. AMMONIA + OXYGEN + H -> HYDROXYLAMINE + WATER

    • Enzyme: Ammonia monooxygenase (cell membrane)

    • Oxygen source: Molecular O₂

    • No ATP produced

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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.

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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.

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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.

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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)

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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.

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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.

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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).

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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

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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

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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) 

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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

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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

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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

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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

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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

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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

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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

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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

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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

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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

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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

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Waterborne Pathogens - E. Coli

  • Gram neg rod, normal flora of GIT

  • Enterotoxigenic, enteropathogenic, enteroinvasive, enterohaemorrhagic 

  • faecal/oral transmission

  • Travellers diarrhea 

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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

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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

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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

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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

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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

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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

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Moisture Treatment

  • Drying = physically removing water or adding solutes such as salt/sugar

  • Prevent bacteria growth

  • Spoilage can still occur, especially from fungi

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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

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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

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Sulfites

  • Sulfur dioxide/salts used since ancient times

  • Used primarily in fruit/veg

  • Antimicrobial activity = pH

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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

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Radiation

  • Ionising radiation including X-rays, gamma rays

  • DNA destruction by ions/reactive molecules

  • Ionising radiation is effective means for reducing microbial contamination

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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 & acceptorsredox 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

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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

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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

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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 

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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

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Fermentation - Bread

  • Saccharomyces cerevisiae

  • Produce carbon dioxide that makes bread rise

  • Produce amylase to break down starch to more fermentable glucose

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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)

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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