Biology • Year 11 • Module 4 • Lesson 22

Conservation: Strategies, Ethics and Australian Case Studies

Apply in-situ and ex-situ concepts to real data, Australian case studies, and a comparative evaluation across multiple criteria.

Apply · Data & Reasoning

1. Interpret data — eastern barred bandicoot captive program

The table below models the eastern barred bandicoot captive breeding program: founder numbers, cumulative captive-bred individuals, and the number reintroduced into predator-proof fenced reserves over four monitoring periods. 7 marks

Period Captive founders Cumulative captive-bred Released to fenced reserves
1991–1999406200
2000–2009401,840150
2010–2019404,100420
2020–2021405,000510

Hypothetical data modelled on published Zoos Victoria recovery records.

1.1 Describe the trend in the cumulative number of captive-bred bandicoots across the four periods. 2 marks

1.2 Calculate the percentage of cumulative captive-bred bandicoots that had been released to fenced reserves by 2021. Show your working. 2 marks

1.3 Using lesson content, explain why the program released animals only into predator-proof fenced reserves rather than into open habitat. 3 marks

Stuck? Revisit the eastern barred bandicoot case study in Card 3 and the threat-abatement section of Card 1.

2. Compare and contrast — in-situ vs ex-situ conservation

Complete the table using information from the lesson. Where a cell is already filled, use it as a clue for the adjacent row. 8 marks

Criterion In-situ conservation Ex-situ conservation
Definition Protecting species within their natural habitat
Main tools Captive breeding, seed banks, zoos, botanic gardens
Cost
Ecological context Preserves ecosystem function, predator–prey relationships and evolutionary processes
When used
Key risk Threats may still operate inside protected areas (feral predators, weeds)
Australian example Taronga Zoo captive breeding of the corroboree frog
Stuck? Use lesson Cards 1 and 2 as your reference. The in-situ vs ex-situ comparison table in Card 4 is also useful.

3. Case study — the corroboree frog

Read the scenario and answer the questions that follow. 6 marks

Scenario. The southern corroboree frog (Pseudophryne corroboree) lives in the alpine sphagnum bogs of Kosciuszko National Park, NSW. By the early 2000s, chytrid fungus — an introduced aquatic pathogen that attacks frog skin — had reduced the wild population to fewer than 100 individuals. No effective field treatment existed. In response, Taronga Zoo established a captive breeding program that now holds more than 2,000 individuals. Reintroduction into chytrid-treated bog habitats is ongoing, but the wild population remains critically small.

3.1 Identify the specific threat driving the corroboree frog's decline and classify it as biotic or abiotic. 2 marks

3.2 Explain why ex-situ conservation was chosen as the primary response for this species rather than in-situ protection of the national park. 2 marks

3.3 Suggest one reason why the corroboree frog recovery is considered less complete than the eastern barred bandicoot recovery, using lesson content to support your answer. 2 marks

Stuck? Compare the corroboree frog and eastern barred bandicoot case studies in Card 3.

4. Predict and justify — the northern hairy-nosed wombat

The northern hairy-nosed wombat (Lasiorhinus krefftii) exists as a single population of approximately 300 individuals at Epping Forest National Park, Queensland. Conservation managers are debating whether to establish a second population at a separate reserve via translocation. 5 marks

4.1 Predict two conservation benefits of establishing a second wombat population. 2 marks

4.2 Predict one biological risk of translocation and explain how it could threaten the success of the new population. 2 marks

4.3 Based on the risks and benefits you identified, predict whether translocation should proceed. Justify your answer in one sentence. 1 mark

Stuck? Activity 1 in the lesson discusses this exact species.
Answers — Do not peek before attempting

Q1.1 — Trend description (2 marks)

The cumulative number of captive-bred bandicoots rises steadily across all four periods, from 620 to about 5,000 [1]. Growth accelerates in the middle periods (the largest decade-on-decade increases occur between 2000 and 2019) as the breeding program matures [1].

Q1.2 — Percentage released (2 marks)

Working: (510 ÷ 5000) × 100 = 10.2% [1 for correct arithmetic; 1 for expressing the answer as a percentage]. So about one in ten captive-bred animals had been released to fenced reserves by 2021.

Q1.3 — Why fenced reserves only (3 marks)

Foxes were the threat that drove the species to Extinct in the Wild, and they still occupy the open landscape [1]. Releasing animals into open habitat would expose them to the same fox predation, so released individuals would be killed before establishing [1]. Predator-proof fencing is in-situ threat abatement that removes the fox threat at the release site, giving reintroduced animals a safe haven in which to breed [1].

Q2 — Compare-and-contrast table (8 marks — 1 per correct cell)

Criterion In-situ Ex-situ
Definition Given (protecting species in natural habitat) Maintaining populations outside natural habitat as a safety net [1]
Main tools National parks, MPAs, wildlife corridors, threat abatement, restoration [1] Given (captive breeding, seed banks, etc.)
Cost Lower per species; one area protects many species [1] High per individual; ongoing facility and staffing costs [1]
Ecological context Given (preserves ecosystem function etc.) Saves the target species but not its ecological context [1]
When used Preferred wherever viable habitat exists and threats can be managed [1] Last resort when populations are too small, threats too severe, or habitat gone [1]
Key risk Given (feral predators, weeds) Adaptation to captivity; genetic drift; loss of wild survival skills [1]
Australian example Gondwana Link corridor; Shark Bay MPA; predator-proof fencing at national parks [1] Given (Taronga Zoo / corroboree frog)

Q3.1 — Threat identification (2 marks)

The specific threat is chytrid fungus (Batrachochytrium dendrobatidis), an introduced aquatic pathogen [1]. This is a biotic threat because it is a living organism (a fungus) that directly attacks and kills the frogs [1].

Q3.2 — Why ex-situ was the primary response (2 marks)

Chytrid fungus spread through the water in Kosciuszko National Park, so the wild habitat itself was the source of the threat [1]. Because no effective in-situ treatment for chytrid existed, protecting the national park could not prevent continued deaths — the only way to keep the species alive was to remove individuals and breed them in a disease-free captive facility [1].

Q3.3 — Why corroboree frog recovery is less complete (2 marks)

The eastern barred bandicoot was reclassified from Extinct in the Wild to Endangered in 2021, meaning a self-sustaining managed wild population exists [1]. The corroboree frog remains critically small in the wild and dependent on ongoing captive breeding because chytrid fungus persists in the habitat and cannot yet be eliminated — recovery requires treating or removing the in-situ threat before any lasting wild population can be sustained [1].

Q4.1 — Benefits of a second population (2 marks)

Benefit 1: reduces the risk of catastrophic loss — if disease, fire, or drought wiped out the single Epping Forest population, the species would go extinct; a second site acts as insurance [1]. Benefit 2: increases total genetic diversity by expanding and connecting breeding pools, reducing inbreeding risk in a species with only ~300 individuals [1].

Q4.2 — Risk of translocation (2 marks)

One risk is disease introduction: translocated individuals may carry pathogens or parasites from Epping Forest that could devastate the new population or other wildlife at the destination site [1]. If this occurred it could threaten both the new wombat population and native species in the receiving reserve [1]. (Accept also: stress-related mortality during capture/transport; failure to establish in different habitat conditions.)

Q4.3 — Recommendation (1 mark)

Translocation should proceed because removing the all-eggs-in-one-basket extinction risk outweighs the manageable risks, provided a strict disease-screening protocol is followed before and after movement [1]. (Accept any biologically justified recommendation with reasoning.)