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AP Environmental Science The Living World: Ecosystems Guide

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Official unit weighting

The Living World: Ecosystems in the AP Environmental Science blueprint

College Board assigns Unit 1, The Living World: Ecosystems, 6–8% of AP Environmental Science multiple-choice questions. This range describes the multiple-choice section, not a percentage of the total exam score.

AP Environmental Science · Unit 1

The Living World: Ecosystems

Systems, evidence, calculations, and solutions
  • May 2027
  • Bluebook
  • Clean-room teaching
  • Read the evidence surface.
  • Trace the environmental mechanism.
  • Check units, scale, and claim scope.
APES-U1
Unit lesson

Unit 1: The Living World: Ecosystems

1.1 Introduction to Ecosystems

When studying The Living World: Ecosystems, biotic and abiotic parts of an ecosystem interact, and resource availability changes those interactions.

1.2 Terrestrial Biomes

1.3 Aquatic Biomes

1.4 The Carbon Cycle

1.5 The Nitrogen Cycle

1.6 The Phosphorus Cycle

1.7 The Hydrologic (Water) Cycle

1.8 Primary Productivity

1.9 Trophic Levels

1.10 Energy Flow and the 10% Rule

1.11 Food Chains and Food Webs

Vocabulary anchors

Introduction to Ecosystems; Terrestrial Biomes; Aquatic Biomes; The Carbon Cycle; The Nitrogen Cycle; The Phosphorus Cycle; The Hydrologic (Water) Cycle; Primary Productivity; Trophic Levels; Energy Flow and the 10% Rule; Food Chains and Food Webs are the official topic anchors used throughout this unit.

Evidence lab: Annual nitrogen budget for a 20-hectare reservoir

Annual nitrogen budget for a 20-hectare reservoir All values are metric tons of nitrogen per year. Storage change equals inputs minus outputs. Flow | Nitrogen (t/yr) Stream inflow | 18 Atmospheric deposition | 4 Fertilizer runoff | 10 Downstream export | 21 Harvested fish | 1

What is the annual increase in nitrogen stored in the reservoir?

10 t/yr — Inputs are 32 t/yr and measured outputs are 22 t/yr, leaving 10 t/yr in storage.

This adds inputs and outputs instead of subtracting them. This is the output total, not the storage change. The sign is reversed; inputs exceed outputs.

One stock-flow equation with labeled units.

Which process can convert nitrate in anoxic sediment to nitrogen gas?

Denitrification — Denitrifying microbes reduce nitrate and return nitrogen gas to the atmosphere under low-oxygen conditions.

Fixation moves atmospheric nitrogen into biologically available forms. Nitrification oxidizes ammonium and generally requires oxygen. Assimilation incorporates inorganic nitrogen into biomass rather than nitrogen gas.

Requires selecting the correct direction and redox context in the nitrogen cycle.

A wetland removes 60% of fertilizer-runoff nitrogen before it reaches the reservoir. What is the new storage increase if other flows stay constant?

4 t/yr — The wetland removes 6 t/yr, so fertilizer input becomes 4 t/yr and total inputs become 26 t/yr; 26-22=4.

This is the amount removed, not the remaining storage increase. This adds the removed amount to the original storage increase. This incorrectly subtracts the full fertilizer input plus the wetland removal.

Two-step percent reduction followed by a mass balance.

Which monitoring design best tests whether the wetland, rather than lower fertilizer use, caused the reduction?

Compare paired upstream and downstream nitrogen loads while recording fertilizer application during multiple storms. — Paired loads measure wetland removal and the fertilizer record addresses a competing source change.

Temperature does not quantify the nitrogen load or source change. Bird abundance is not a direct nitrogen-removal measure. Different size and source conditions confound the comparison.

Requires a load metric, repeated sampling, and control of a source confounder.

The wetland also emits 0.8 t/yr of nitrogen as nitrous oxide. Which conclusion is most defensible?

The wetland lowers aquatic nitrogen loading but introduces a greenhouse-gas tradeoff that should be compared on a common impact basis. — The two effects occur in different environmental pathways and require an explicit tradeoff analysis.

A tradeoff does not erase the measured water-quality benefit. Nitrous oxide can be an intermediate or product of denitrification. Species richness alone omits both nitrogen removal and greenhouse forcing.

Integrates mass balance, biogeochemical mechanism, and cross-medium tradeoff.

Evidence lab: Marsh food web and annual production

Marsh food web and annual production Arrows show energy transfer from food to consumer. Annual production is 90,000 kJ for cordgrass, 36,000 kJ for algae, 7,200 kJ for snails, 4,500 kJ for grasshoppers, 900 kJ for small fish, and 120 kJ for herons.

Which organisms are primary producers in the model?

Cordgrass and algae — Both convert external energy into biomass and appear at the base of feeding paths.

They consume producers and are primary consumers. They obtain energy by consuming other organisms. Only cordgrass is a producer in that pair.

Direct model classification with no calculation.

What is the transfer efficiency from algae production to snail production?

20% — 7,200 divided by 36,000 equals 0.20, or 20%.

This reverses the ratio. This subtracts the ratio from one. This treats the producer-to-consumer ratio as the efficiency.

Selects the correct numerator and denominator and converts to percent.

After a pesticide sharply reduces grasshoppers, which direct effect is most likely before other populations adjust?

Less energy is available to herons through the grasshopper pathway. — The arrow from grasshoppers to herons represents that direct energy route.

Cordgrass does not obtain energy from grasshoppers. No such link appears in the model. The model gives no direct grasshopper-to-algae dependence.

Requires reading arrow direction and limiting the inference to a direct path.

Heron production is 120 kJ. Why can it not be compared with 90,000 kJ of cordgrass as proof of one fixed trophic efficiency?

Herons receive energy through multiple paths with different intermediate transfers, so the two values do not define one adjacent-level efficiency. — A valid trophic efficiency comparison needs a specified source and adjacent transfer boundary.

Energy is transformed and dissipated, not created by consumers. They occupy very different feeding positions. Energy production can be measured in kilojoules over a stated interval.

Requires topology, denominator discipline, and rejection of a tempting endpoint ratio.

A restoration doubles algae production but leaves habitat for snails unchanged. Which prediction is most cautious?

Fish production may rise through direct algal feeding, but a proportional increase is not guaranteed because snail and other limits remain. — The web supports one additional input path while showing why a single-resource multiplier is insufficient.

Continue in the A+ teaching layer for the remaining evidence labs, figure, and final audit.

How it is assessed

How the AP Environmental Science assesses The Living World: Ecosystems

ItemWeight / countWhat it means
Official topic denominator11
Multiple choice80 questions in 90 minutes
Free response3 questions in 70 minutes
Calculation credit
AdministrationMay 2027
Worked examples

Energy transfer through two trophic steps

Read each question as it appears on the exam paper, choose your answer, then tap it to see the feedback.

Practice 1: Calculate energy through two trophic transfers

Q. Which approach applies each transfer efficiency to the energy entering that trophic step? Read the exam question below, choose one option, then tap it to check.
SECTION I · MULTIPLE CHOICE · QUESTION 1

Producers store 48,000 kJ. Twelve percent reaches herbivores, and 8% of herbivore energy reaches predators.

How much producer energy reaches the predators?

Select the best answer.

A. 48,000 kJ × 0.12 × 0.08 = 460.8 kJ

✅ Correct! 😊 The two successive retained fractions are multiplied. The result is smaller than either preceding energy stock and remains in kJ.

B. 48,000 kJ × 0.12 = 5,760 kJ

❌ Not quite 😭 This is the energy reaching herbivores after only the first transfer. It omits the predator transfer efficiency.

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C. 48,000 kJ × 0.80 = 38,400 kJ

❌ Not quite 😭 This treats the two percentages as though they combine into 80%. The stated efficiencies are sequential retained fractions, not digits to merge.

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D. 48,000 kJ × (0.12 + 0.08) + 45,696 kJ = 55,296 kJ

❌ Not quite 😭 Adding transfer efficiencies does not model two trophic steps, and the answer exceeds the stated producer energy. Both checks reveal an invalid setup.

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Full explanation
  • Step 1First transfer: 48,000 kJ × 0.12 = 5,760 kJ reaches herbivores.
  • Step 2Second transfer: 5,760 kJ × 0.08 = 460.8 kJ reaches predators.
  • Step 3Successive efficiencies multiply, and the energy measurement remains kJ.
Answer. A. 48,000 kJ × 0.12 × 0.08 = 460.8 kJ
Model answer. Answer: A — “460.8 kJ”
Scoring guideline. Calculation credit requires applying both transfer efficiencies sequentially, converting percentages to decimals, and checking that energy declines across trophic steps.

Practice 2: Analyze a reservoir nitrogen budget

Q. Which response closes both mass balances and tests the wetland against a competing change in fertilizer use? Read the exam question below, choose one option, then tap it to check.
SECTION II · FREE RESPONSE · QUESTION 210 points

Annual nitrogen inputs to a reservoir are 18 t/yr from streams, 4 t/yr from atmospheric deposition, and 10 t/yr from fertilizer runoff. Outputs are 21 t/yr downstream and 1 t/yr in harvested fish.

Calculate the annual storage change, recalculate it if a wetland removes 60% of fertilizer-runoff nitrogen, explain one nitrogen-removal process, and describe a monitoring design that isolates wetland performance.

Show your work.

A. Add inputs and outputs to obtain 54 t/yr, then sample only downstream once.

❌ Not quite 😭 Storage change is inputs minus outputs, not their sum. One downstream sample cannot separate wetland removal from changing source loads.

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B. Calculate 10 t/yr then 4 t/yr; compare repeated paired upstream and downstream loads while recording fertilizer application.

✅ Correct! 😊 Both balances use directed flows correctly. Paired load measurements and fertilizer records address wetland removal and the alternative explanation of lower source use.

C. Subtract the full 10 t/yr fertilizer input and its 6 t/yr removal from the original storage change.

❌ Not quite 😭 This counts the same fertilizer change twice. Sixty percent removal leaves 4 t/yr of fertilizer input rather than removing 16 t/yr.

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D. Use nitrification as the process that converts nitrate to nitrogen gas under anoxic conditions.

❌ Not quite 😭 Denitrification performs that low-oxygen conversion. Nitrification oxidizes ammonium and generally requires oxygen.

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Full explanation
  • Step 1Original inputs are 18 + 4 + 10 = 32 t/yr; outputs are 21 + 1 = 22 t/yr, so storage rises 10 t/yr.
  • Step 2The wetland removes 0.60 × 10 = 6 t/yr, leaving 4 t/yr; new storage increase is 26 − 22 = 4 t/yr.
  • Step 3In anoxic sediment, denitrifying microbes reduce nitrate and return nitrogen gas to the atmosphere.
  • Step 4Compare repeated flow-weighted upstream and downstream loads across storms while recording fertilizer application.
Answer. B. Calculate 10 t/yr then 4 t/yr; compare repeated paired upstream and downstream loads while recording fertilizer application.
Model solution. Inputs are 18 + 4 + 10 = 32 t/yr and outputs are 21 + 1 = 22 t/yr, so storage increases by 10 t/yr. The wetland removes 0.60 × 10 = 6 t/yr, leaving 4 t/yr of fertilizer nitrogen; new inputs are 26 t/yr and storage rises 4 t/yr. Denitrifying microbes can reduce nitrate to nitrogen gas in anoxic sediment. To isolate wetland performance, compare repeated flow-weighted upstream and downstream nitrogen loads during multiple storms while recording fertilizer application.
Scoring guideline. Quantitative-data credit requires complete directed mass balances; reasoning credit requires the correct nitrogen process and a paired, repeated, load-based design that tracks the source confounder.
Glossary

Key terms for The Living World: Ecosystems

Introduction to Ecosystems
Terrestrial Biomes
Aquatic Biomes
The Carbon Cycle
The Nitrogen Cycle
The Phosphorus Cycle
The Hydrologic (Water) Cycle
Primary Productivity
Trophic Levels
Energy Flow and the 10% Rule
Food Chains and Food Webs
FAQ

The Living World: Ecosystems FAQ

How should I distinguish an ecosystem from a biome in a data question?

Treat an ecosystem as interacting organisms plus their local physical environment, while a biome is a broad climate-defined region. Use the scale, variables, and boundary shown rather than choosing the more familiar label.

What is the safest way to follow matter through a biogeochemical cycle?

Name each reservoir, label the process on every transfer arrow, and check that atoms are conserved. Photosynthesis, respiration, combustion, weathering, fixation, and denitrification move matter through different pathways.

Why is energy not recycled in the same way as nutrients?

Energy enters many ecosystems as sunlight and leaves largely as heat after metabolic work. Nutrient atoms can return to reservoirs, but usable energy declines at successive trophic transfers.

When is the ten-percent rule useful and when is it only an estimate?

Use it for an order-of-magnitude trophic calculation when the prompt supplies or implies that efficiency. Real transfer efficiency varies, so do not present ten percent as a universal measured constant.

What earns the mechanism point in a Unit 1 explanation?

A mechanism names the intermediate process between driver and outcome—for example, added nitrogen increases primary production, more biomass decomposes, microbial respiration consumes oxygen, and aquatic dissolved oxygen falls.

Study strategy

How to study The Living World: Ecosystems

Build three separate diagrams from memory: a carbon reservoir map, a nitrogen transformation map, and a trophic-energy pyramid. Then annotate each arrow with a process and test whether matter is conserved while usable energy declines.

Practice translating one ecosystem observation into two sentences. The first must report only the displayed direction and comparison; the second must name the biotic or abiotic mechanism. This separation prevents a plausible story from replacing evidence.

For every Unit 1 calculation, write the requested unit before substituting values. Use that target to choose a ratio, transfer efficiency, or productivity equation, and reject any result whose order of magnitude contradicts trophic loss.

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