Temperature changes decomposition rate
Decomposition
Decomposition is the breakdown of dead organic material and organic waste into simpler substances by decomposers.
- Decomposition depends on enzyme-controlled reactions in bacteria and fungi, so environmental conditions affect how quickly dead material is broken down.
- At low temperatures, enzyme and substrate molecules have less kinetic energy and fewer successful collisions occur each second.
- Digestion, respiration and microbial growth are slower, so decomposition proceeds slowly.
- As temperature increases towards a suitable optimum, molecules move faster and successful collisions become more frequent.
- More enzyme-substrate complexes form per second, increasing the rate of reactions involved in decomposition.
- Above a suitable temperature range, enzymes can denature, changing the shape of their active sites so substrates no longer fit effectively.
- High temperatures can also kill microbial cells, reducing the number of decomposers able to act on the material.
- Different microorganisms have different temperature tolerances, so a mixed decomposer community does not have one universal optimum.
Enzymes are denatured, not killed; low temperature usually reduces their activity without denaturing them.
Moisture and oxygen support decay
Aerobic conditions
Aerobic conditions are conditions in which oxygen is available.
Anaerobic conditions
Anaerobic conditions are conditions in which oxygen is absent.
- Microorganisms need water for cellular reactions and for dissolved substances to move to and from their cells.
- In dry material, fewer substances can dissolve and microbial growth is restricted, so decomposition is slower.
- Adding water to dry material can therefore increase decomposition when other conditions are suitable.
- Aerobic conditions contain oxygen, allowing decomposers to release energy through aerobic respiration.
- This energy supports cellular processes and growth, allowing a larger active microbial population to break down material.
- When material becomes waterlogged, water fills the air spaces and the supply of oxygen can become limited.
- Oxygen moves through water much more slowly than through air, so it may be used faster than it is replaced.
- Anaerobic conditions lack oxygen, although microorganisms capable of functioning without oxygen may still decompose material.
- Decomposition is often slower in oxygen-poor conditions, so partially decomposed material can accumulate.
- Increasing moisture therefore does not always increase decay: very dry conditions restrict activity, but waterlogging can restrict oxygen.
- Link each condition to its mechanism: temperature changes enzyme activity, water enables reactions and transport, and oxygen supports aerobic respiration.
- Use the range shown in the data when explaining a temperature trend rather than adding denaturation if the results never reach temperatures where it occurs.
Decay can be encouraged or slowed
- A compost heap decomposes plant material efficiently when it remains moist, has a suitable temperature and receives enough oxygen.
- Turning or mixing compost admits air, while avoiding excessive watering helps keep air spaces open.
- Respiration by decomposers releases energy that warms the heap, although excessive heating can reduce the activity of some microorganisms.
- Compost supplies organic material and mineral nutrients to soil as decomposition continues.
- Refrigeration slows microbial reactions, while freezing also reduces the availability of liquid water.
- Freezing does not reliably kill every microorganism, so microbial activity can increase again when food thaws.
- Drying reduces available water and therefore slows the reactions and growth needed for decay.
- Removing oxygen slows aerobic decay, but does not prevent every form of decomposition because some microorganisms can function anaerobically.
- In canning, heating kills microorganisms and subsequent sealing prevents new microorganisms entering; sealing alone does not make contaminated food safe.
Investigating leaf decomposition
- Aim: compare the loss of leaf material at different moisture levels while keeping temperature and access to air as similar as possible.
- Apparatus: use identical ventilated containers, fine-mesh bags, leaves of one species and similar age, soil from one mixed sample, a balance, measuring cylinders, labels, gloves and a teacher-controlled drying oven.
- Preparation: dry the leaves gently to constant mass, allow them to cool and weigh equal starting masses into labelled mesh bags.
- Constant mass: dry, cool and reweigh until consecutive measurements agree within the resolution of the balance, so changes in water content do not dominate the measurements.
- Set-up: place equal masses of well-mixed soil in identical containers and add measured water volumes to create low, medium and high moisture treatments without submerging the soil.
- Replication: prepare at least three separate containers for each moisture treatment and put the same number of identical leaf bags at the same depth in each container.
- Controls: keep leaf species, initial dry mass, leaf fragment size, soil source, temperature, mesh size, ventilation and duration the same.
- Moisture control: record the starting mass of each container and check regularly, replacing evaporated water to keep each treatment close to its intended moisture level.
- Sampling: retrieve a different bag from each container at each planned interval, such as after one, two and three weeks, so drying a sample does not interrupt decomposition of the remaining samples.
- Measurement: gently remove adhering soil without losing leaf fragments, dry the remaining leaf material to constant mass, cool it and record its dry mass.
- Processing: calculate dry mass lost and percentage mass lost for each bag, then calculate a mean for each treatment at each time.
- Presentation: plot time on the horizontal axis and mean percentage mass lost on the vertical axis, with separate labelled lines for the moisture treatments.
- Interpretation: compare mass loss over the same time interval, because greater loss during an equal interval indicates faster breakdown.
- Evaluation: some loss may result from soluble substances being washed out or fragments escaping through the mesh, so dry mass loss is an estimate rather than a direct measurement of microbial activity alone.
- Safety: wear gloves when handling soil or decaying material, wash hands afterwards, avoid inhaling dust and let the teacher handle heated equipment and disposal.
Microbial activity can change milk acidity
- Some bacteria use the sugar in milk and produce lactic acid, causing the milk’s pH\mathrm{pH}pH to decrease.
- A faster decrease in pH\mathrm{pH}pH over a fixed interval can indicate faster microbial activity when the starting conditions are controlled.
- This is an indirect indicator of decomposition and does not measure dry mass loss.
- Because pH\mathrm{pH}pH is a logarithmic scale, equal changes in pH\mathrm{pH}pH do not represent equal amounts of acid produced.
Investigating milk decomposition
- Aim: investigate how temperature affects the change in milk acidity caused by a teacher-approved, non-pathogenic lactic acid bacterial culture.
- Apparatus: use milk from one batch, the same food-grade bacterial starter, sterile tubes and caps, measuring pipettes, controlled-temperature water baths or incubators, thermometers and a calibrated pH\mathrm{pH}pH probe.
- Set-up: place equal milk volumes, such as 10 cm310\,\mathrm{cm^3}10cm3, in labelled tubes and allow them to reach the chosen temperatures before adding the starter.
- Temperature range: use teacher-approved school conditions, for example 10 ∘C10\,^{\circ}\mathrm{C}10∘C, 20 ∘C20\,^{\circ}\mathrm{C}20∘C and 25 ∘C25\,^{\circ}\mathrm{C}25∘C, and check the actual temperatures with thermometers.
- Starting the investigation: add the same measured volume and concentration of starter to each tube, mix in the same way and record the starting time.
- Controls: keep the milk source, milk volume, starting pH\mathrm{pH}pH, bacterial inoculum, vessel size, mixing and exposure to air the same.
- Control treatment: include uninoculated milk at each temperature to check whether changes also occur without the added starter.
- Replication: prepare at least three independent tubes for each temperature and each sampling time, using separate tubes so repeated opening does not alter later samples.
- Measurement: at fixed intervals selected in a pilot study, measure pH\mathrm{pH}pH using the same calibrated probe, rinsing it between samples to prevent carry-over.
- Recording: use a table with time and the individual pH\mathrm{pH}pH readings for each temperature, then calculate the mean of the repeats.
- Graph: plot time on the horizontal axis and mean pH\mathrm{pH}pH on the vertical axis, drawing a separate labelled line for each temperature.
- Interpretation: within a suitable temperature range, a steeper initial fall indicates faster acidification, which can be linked to faster enzyme-controlled activity.
- Evaluation: judge the measured trend within the temperature range tested and do not assume that the trend would continue indefinitely at higher temperatures.
- Safety: use only the approved starter, never taste the milk, minimise opening of cultures, disinfect the work area and leave culture disposal to the teacher.
Calculate rates and percentage loss
- Use the same time interval when comparing decomposition rates, and use dry mass when changing water content could affect the result.
- Calculate the loss using mass lost=initial dry mass−final dry mass\text{mass lost}=\text{initial dry mass}-\text{final dry mass}mass lost=initial dry mass−final dry mass.
- The mean rate is mean rate of mass loss=mass losttime taken\text{mean rate of mass loss}=\dfrac{\text{mass lost}}{\text{time taken}}mean rate of mass loss=time takenmass lost.
- If mass is measured in grams and time in days, report the rate in g day−1\mathrm{g\,day^{-1}}gday−1.
- To compare samples with different starting masses, calculate percentage mass lost=mass lostinitial dry mass×100%\text{percentage mass lost}=\dfrac{\text{mass lost}}{\text{initial dry mass}}\times100\%percentage mass lost=initial dry massmass lost×100%.
- A mean rate over a whole investigation may hide changes during that period, so compare shorter intervals when the data allow this.
- A leaf sample decreases from 12.0 g12.0\,\mathrm{g}12.0g to 7.2 g7.2\,\mathrm{g}7.2g dry mass during 24 days24\,\text{days}24days.
- The dry mass lost is 12.0−7.2=4.8 g12.0-7.2=4.8\,\mathrm{g}12.0−7.2=4.8g.
- The mean rate of mass loss is 4.824=0.20 g day−1\dfrac{4.8}{24}=0.20\,\mathrm{g\,day^{-1}}244.8=0.20gday−1.
- The percentage mass lost is 4.812.0×100%=40%\dfrac{4.8}{12.0}\times100\%=40\%12.04.8×100%=40%.
- A second sample losing the same mass in half the time has twice the mean rate, not twice the percentage mass loss.
Interpret decomposition results
- On a graph of mass remaining against time, a more steeply falling line indicates faster mass loss.
- On a graph of mass lost against time, a more steeply rising line indicates faster mass loss.
- A curve that becomes less steep shows that the rate is slowing, which may happen as the more easily decomposed material is used up.
- Use repeat measurements to calculate a mean and inspect their spread before deciding that a small difference between treatments is convincing.
- Check unusual results against the method and repeat the measurement where possible rather than deleting them simply because they do not match the expected pattern.
- A conclusion should identify the observed relationship and support it with comparable values, followed by the biological explanation that fits the tested conditions.
- Why does increasing temperature initially speed up decomposition?
- Why can waterlogging slow decay?
- What does anaerobic mean?
- Why should leaf samples be dried to constant mass?
- Why does a fall in milk pH\mathrm{pH}pH provide evidence of microbial activity?