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Welcome to GCSE Edexcel Science revision.

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Unit S B 9: Ecosystems and material cycles.

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An individual organism is one living thing.

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A population is all the organisms of one species in a particular area at a particular time.

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A community consists of the populations of different species living in an area.

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An ecosystem includes that community and its non-living environment, including interactions between them.

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A habitat is the place where an organism lives.

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Different species can share a habitat while using different resources.

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Organisms need resources such as food, water, space and suitable conditions.

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Plants also compete for light and mineral ions; animals may compete for food, mates and territory.

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Interdependence means organisms depend on others, for example for food, pollination or shelter.

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Changing one population can affect other species in the community.

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An ecosystem includes both biotic and abiotic components.

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Do not use population, community and ecosystem as interchangeable terms.

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Abiotic factors are non-living influences, including temperature, light intensity, water availability, soil conditions and pollutants.

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Biotic factors involve living organisms and their interactions, including predation, competition, disease and the availability of food organisms.

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Species are adapted to particular conditions.

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A substantial change in temperature, rainfall or other conditions can change survival, reproduction, abundance and distribution.

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Competition occurs when organisms need the same limited resource.

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Competition can occur within a species or between different species.

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In a simplified predator, prey cycle, prey numbers rise first, giving predators more food.

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Predator numbers may rise after a delay, increasing predation and reducing prey numbers; predator numbers may then fall.

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Real populations are also affected by other foods, disease, migration and environmental changes.

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Predator, prey cycles and food-web responses are not guaranteed to follow one fixed pattern.

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Food chains and webs show feeding relationships.

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An arrow goes from the organism eaten to the organism eating it, showing the direction of energy transfer in food.

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Producers, such as green plants, make biomass using photosynthesis.

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Primary consumers eat producers; secondary consumers eat primary consumers, and tertiary consumers feed further along a chain.

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A food web links several chains, so a consumer may have more than one food source.

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If one prey population falls, its predators may fall or switch to other prey, affecting those populations too.

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A simplified food web: a population change can affect several linked species.

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A change can have indirect effects: fewer predators may allow a prey population to rise, increasing pressure on the prey's food.

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Explain the links and qualify predictions using other relevant factors.

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A parasite benefits at its host's expense, often living on or inside it.

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For example, a flea feeds on a mammal's blood; harm to the host does not mean that it must die immediately.

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Mutualism benefits both partners.

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A pollinating bee gains nectar or pollen while helping a flowering plant reproduce.

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Legumes and bacteria in their root nodules can also be mutualistic: bacteria provide fixed nitrogen, while the plant supplies carbohydrates and a suitable habitat.

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Abundance describes how common a species is, measured using counts, density, frequency or percentage cover as appropriate.

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It is not always simply a total population count.

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A quadrat is a frame enclosing a known area.

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It is useful for sampling plants and animals that remain in place, rather than animals that quickly move into or out of the frame.

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For a representative area estimate, mark a study area and use random coordinates to choose quadrat positions.

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Choosing only convenient or visibly crowded patches introduces bias.

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Identify the species consistently, count individuals and use a consistent rule for plants touching the frame.

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Use percentage cover instead when distinct individuals cannot sensibly be counted.

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Repeat with enough non-overlapping samples distributed across the study area.

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Record quadrat size, locations and counts so the method can be evaluated.

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Density equals total count in sampled quadrats divided by total area sampled.

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Estimated population equals density times total suitable habitat area.

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For ten zero point two five square metre quadrats containing forty plants in total,

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sampled area equals two point five square metres and density equals sixteen plants per square metre.

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Across a representative one hundred square metre area, the estimated population is one thousand six hundred.

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Use the total sampled area, not just the area of one quadrat.

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Alternatively, multiply the mean count per quadrat by the number of quadrat-sized areas in the habitat.

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Convert all areas to the same units before calculating.

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An estimate assumes samples represent the area.

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Patchiness, identification errors, too few quadrats or sampling only part of the habitat can reduce reliability; the estimate is not an exact census.

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A belt transect samples a strip across an environmental gradient, such as from shaded woodland to open grassland, using quadrats along a measured line.

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A continuous belt uses adjacent quadrats; an interrupted belt uses quadrats at specified intervals.

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Record distance along the transect and keep quadrat area and counting rules consistent.

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Record distribution across a gradient; this is different from random area sampling.

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Measure the relevant abiotic factor at sampling positions, for example light intensity or soil moisture, as well as species abundance or cover.

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Repeat transects where possible and compare patterns.

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Keep the measurement procedure consistent and consider weather, time of day and identification errors.

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A transect uses regular sampling positions (systematic sampling) to investigate how species distribution changes along an environmental gradient.

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It is not random sampling.

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Only use it to estimate the whole habitat if the sampled area represents that habitat.

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Plot abundance or cover against distance or a measured abiotic factor.

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A correlation can support an explanation but does not prove that one factor alone caused the pattern.

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Frequency ( percent) equals quadrats containing the species divided by total quadrats times 100.

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A species in 6 of 10 quadrats has 60 percent frequency; that does not mean it covers 60 percent of the ground.

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Work safely in the study area, avoid unnecessary disturbance and leave organisms and habitats intact.

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Record the method and environmental conditions so comparisons are meaningful.

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Biodiversity is the variety of living organisms in an area.

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More individuals of one species do not automatically mean greater biodiversity.

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Maintaining biodiversity protects species and interdependent relationships.

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Diverse ecosystems may be more resilient to disturbance, although outcomes depend on the particular species and event.

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Species can provide food, medicines and other useful materials, while ecosystems provide services such as pollination.

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Conservation also values species beyond their direct uses to people.

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Conservation can protect and restore habitats, reduce pollution, regulate harvesting and protect threatened species locally and globally.

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Reforestation restores tree cover and can provide habitat, store carbon and support biodiversity.

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Using suitable native species and varied habitats can be more beneficial than a single-species plantation.

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Captive breeding can increase numbers of threatened species for possible reintroduction.

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It needs genetic diversity, suitable habitat and management of the original threats to support long-term success.

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Controlling an invasive population, sometimes including culling, may protect native species.

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Evaluate effectiveness, animal welfare, unintended effects and alternatives rather than assuming that killing competitors is always beneficial.

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Overfishing can reduce wild fish populations and disrupt food webs.

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Fish farming can provide food and may reduce some harvesting pressure on wild stocks, depending on the farming system and feed sources.

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High stocking density can increase stress and disease transmission.

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Waste and uneaten feed can add nutrients to nearby water; these are possible impacts rather than proof that every farm is unhealthy.

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Escaped farmed fish may compete or breed with wild populations, and parasites or diseases can spread.

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Better siting, waste management and biosecurity can reduce risks.

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Medicines used in some systems can affect nearby organisms or contribute to antimicrobial-resistance concerns.

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Evaluate evidence and management practices rather than assuming every farm uses antibiotics routinely.

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A non-indigenous species has been introduced outside its native range.

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Some become invasive and harm native populations through competition, predation or disease; not every introduced species becomes invasive.

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An introduced predator or competitor can change several populations indirectly through a food web.

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Predict effects using the organism's interactions and the environmental context.

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Eutrophication can occur when excess nutrients, such as nitrates or phosphates from fertiliser runoff or sewage, enter water and stimulate rapid algal growth.

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A dense algal bloom reduces light reaching submerged plants, reducing photosynthesis and potentially causing plant death.

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Algae also eventually die and provide material for decomposition.

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Microorganisms decompose dead material and respire aerobically, using dissolved oxygen.

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Increased decomposition can greatly reduce oxygen concentration.

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Fish and other organisms requiring oxygen may die or leave when oxygen is too low.

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The main immediate problem is oxygen depletion, rather than carbon dioxide alone.

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Microbial respiration links decomposition to dissolved-oxygen loss.

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Some organisms can survive very low oxygen levels, so eutrophication changes the community rather than necessarily killing everything in the water.

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Reducing nutrient inputs through appropriate fertiliser use and sewage treatment helps prevention.

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Explain the sequence from nutrient addition to oxygen loss, rather than saying fertiliser directly poisons all fish.

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Carbon is present in carbohydrates, lipids, proteins and other components of biomass.

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Materials cycle between organisms and the non-living environment; energy flows through ecosystems and is not recycled in the same way.

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Photosynthesis takes carbon dioxide from air or water.

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Producers use its carbon atoms to make organic molecules such as glucose.

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Feeding transfers carbon-containing material from producers to consumers and between consumers.

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Carbon atoms are rearranged rather than created anew at each transfer.

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Plants, animals and microorganisms respire, returning carbon dioxide to the environment.

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Plants respire as well as photosynthesise.

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Death, fallen leaves and waste supply organic material to decomposers, including bacteria and fungi.

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Decomposition makes materials available again, while decomposer respiration releases carbon dioxide.

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Some organic carbon can be stored for long periods, for example in fossil fuels formed under particular conditions over geological time.

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This does not happen to all dead material.

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Main transfer pathways; dead material does not all become fossil fuel.

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Combustion of fossil fuels or biomass releases carbon dioxide.

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Deforestation can reduce carbon uptake and storage; reforestation can increase them.

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Water is needed for cell reactions and is a major component of cytoplasm and blood plasma.

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It moves between oceans, freshwater, the atmosphere, land and living organisms.

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Energy from the Sun drives evaporation from water surfaces.

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Transpiration from plants also transfers water vapour into the atmosphere.

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Water vapour cools and condenses into droplets or ice crystals that form clouds.

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Condensation changes gas to liquid; it is not the same process as rainfall.

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Precipitation returns water to the surface as rain, snow or other forms.

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Water may collect in lakes and rivers or return to the ocean.

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Some water soaks into soil and rock (infiltration) and moves underground as groundwater.

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Some flows over the land as surface runoff.

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Rivers and groundwater can return water to the sea.

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Water moves between stores through several processes; cloud formation and rainfall are different steps.

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Organisms take up water, and return it through processes including transpiration, respiration and excretion.

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Water is continuously redistributed rather than permanently used up by one organism.

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Nitrogen is needed for amino acids, proteins and D N A.

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Although nitrogen gas is abundant in air, most plants cannot use it directly and take up nitrogen compounds such as nitrate ions through their roots.

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Nitrogen-fixing bacteria convert nitrogen gas into ammonia or ammonium compounds.

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Fixation does not directly turn nitrogen gas into nitrate in a single step.

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Some nitrogen-fixing bacteria live freely in soil; others live in legume root nodules.

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The bacteria and the legume can both benefit from their association.

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Decomposers break down dead organisms and waste, releasing ammonium compounds into soil.

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This returns nitrogen from organic material to a form that can undergo further processing.

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Nitrifying bacteria convert ammonium compounds to nitrites and then nitrates under oxygenated conditions.

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Nitrates can be absorbed by plant roots and used to build organic molecules.

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Animals obtain nitrogen by eating plants or other animals, not by absorbing atmospheric nitrogen directly.

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Feeding transfers nitrogen-containing compounds through the community.

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Denitrifying bacteria can convert nitrates to nitrogen gas, returning nitrogen to the atmosphere, especially in oxygen-poor soil.

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Distinguish this from fixation and nitrification.

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Fixation, nitrification and denitrification are distinct processes; decomposition returns organic nitrogen to ammonium compounds.

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Fertilisers supply mineral nutrients, including nitrogen compounds that can increase plant growth when these nutrients are limiting.

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They do not supply the carbon in glucose produced by photosynthesis.

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Crop rotation changes the crop grown on a field in successive seasons.

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Including legumes can introduce biologically fixed nitrogen into the system.

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Nitrogen in legume residues can become available to later crops after decomposition and bacterial processing.

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Nitrogen is not instantly transferred from atmospheric gas to every neighbouring root.

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Returning suitable organic matter to soil can provide nutrients as decomposers act.

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Excess nutrient applications can still cause runoff and eutrophication.

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Evaluate farming practices using crop yield, soil conditions, fertiliser demand and environmental impacts.

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More fertiliser does not always produce more growth if another factor is limiting.

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Potable water is safe to drink and need not be chemically pure water.

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It must contain acceptably low levels of harmful dissolved substances and microorganisms.

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Freshwater treatment commonly removes solids by settling and filtration, then uses disinfection, such as chlorine, to reduce harmful microorganisms.

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Ordinary filtration does not remove all dissolved salts.

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Where freshwater is scarce, desalination removes dissolved salts from seawater.

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Distillation evaporates water and condenses the vapour, leaving most dissolved salts behind.

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Reverse osmosis is another desalination method: pressure pushes water through a suitable membrane while rejecting much of the dissolved salt.

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Desalination provides an additional water supply but requires energy and suitable management of concentrated brine.

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Compare these costs and impacts with local water availability.

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Different treatment steps have different purposes: filtration removes particles, disinfection reduces microorganisms and desalination removes salts.

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One step does not automatically replace all the others.

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Energy enters most ecosystems through photosynthesis.

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At each feeding level (trophic level), some energy transfers through respiration and movement and eventually heats the surroundings.

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Uneaten parts and waste do not become part of the next consumer’s biomass.

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Respiration, waste and uneaten material reduce transfer between each level.

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Pyramids of biomass usually become narrower at higher trophic levels because less biomass can be supported.

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Energy losses limit food-chain length; a pyramid of numbers can have a different shape if organisms differ greatly in size.

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Transfer efficiency ( percent) equals energy or biomass transferred to the next level divided by energy or biomass available at the previous level times 100.

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Compare matching measurements and time periods; biomass values often use dry mass to exclude variable water content.

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Food security means reliable access to enough suitable food.

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It can be reduced by population growth, greater meat and fish consumption, pests, pathogens, environmental changes and the costs of farming supplies such as fertiliser and feed.

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Growing crops for biofuels can compete with food production for land and water.

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Animal farming uses feed that could sometimes feed people directly; however, some grazing land cannot grow human food crops, so evaluate the particular system.

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Sustainable responses include reducing waste, maintaining soils and water supplies, managing pests and protecting fish stocks.

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A higher short-term yield alone does not show a system is sustainable.

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(Higher tier) Water low in oxygen can support pollution-tolerant bloodworms and sludgeworms,

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while freshwater shrimps and stonefly larvae are generally associated with cleaner,

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well-oxygenated water.

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Use a community survey and supporting measurements rather than treating one animal as conclusive proof.

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(Higher tier) Lichen communities can indicate air quality because species differ in sensitivity to pollutants.

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Blackspot fungus on roses is sensitive to sulfur dioxide,

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so its occurrence can support evidence of relatively low sulfur-dioxide pollution;

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weather and habitat also affect observations.

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Decomposers need suitable temperatures, water and often oxygen.

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Increasing temperature towards an optimum accelerates enzyme reactions,

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but very high temperatures can denature enzymes;

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freezing slows microbial activity rather than sterilising all food.

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Refrigeration, drying and limiting oxygen can slow decomposition in food.

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Some microbes can grow without oxygen, so removing oxygen alone is not a guarantee of safety.

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Composting benefits from moisture, warmth and air.

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Turning a heap improves oxygen supply; waterlogging fills air spaces and reduces aerobic decomposition.

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Microbial respiration can warm the heap.

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Calculate decomposition rate as mass lost divided by time, using matching units.

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Compare the same starting material and conditions, include repeats and consider water loss as a possible reason for apparent mass reduction.

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That completes Ecosystems and material cycles.

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Revisit the notes and test yourself on the revision website.
