Topic 5: Land

A soil system needs a stated boundary so stores, inputs, outputs and internal flows can be tracked.

Choose the depth and area first. Then label water, organic matter, minerals and organisms as stores; rainfall, litter and fertilizer as inputs; leaching, erosion and gases as outputs.

For a farm plot, fertilizer enters, nitrate leaches downward, carbon is stored in humus and CO₂ leaves through respiration.

Inputs and outputs change when depth, area or time window changes.

A system diagram without a boundary cannot show whether matter is entering, leaving or merely moving internally.

Soil combines mineral particles, organic matter, pore water and pore air; it is not solid rock or solids only.

Rock fragments provide structure; humus stores carbon and nutrients; pore water transports dissolved substances; pore air supplies gases to roots and microbes. Their proportions control function.

A compacted soil may contain the same minerals but less pore air and water movement, restricting roots.

A complete account of soil composition includes mineral particles, organic matter, pore water and pore air; texture alone describes only part of the system.

Pore space is part of the system even though it is not a solid ingredient.

A soil profile records long-term processes with depth: upper horizons are usually richer in organic matter, while deeper horizons show mineral movement, accumulation and parent material.

Interpret colour, texture, roots and translocation together. For a fair investigation, sample the B horizon from one managed garden or field and one natural ecosystem at comparable depth and sample size; compare texture, organic matter, NPK, aeration, drainage and water retention.

The mass lost after heating estimates burned organic matter. Use dry samples and the same procedure for both soils; the estimate does not by itself identify which carbon compounds were present.

Colour alone cannot identify a horizon process or carbon content; combine profile observations with measured texture and chemistry.

Soil inputs can be natural internal recycling, externally transported material or deliberate management additions.

Plant litter, dead animals, manure and decomposition add organic matter; weathering, wind- or water-borne deposition and precipitation add minerals or water; air, gases, humidity and solar energy also cross the boundary. Managed systems add compost, fertilizer, agrochemicals and irrigation, which can also increase salinity.

Compost added to a field is a managed carbon and nutrient input, while leaf fall is a natural seasonal input.

Rainfall and irrigation both add water, but irrigation is a human-controlled input whose timing, dissolved salts and allocation can alter the soil system.

‘Natural’ describes source, not whether the input is beneficial; excess natural sediment can still bury soil.

A soil output changes a store through plant uptake, leaching, gas exchange, evaporation, heat loss or erosion.

Name the material and destination: decomposition reduces dead organic matter and releases gases; roots absorb water and minerals; nitrate leaches to groundwater; CO2 diffuses to air; water evaporates; heat leaves the system; and wind or water can export particles. Component loss is different from removal of the whole soil by erosion.

Heavy rain carries nitrate below roots, so soil nitrogen falls while groundwater nitrate rises.

Erosion exports soil particles and their contents, whereas evaporation removes water without directly removing soil mass.

An output is not disappearance; trace where the material goes.

Transfers move water, particles or dissolved substances; name the material and destination before choosing infiltration, percolation, leaching, flow, mixing, aeration or erosion.

Infiltration moves water into soil; percolation moves it through horizons; leaching transports dissolved substances; groundwater flow moves water below; burrowing organisms mix particles; aeration exchanges gases; and erosion detaches and exports particles.

Rain infiltrates, nitrate leaches with percolating water, and a stream later carries the dissolved load away.

Soil particles detached and transported by wind or water undergo erosion, not dissolved-solute leaching.

Infiltration and percolation are stages of movement, not interchangeable labels.

A transformation changes form or chemical identity; decomposition, weathering, nutrient cycling and salinization are not simple movement.

Decomposition changes organic matter into smaller compounds; weathering changes parent material; microbes transform nutrient forms; and evaporation after irrigation can concentrate dissolved salts until solid salts accumulate, producing salinization.

Dead leaves become mineral nutrients through decomposition; the nitrogen is chemically transformed before plants absorb it.

Nitrate moving downward unchanged is a transfer; a transformation changes its chemical or physical form.

A process can include both movement and transformation; identify which step the question asks about.

A useful soil diagram links stores to named inputs, outputs, transfers and transformations for one material and boundary.

Start with water, organic carbon or mineral nutrients; draw arrows with direction and process. Check whether each arrow changes location, chemical form or both.

Leaf litter adds organic carbon and nitrogen to a soil store. Decomposition returns some carbon to the atmosphere as CO2 and mineralizes organic nitrogen into forms plants can absorb; infiltration, uptake and leaching link the same soil boundary to the water and nitrogen cycles.

An auditable arrow names the material, source, destination and process; unlabeled arrows cannot distinguish a transfer from a transformation.

A diagram is not complete because it has many arrows—every arrow needs a defined boundary and mechanism.

Soil provides anchorage, water storage, nutrients and a seed environment; atmospheric CO₂ supplies most plant carbon.

N, P and K support different functions, but fertilizer cannot replace light, water, roots or carbon fixation. Trace the resource to its source and process.

A seed bank and moist soil support germination, while leaves take CO₂ from air and photosynthesize biomass.

Fertilizer supplies selected mineral nutrients; most plant carbon enters as atmospheric CO2 fixed during photosynthesis, not from soil fertilizer.

Plant nutrition is not one soil input; distinguish water, minerals, anchorage and carbon.

Soil supports diverse organisms because pore size, depth, moisture, oxygen and food create different microhabitats.

Large pores drain and aerate; small pores retain water; surface litter supplies carbon; deeper layers differ in oxygen and chemistry. Microbes, fungi and animals partition these conditions.

A water-filled deep pore favours anaerobic microbes, while an oxygenated surface pore supports aerobic decomposers.

Compaction removes pore space and blocks oxygen and water pathways, reducing the range of soil microhabitats and niches.

Soil life is not evenly distributed; conditions vary over centimetres and depth.

Detritivores fragment litter; saprotrophs secrete enzymes and decompose it, releasing nutrients that plants can reuse.

Keep physical breakdown separate from chemical decomposition. The chain is litter → fragments → microbial breakdown → inorganic nutrients → plant uptake.

Earthworms shred leaves, fungi decompose the fragments, and nitrate released later enters plant roots.

Fungi and bacteria are saprotrophs that carry out extracellular chemical decomposition; detritivores such as earthworms mainly ingest and fragment litter.

Decomposition is not the same as eating litter; identify the chemical transformation step.

Sand feels gritty, silt smooth or floury, and clay sticky when wet; texture is the relative proportion of these particle sizes.

A settling test estimates proportions by how quickly particles fall. Humus modifies aggregation, water retention and nutrient behaviour but does not change the mineral-size label itself.

A jar with a thick slow-settling layer suggests more clay; gritty feel suggests sand-rich soil.

Colour may reflect humus or iron; texture requires particle feel or measured proportions.

Texture and structure are different: particle proportions do not fully describe aggregates and pore spaces.

Texture creates trade-offs: sand drains and aerates quickly, clay retains water and nutrients, and loam often balances both.

Clay’s surface area can retain ions and water but may drain slowly; sand can lose nutrients and dry rapidly. Humus and structure modify the prediction.

A sandy field may need frequent irrigation and nutrient management; a clay field may waterlog after heavy rain but retain more nutrients.

With comparable structure and compaction, sand-rich soil usually infiltrates water faster; clay-rich soil usually retains more water and nutrients but may drain and aerate poorly.

‘Clay is fertile’ is not universal; retention can coexist with poor aeration or waterlogging.

Compare carbon inputs and outputs: inputs greater than outputs make soil a sink, outputs greater make it a source, and equality is balance.

Compare inputs from litter and roots with losses through decomposition, respiration and erosion over a stated depth and period. Tropical forest soils often store little carbon because warm, moist conditions speed decomposition; tundra and waterlogged wetlands accumulate carbon because cold or low-oxygen conditions slow decay, while temperate grasslands add substantial carbon through dense roots.

A soil is a sink while inputs exceed outputs, a source while outputs exceed inputs, and a store describes the carbon stock present; the same soil can hold a large store yet currently be a source.

Classify sink or source from the net rate of stock change, not from dark colour or the absolute size of the carbon store.

A sink is defined by net rate, not by having a large carbon store.

Ice-free land is the broadest set; agricultural land is smaller; arable cropland is the subset suited to repeated crop cultivation.

About 70% of ice-free land is used for agriculture and forestry, but agricultural land is not all arable: steep slopes or nutrient-poor soils may support livestock while remaining unsuitable for repeated crop cultivation.

Population growth increases food demand while the land area remains finite, so expanding cropland can compete with forestry, grazing, settlements and ecosystem conservation.

Plan from the arable subset and its soil, slope and water limits—not from total ice-free land.

Agricultural land is not synonymous with arable cropland.

Marginalized groups become more vulnerable when land-use decisions remove the rights or access needed for food production, income, culture or recovery from shocks.

Named example—Indigenous peoples of the Brazilian Amazon: illegal land grabbing registers public land as private property. Indigenous people may then be evicted from land they use.

Eviction removes secure access and livelihood options; the local ESS textbook explains that displaced people may move into previously uncleared forest to survive, shifting pressure rather than resolving their needs.

Trace the chain: unequal decision power → loss of land rights → reduced livelihood security → greater food vulnerability and displacement.

Identity does not itself cause vulnerability; unequal rights, exposure and alternatives do. This case does not justify claims about every Indigenous group.

World agriculture produces enough food to feed about eight billion people, yet food insecurity persists because food is not distributed equitably and loss or waste occurs along the supply chain.

At least one-third of food production is estimated to be lost or wasted: losses can occur after harvest, during storage and distribution, while retail and consumers can discard edible food.

SDG 12 aims to halve per-capita global food waste at retail and consumer level and reduce losses along production and supply chains by 2030.

Diagnose production, loss, distribution and purchasing power separately; increasing harvest addresses only one possible bottleneck.

National food supply is not proof that every household can obtain it.

Climate and soil constrain feasible farming, while water access, cost and risk determine which feasible option is chosen.

Heat, rainfall, drainage, nutrients and rooting depth affect crop performance; irrigation can relax water limits but adds energy, cost and salinisation risk.

A dry grassland may support grazing; irrigation could enable wheat, but only if water cost and salt accumulation remain acceptable.

It describes a constraint, not the full decision; technology and economics modify the feasible set.

Environmental conditions constrain choices; they do not dictate one inevitable farming system.

Agricultural labels describe separate axes, so one farm can carry several labels at once.

A hydroponic tomato greenhouse selling to supermarkets may be commercial, intensive, irrigated, arable and monocultural at the same time; each label answers a different question.

Classify first, then evaluate how each choice changes economic, social and environmental sustainability.

Commercial does not automatically mean intensive, and subsistence does not automatically mean extensive.

Nomadic pastoralism moves livestock between grazing areas; slash-and-burn clears a plot for cultivation and relies on a sufficiently long fallow for vegetation and soil fertility to recover.

Both can sustain low-density populations when mobility, land area, stocking or cultivation pressure and recovery time remain in balance.

Fixed settlement, higher population density, restricted movement or shorter fallows concentrate pressure, so grazing vegetation or soil nutrients may be removed faster than they recover.

Compare current use rate, recovery rate, available area and population density for each system.

Traditional is not automatically sustainable or unsustainable; the present pressure-to-recovery balance determines the outcome.

The Green Revolution of the 1950s–1960s combined high-yield crop varieties with improved irrigation, synthetic fertilizers and pesticides; the yield change came from the package, not seed alone.

Potential benefits include higher yields and improved food security. Costs can include fossil-fuel dependence in fertilizer production, water demand, salinization, pollution, reduced crop diversity, unequal access to inputs and farmer debt.

A high-yield variety may perform poorly without reliable irrigation and nutrients; adding those inputs can raise production while also shifting environmental and financial risks to farmers and ecosystems.

Evaluate yield and food-security gains together with environmental, economic and sociocultural consequences, noting that the package did not reach every developing nation.

A yield increase does not by itself prove equitable food security or long-term sustainability.

Synthetic fertilizers supply soluble nutrients rapidly and can sustain high intensive-system productivity, but fertility also depends on organic matter, soil structure, water retention and biological cycling.

If a field is nutrient-poor, compacted and low in organic matter, soluble nitrogen may give a short response while compost, cover and biological methods address slower structural and cycling problems.

Match the input to the limiting process and judge nutrient supply, retention, timing and external losses together.

Natural inputs can also pollute when applied faster than crops and soils can retain their nutrients.

Choose soil conservation by identifying the degradation pathway and selecting a technique that interrupts it.

On a bare slope, contour cultivation and cover crops directly slow water and bind soil; lime would address acidity but not the main erosion pathway.

Explain the threat → technique → changed process → environmental, economic or sociocultural benefit.

One technique may solve several problems, but naming it without a mechanism does not show that it fits the site.

Feeding edible crops to livestock adds a trophic transfer, so much energy and biomass are lost before human consumption.

The trade-off depends on the feed and land: grazing animals on non-arable grassland differs from feeding human-edible grain on cropland.

Replacing grain-fed beef with beans can release cropland for direct food, whereas grazing marginal rangeland may not compete with crops in the same way.

Compare feed type, land opportunity cost, local ecology and the product’s nutrition.

A general trophic pattern is not a universal verdict on every food system.

A sustainable food strategy should reduce demand or waste, lower production emissions, or raise productivity without expanding agricultural land.

Cold storage can reduce post-harvest loss, but its net benefit depends on energy source and whether the saved food reaches people who can access it.

Locate the bottleneck, select a matching strategy, then evaluate new energy, nutrient, equity or biodiversity costs across the system.

Higher productivity alone is not sustainable if it expands inequity or shifts damage elsewhere.

Food security means physical and economic availability of enough safe, balanced food for every person to live an active and healthy life.

Test four linked dimensions: availability of supply, economic and physical access, nutritional utilization, and stability through seasonal, economic or conflict-related shocks.

A market can remain stocked while low-income households lose access as prices rise; another region may have adequate calories but insufficient dietary diversity for balanced nutrition.

Compare regions and households using supply, affordability, access, diet quality and exposure to shocks—not national production alone.

Food in a country does not guarantee food security for every household.