Jarrah Forest is an interim Australian bioregion located in Western Australia. The Jarrah Forest comprises reserves across the south-west corner of WA and is managed for uses including recreation. There are many small areas of parkland while larger protected areas include the Dryandra Woodland, Lane-Poole Reserve, and the Perup Forest Ecology Centre. Also managed for land uses such as water, timber and mineral production, recreation and conservation, the forest is recognised globally as a significant hotspot of plant biodiversity and endemism.
Location and description
The bioregion stands on the 300-metre-high (980 ft) Yilgarn block inland plateau and includes wooded valleys such as those of Western Australia's Murray River and the Helena River. On the west coast further south the jarrah forest region also covers the Leeuwin-Naturaliste Ridge. At the southern end of the plateau is the Whicher Range and inland is the lower Blackwood Plateau. The eastern interior of the region includes the peaks of the Stirling Range, now preserved within Stirling Range National Park.
The name of the forest refers to the region's dominant ecosystem: jarrah forest; that is, a tall, open forest in which the dominant overstory tree is the jarrah. (Eucalyptus marginata). Soils in the jarrah forest are fertile, but often salt laden. The area has a warm Mediterranean climate, with more annual rainfall (1,300 millimetres (51 in)) on the scarp than inland or to the north-east (700 millimetres (28 in)).
Jarrah (Eucalyptus marginata) is considered one of the best general purpose hardwoods in the world. The British started logging jarrah forest in south-west Western Australia in the 1840s to produce timber for use in construction, transport and power, and to protect water supplies. Logging was largely unregulated until the release of the Forests Act of 1918. The following 50 years saw forest management expand to include water quality and yield, soil management, rehabilitation of mined forest, recreation and nature conservation. Today jarrah is harvested for high quality furniture and flooring.
The Jarrah Forest is unique in that it is dominated by two eucalypt species; jarrah and marri (Corymbia calophylla). Marri is a prevalent canopy species and the jarrah forest is commonly called jarrah-marri forest. Other Eucalypts are present but in much less abundance. The Southern Jarrah Forest contains extensive areas of wetland vegetation in the south–east, dominated by paperbarks including the swamp paperbark (Melaleuca rhaphiophylla), and other eucalypts such as the swamp yate (Eucalyptus occidentalis) and the Albany blackbutt (Eucalyptus staeri)  The eastern forest is largely wandoo woodland, dominated by the canopy species wandoo (Eucalyptus wandoo), and, on breakaways, powderbark (also known as powderbark wandoo) (Eucalyptus accedens). Other eucalypts in these eastern areas include York gum (Eucalyptus loxophleba). The upland areas are particularly rich in plant life, while the drier inland plateau is less so. The wetter valleys with fertile soils contain flooded gum (Eucalyptus rudis), bullich (Eucalyptus megacarpa) and blackbutt (Eucalyptus patens). Heath is a common understorey of the jarrah forest in the north and east.
The smaller trees commonly found in Jarrah forest include bull banskia (Banksia grandis), sheoak (Allocasuarina fraseriana), snottygobble (Persoonia longifolia) and woody pear (Xylomelum occidentale). Rare plants within the Jarrah Forest include orchid species Drakaea confluens and Caladenia bryceana, and Baumea reed beds are unique to the forest and adjacent areas.
The Jarrah Forest supports 29 mammal, 150 bird, and 45 reptile species. Mammals include the numbat (Myrmecobius fasciatus), Gilbert’s potoroo (Potorous gilbertii), western quoll/chuditch (Dasyurus geoffroii), woylie (Bettongia penicillata), tammar wallaby (Macropus eugenii), western ringtail possum (Pseudocheirus occidentalis), the common brushtail possum (Trichosurus vulpecula''), southern brown bandicoot or quenda (Isoodon obesulus), and the red-tailed phascogale (Phascogale calura). Most of these were once widespread vertebrate species but are now limited to the fragmented portions of the Jarrah Forest.
The chuditch, before the introduction of large mammalian pest species, was the largest carnivorous marsupial in south-west WA, distributed across 70% of mainland Australia.  It now inhabits only 2% and is listed as 'Vulnerable' under the Environmental Protection and Biodiversity Conservation Act of 1999. For species such as the brushtail possum, population decline has not been extensive as they will colonise older restored minesites.
The Carnaby's black cockatoo (Calyptorhynchus latirostris) is endemic to south-west Western Australia and is listed as endangered under the EPBC of 1999. Other birds to inhabit the Jarrah forest include rare birds such as the forest red-tailed black Cockatoo (Calyptorhynchus banksii naso), Muir`s corella (Cacatua pastinator pastinator), the western whipbird (Psophodes nigrogularis), the western bristlebird (Dasyornis longirostris), the noisy scrub-bird (Atrichornis clamosus) and Baudin's black cockatoo (Calyptorhynchus baudinii).
Reptiles inhabiting the Jarrah Forest include legless lizards, dragon lizards, skinks, blind snakes, pythons and venomous snakes. The western bearded dragon (Pogono minor) was found in restored forest rather than old growth forest.
Amphibians found in the northern sector of the Jarrah Forest include the rare white-bellied frog (Geocrinia alba), yellow-bellied frog (Geocrinia vitellina) and sunset frog (Spicospina flammocaerulea). Endemic frogs inhabit the southern sector of the Jarrah Forest such as the small western froglet (Crinia subinsignifera) and the western marsh frog (Heleioporus barycragus).
Diverse invertebrate fauna populations are also present within the Jarrah Forest. Many of these invertebrate species are responsible for nutrient recycling, an essential element of Western Australia’s biodiversity. In particular, the invertebrate group Aprocrita are a keystone group that, through predation and parasitism, keep other invertebrate populations controlled. The loss of Aprocrita could be detrimental to the invertebrate community and to the jarrah forest ecosystem.
Most of the Jarrah Forest has been cleared for agriculture, timber and mining, leading to the consequent degradation of flora and fauna species and ecosystems. This is further threatened by the replacement of native vegetation with exotic grasses and weeds, introduced grazing species and predators such as the fox (Vulpes vulpes). Native flora also suffers from disease and exploitation of water sources for agriculture. Less anthropological threats include periodic wildfire, pathogens, variable climate and outbreaks of defoliating insects.
The significant population loss of fauna species in the Jarrah Forest is attributed to the fox and cat (felis catus). Predators can influence abundances and ranges of species at all trophic levels, including primary producers, prey and other predators. Between 1933 and 1944 the terrestrial range of the quokka (Setonix brachyurus), the woylie, the chuditch, the brushtail possum, the western ringtail possum, the tammar wallaby and the numbat contracted quite dramatically. This was blamed on the fox. Population numbers, however, of woylies and boodies were already declining in 1911, most likely due to cats (Felis catus) introduced by Europeans. Another introduced species that is a major threat to birds in some areas of the Jarrah Forest, but for a very different reason, is the feral bee (Apis mellifera). Swarms of feral bees take over tree hollows, stealing the nesting sites of hollow-nesting birds.
Habitat loss and fragmentation
Landscape fragmentation and the loss of suitable macro- and microhabitats can be detrimental to an animal’s ability to live in or traverse through an area. The range of the western quoll has dramatically reduced since European settlement. With matrix permeability greatly reduced this wide-ranging carnivore is highly susceptible to being hit by vehicles as it crosses road reserves moving from one area to another. The roadkill count of fauna in general on bauxite mines fringing Jarrah Forest is high. Despite the restoration and protection of jarrah forest in areas previously used by mine sites, the lack of hollow logs and stumps on the ground is evident. Low understory cover, low plant species richness and relatively low biomass are all problems associated with protected restored jarrah forest. Suitable habitats can take decades to form and animals that rely on these for shelter, such as the chuditch and Egernia napoleonis, are left without. Similarly birds that nest in tree hollows will not do so until trees are big enough and old enough to have sufficient hollows. Jarrah is a slow growing species and 130 years can be considered the minimum age for the development of appropriate hollows in jarrah and marri.
The loss of forest for agriculture and timber has resulted in diminishing population numbers of many fauna species. Nine mammal and seventeen bird species are obligate users of tree hollows. Species that use large hollows usually have a relatively small home range and depend on their hollows for breeding. These species are most likely to be negatively impacted by logging. Roost sites (hollows) are critical for the persistence of insectivorous bats living in the Jarrah Forest. Spending a large portion of their lives in roosts, they are used as diurnal shelters, shelter during maternity, and shelter for bachelors, migrating and hibernation sites. Facilitating complex social interactions including information transfer, roost sites also act as breeding sites, they provide protection from bad weather and predators, they minimise parasite load and promote energy conservation.
Prevalent in the northern areas of the Jarrah Forest, dieback disease, caused by the introduced soil-borne pathogen Phythopthora cinnamomi, is a serious threat to many plant species. The disease involves the formation of lesions (decaying tissue) starting in the roots and moving up the stem of a plant, and, in the case of many species, killing them. It negatively affects more than 22% of the plant species in the forest. P. cinnamomi has been found in suberized and partially suberized roots that are perennial and it is these roots that form the specialised feeder root system of the jarrah. The spread of dieback is exacerbated by altered drainage caused by mining and timber harvesting. The soil population of P. cinnamomi is generally highest during spring, the time of year when soil temperature and moisture levels are high. An increase in summer rainfall is likely to increase the harm that this pathogen causes in the northern and southern jarrah forests, with high mortality rates of jarrah expected.
FORESTCHECK is a Department of Parks and Wildlife initiative that is responsible for monitoring biodiversity in the jarrah forests of south-west Western Australia. Monitoring total species richness, abundance and composition FORESTCHECK is designed to provide forest managers with accurate accounts of changes and trends in biodiversity associated with management activities. FORESTCHECK use four Jarrah Forest ecosystems that reflect four different management systems: old-growth forest that has not been harvested or at least not in the last 40 years, coupe buffers (temporarily unharvested forest between harvested areas), shelterwood forest and forest receiving gap release treatment. Shelterwood forest limits logging to a residual basal area of c. 13m2ha-1 and gap release treatment to a residual basal area of c. 6m2ha-1. These are surrounded by an unlogged coupe buffer of approximately 100m. Focussing on timber harvesting and silviculture treatments in the present, future monitoring programs may be extended to include fire, climate change, mining, utility corridors and recreational use. Silviculture is a practice carried out in restored areas of Jarrah Forest. It aims to promote growth of retained trees, to enable the growth of young regeneration trees without having to compete with the overstory, to establish seeding regeneration and to retain and promote flora species and individuals in forests infested by dieback. Disease-loss appraisal is critical in developing economic and rational management strategies for dieback.
The benefits of using biological controls and fungicides have been explored in the management of P. cinnamomi. Fifteen native Western Australian legumes were tested for their effectiveness as biological control agents against the pathogen. Five species showed high potential and by manipulating rehabilitation seed mix ratios could be used to suppress the pathogen. The fungicide phosphite has been found to be effective treatment against P. cinnamomi, especially when applied before a plant is infected. The fungicide can be applied after infection, however the greater the time between infection and treatment, the less effective it will be. It is difficult to estimate the cost of plant disease in conservation areas; loss of conservation values cannot be given monetary value. However, the cost of controlling the disease can. It was estimated that the control of P. cinnamomi in 1989 cost the Western Australian Government at least $3.4 million. Disease management plans focus on minimising the spread of the mould by restricting movement of propagules in soil and by translocating plant species from infected sites to healthy sites.
Vertebrate fauna play a key role in jarrah forest ecosystem processes including pollination, grazing and predation. The chuditch, quenda and common brushtail possums are three such species considered essential in the development of a sustainable restored forest ecosystem. To prevent population numbers of these species and other vertebrates from further declining an aerial fox baiting program was introduced forest-wide.
Management practices carried out to ensure the persistence of hollow-using species include protecting old growth jarrah forest and keeping extensive areas of forest reserved from logging. In the sections of jarrah forest are available to timber harvesting, science-based prescriptions have been implemented delegating those trees that are to be retained.
Benefits of Protection
Unlogged buffers and old growth forest contain high densities of trees with appropriate hollows for roosting, where gap release and shelterwood areas do not. Mature forest is essential to the development of tree hollows and the prescribed retention of the largest trees will significantly improve the chances of large species such as the red-tailed black cockatoo and the common brushtail possum inhibiting appropriately sized tree hollows.
The implementation of the fox baiting program was expected to greatly increase the population numbers and range of native including the western ringtail possum which was re-introduced into the jarrah forest in the same time-frame. The abundance and distribution of the chuditch population in south-west WA has recovered quite significantly in the last decade and this has been attributed to the control of foxes. Within two to three years of the aerial baiting program mammal species numbers increased. Capture rates (interpreted as mammal abundance) of the woylie, chuditch and common brushtail possum coincided with the efforts of this program. In 1974-1999 six mammals were listed as threatened under Australian Commonwealth and WA stage legislation, the woylie, tammar wallaby, quenda, chuditch, numbat and the western ringtail possum. Now, the quenda and the tammar wallaby are no longer classified as a threatened species.
Studies of reptiles in the Jarrah Forest show that the older a rehabilitated forest is, the greater the number of reptile species will be present. Species requiring particular habitats such as exfoliating bark (gecko Phyllodactylus marmoratus) or deep leaf litter (blind snake Ramphotyphlops australis) were not present in rehabilitated sites that were eight years old, but were present in those greater than twelve years old. Similarly, various rehabilitated sites were monitored and black cockatoos were found feeding only in rehabilitated forests established eight or more years ago, the time needed for food resources to become available. Birds rapidly colonise and 95% of species found in old growth Jarrah Forest are now in rehabilitated forests ten years or older. The protection of old growth jarrah forest needs to continue and additional jarrah forest needs to be rehabilitated to promote further growth, decrease fragmentation and to maintain and improve flora and fauna biodiversity, a process that may take decades.
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