Teacher/student led
In this lesson, students will learn about the significant human-induced changes to the Illawarra-Shoalhaven subtropical rainforests, focusing on the historical practices of the Dharawal Nation and the impacts of European settlement. They will explore the consequences of land clearing for agriculture, logging, and urban development, alongside the effects of climate change and invasive species on biodiversity and ecosystem health. Students will create a timeline of key modifications to the rainforest ecosystem and analyse climate projections for the region, proposing the effects in the rainforest ecosystem. Additionally, students will evaluate the consequences of potential tipping points, including habitat connectivity loss, altered fire regimes, and invasive species proliferation, and how these could lead to irreversible changes in the Illawarra-Shoalhaven rainforests.
40 minutes
Lesson 3 worksheet - Human-induced modifications
Prior to European settlement, the Dharawal people, as custodians of their land, used cultural fire practices involving low-intensity fire regimes. While these practices were more prevalent in open woodlands and grasslands, they also influenced the edges of subtropical rainforests, promoting a mosaic of vegetation and reducing the risk of large-scale fires in fire-sensitive areas. This sustainable approach maintained the natural balance of the rainforest.
Land clearing surrounding Saddleback Mountain, c. 1890s.
The arrival of European settlers in the late 18th and early 19th centuries marked the beginning of significant changes. The fertile volcanic soils of the Illawarra Escarpment attracted farmers, and large portions of subtropical rainforest were cleared for agricultural purposes, particularly for dairy farming and cropping. By the mid-1800s, vast areas of lowland rainforest had been cleared to support agricultural expansion, especially in places like Jamberoo, Kiama, and Albion Park. By the early 1900s, less than a quarter of the original forest remained.
Cedar getters c.1850s.
Simultaneously, the rainforests were heavily exploited for valuable timber resources. The Illawarra region was a prime source of Red Cedar (Toona ciliata), which was felled extensively for use in construction and furniture. The removal of red cedar and other large hardwood species had a profound effect on forest structure and biodiversity. Logging in the region persisted into the early 20th century, significantly reducing old-growth rainforests.
From 1840 to 1900, Red Cedar was logged so intensively that it was almost completely removed from the Illawarra rainforests. The rapid depletion of these trees destabilised the rainforest ecosystem, making it more susceptible to erosion and loss of biodiversity.
Mt Kembla coal mine, 1902
Throughout the 20th century, coal mining, particularly on the Illawarra escarpment, was a major driver of deforestation and habitat destruction. Both open-cut and underground mining operations not only cleared large areas of rainforest but also degraded soil quality and polluted waterways, which disrupted the delicate balance of the ecosystem. For example, the Mount Kembla Mine, operational since 1880, and subsequent mining expansions caused significant fragmentation of rainforest habitats. This led to increased soil erosion and watercourse degradation, which compounded the negative impacts on surrounding subtropical rainforest ecosystems, reducing biodiversity and altering water flow patterns.
Wollongong from Mt Keira, c.1950.
Urbanisation has significantly impacted the Illawarra-Shoalhaven subtropical rainforest, particularly from the mid-20th century onward. The expansion of Wollongong and surrounding coastal areas led to widespread land clearing, reducing forest cover and fragmenting ecosystems. For example, post-World War II development in the 1950s and 1960s accelerated urban sprawl, as housing, roads, and industrial infrastructure encroached on the natural environment. By the 1970s, significant sections of rainforest had been lost to urban development, which further isolated patches of forest and increased vulnerability to environmental threats such as invasive species and pollution.
Port Kembla steel works
Urban expansion in the Illawarra-Shoalhaven region is somewhat constrained by the steepness of the escarpment, which limits available flat land for development. As a result, urban growth tends to occur along the coastal areas and valleys, leading to the fragmentation of remaining rainforest patches. Although urban sprawl is restricted, any development that does occur still impacts the rainforest by introducing runoff, pollutants, and invasive species, while increasing the pressure on already vulnerable habitats.
The subtropical rainforests of the Illawarra-Shoalhaven have been significantly altered due to extensive land clearing and habitat destruction since European settlement in the late 18th century. This initial clearing for agriculture and urban development has created fragmented landscapes, making the native ecosystem more vulnerable to invasion by non-native species. The introduction of various plants and animals, either intentionally or accidentally, has compounded the ecological pressures on these already stressed environments. Invasive species thrive in the disturbed habitats, often outcompeting native flora and fauna for resources. As a result, they contribute to a decline in biodiversity, disrupt ecosystem functions, and ultimately threaten the health of the rainforest.
Key invasive plants and animals to the subtropical rainforests of the Illawarra-Shoalhaven are detailed below.
(Lantana camara)
Arrival: Lantana was introduced to Australia from South America in the early 19th century as an ornamental plant and for erosion control.
Impact: It forms dense thickets that shade out native plants, inhibiting their growth and preventing the regeneration of native species. Lantana's rapid spread can lead to a reduction in biodiversity and alter the overall structure and function of the ecosystem, making it harder for native plants to thrive .
(Asparagus aethiopicus)
Arrival: Asparagus fern was introduced from South Africa in the mid-19th century as an ornamental plant and ground cover.
Impact: This plant can quickly invade forest understories, smothering native plants and preventing seedling establishment. Its rapid spread disrupts local ecosystems, leading to decreased biodiversity and altered habitat dynamics.
(Solanum mauritianum)
Arrival: Tobacco Bush was introduced to Australia from Argentina in the 19th century as a garden plant.
Impact: It can smother and shade native plants, leading to a decline in native flora. Its spread contributes to the overall degradation of the rainforest ecosystem, as it outcompetes native species for resources, further impacting biodiversity.
(Capra hircus)
Arrival: Feral goats were introduced to Australia in the late 18th century for meat production and later escaped into the wild.
Impact: They are significant browsers that overgraze vegetation, leading to soil erosion and reduced regeneration of native plants. Their presence disrupts local ecosystems and degrades habitat quality, threatening native biodiversity.
Arrival: Red foxes were introduced to Australia from Europe in the mid-19th century for recreational hunting.
Impact: They are predators that pose a serious threat to native wildlife, particularly small mammals and ground-nesting birds. Their predation contributes to the decline and extinction of vulnerable species, further disrupting the balance of the ecosystem
(Dama dama) and (Rusa unicolor)
Arrival: Various deer species were introduced to Australia in the 19th century for hunting purposes.
Impact: Deer cause significant damage by overgrazing native plants, leading to habitat degradation. They can also contribute to soil erosion and alter the composition of plant communities, which impacts the broader ecosystem.
Lilly Pilly tree infected with myrtle rust
Myrtle Rust (Austropuccinia psidii) is an invasive fungal disease that poses a significant threat to the subtropical rainforests of the Illawarra-Shoalhaven region. It was first identified in Australia in 2010, likely arriving from South America. This pathogen primarily affects plants in the Myrtaceae family, including key rainforest species like Lilly Pilly (Syzygium spp.) and the critically endangered Scrub Turpentine (Syncarpia glomulifera).
Myrtle rust infects young leaves, buds, and stems, leading to symptoms such as leaf blight, defoliation, and reduced reproductive success. In the case of Scrub Turpentine, which is a dominant species in these rainforests, infection can result in severe health decline, impacting its growth and ability to provide habitat and food for local wildlife. The loss of Scrub Turpentine affects not only the plant's ecosystem role but also the various fauna that depend on it for shelter and sustenance.
Historically, subtropical rainforests are fire-sensitive ecosystems. Increased temperatures and prolonged droughts due to climate change elevate the risk of wildfires in regions that are typically wet, such as the Illawarra-Shoalhaven escarpment. This ecosystem, which is not adapted to frequent fire events, can experience severe damage. Fire can lead to the destruction of the forest canopy, making it difficult for the rainforest to regenerate and allowing invasive species to colonise the area more easily.
Prolonged drought and heat stress resulting from climate change can compromise tree health, reducing canopy cover and negatively affecting the biodiversity that depends on it. The Illawarra Socketwood, for example, which is already endangered, may become more susceptible to heat and water stress. This decline in health can also impact the forest's understorey, leading to decreased nutrient cycling and fewer suitable habitats for smaller plants and animals.
The Illawarra-Shoalhaven rainforests are situated on steep escarpments, making them highly susceptible to damage from more intense storms, a likely outcome of climate change. Heavy rain and strong winds could lead to landslides, tree falls, and erosion, further fragmenting the rainforest. The destruction of tree cover and soil disturbance can hinder regeneration, affecting species that rely on dense canopy cover and stable soils.
As the rainforest becomes more fragmented and stressed by climate change, invasive species and diseases can take advantage of the weakened ecosystem. For example, the spread of invasive plants like lantana or asparagus fern could outcompete native species, altering the forest composition. Similarly, trees weakened by drought and storms may become more vulnerable to pests and diseases, further degrading forest health and resilience.
Changes in temperature and rainfall patterns can disrupt the regeneration cycles of native plant species. For example, Illawarra Zieria and White-flowered Wax Plant, both endemic species, depend on specific environmental conditions to reproduce. Shifts in these conditions can reduce their recruitment success, potentially leading to population declines. These changes can also affect seed dispersal mechanisms, particularly for species dependent on animal pollinators, which might also face habitat changes due to climate variability.
Access the map and website
Visit the NSW Climate Projections Map.
Use the Illawarra Climate Change page for additional context.
Investigate climate factors
Temperature: Explore projected changes in the mean temperature and days over 35 C for 2050, 2070, and 2090.
Rainfall: Examine changes in annual and seasonal rainfall patterns.
Fire: Analyse projections for increased severe fire weather days.
Write a summary
Refer to Question 2 c)., in your worksheet to complete the instruction below.
Summarise how these changes could affect the biodiversity and ecosystem resilience of the subtropical rainforests in the Illawarra-Shoalhaven region.
A tipping point occurs when gradual changes lead to sudden, irreversible shifts in the ecosystem. Some key tipping points relevant to the Illawarra-Shoalhaven rainforests include:
Loss of habitat connectivity: Fragmentation due to urban expansion, agriculture, and infrastructure has reduced connectivity between forest patches. A tipping point could be reached where species, particularly those reliant on large contiguous habitats (like the glossy black cockatoo), are no longer able to migrate or reproduce successfully. This can lead to local extinctions and a cascade of biodiversity loss.
Fire regimes: The Illawarra region has historically experienced low-intensity fires, but climate change and altered fire management practices could lead to more frequent, intense fires. Once a tipping point is reached where the forest can no longer recover between fires, it may transition into a different, less biodiverse ecosystem, like a grassy woodland.
Invasive species proliferation: Invasive species like lantana and feral deer put pressure on native flora and fauna. A tipping point may occur when native species can no longer compete, and the invasive species dominate, altering the forest structure and nutrient cycles permanently.