Biodiversity Strategy - Gosford City Council - NSW Government

Biodiversity Strategy - Gosford City Council - NSW Government Biodiversity Strategy - Gosford City Council - NSW Government

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A - 7.4.2 Feral Deer In the Gosford LGA two species of feral deer are known, Rusa and Fallow Deer. Some deer and goat populations are thought to have been introduced area as a result of being deliberately or inadvertently allowed to roam into other areas, this is exacerbated by a falling deer meat market (B Pengilley, D Kelly pers. comm. 2004). There is some anecdotal evidence that deer may be increasing in the Bouddi National Park/ Bensville area (Dave Kelly pers. comm. 2004). Rusa and Fallow Deer have been reported at Mangrove Mountain, Somersby, Kulnura and Cockle Bay Nature Reserve and adjoining lands also Bouddi National Park. A - 7.4.3 Feral Pigs Feral pigs are known to occur in the upper reaches of Patonga Creek (pers. observation R. Lonie mid 1990s), Mangrove Dam Catchment area. (G Woolcock pers. Observation 11/04). A - 7.4.4 Aquatic Pests The extent of aquatic pest and introduced species has not been assessed. Gambusia or Mosquito Fish are a known serious pest in waterways and predate on native fish and frog spawn. Gambusia appears to be widespread in Gosford waterways. European Carp is known to be present in Mangrove Creek (pers. comm. Grant Woolcock). Carp can degrade waterways though increasing turbidity and predation on native fish. The impacts of other introduced fish such as the Mountain Cloud Minnow that are deliberate or accidental escapees from aquariums and garden ponds on native fish and habitats is not known at this stage. A - 7.4.5 Feral Cats Feral cats were identified in Council’s wildlife survey as being an issue for the Gosford LGA and they are recognised as a key threatening process. Little is known about whether feral cats are in fact widespread or abundant in the LGA. Cats may at times stray or be partially domesticated and roam bushland areas predating on animals found there. Further research is required to determine whether feral cats are a significant regional pest and whether they are leading to a decline of native species. There are some new control methods that could be considered to manage them. Targeted trapping is also an option. They should also be considered as part of a possible predator/prey relationship if other species such as foxes are controlled and their numbers could result as an increase. A - 7.4.5 Wild Dogs Domestic dogs may also become feral; attacking wildlife and domestic animals and they interbreed with dingoes to become wild dogs. Wild dogs are already an issue in the Somersby, Mangrove Mountain to Kulnura area and in the Mangrove Creek Catchment, Brisbane Water and Dharug National Parks where wild dog baiting is undertaken. Through interbreeding with dingoes, wild dogs are further reducing the pure dingo strain. A - 7.5 Diseases Diseases are likely to become an increasing threat to native species. Some diseases already affecting local species are Chytrid fungus in frogs, Clamydia in koalas, mange in wombats. Elsewhere diseases such as the devastating Devil Facial Tumour disease that is likely to result in the extinction of the Tasmanian Devil (Tasmanian Department website at http://www.dpiwe.tas.gov.au/inter.nsf) and the herpes virus which resulted in major fish kills around Australia (Low 1999) are of major concern. The catastrophic extinctions of many frog species, particularly in high montane rainforest, is thought to be the result of the Chytrid fungus. Biodiversity - Technical Report Page 157

Low (1999) surmised that this fungus may emerge as a ‘greater agent of extinction in Australia than any feral animal, except perhaps the fox’. Council needs to ensure that it can identify emerging disease issues that threaten local diversity and collaborate with other lead agencies to effectively manage disease risks. The fact that Australia is an island continent and that native plants and animals have evolved in isolation means that they have no natural immunity or resistance to introduced diseases. Disease may be a secondary factor but when compounded with others such as habitat loss, climatic stress, reduced food resources and competition with other species, diseases may be the tipping point for species extinction. Phytophthora, which is a root borne disease that results in serious dieback in plants, is also a serious issue for Gosford. It was responsible for example for the loss of 6,000 hectares of eucalypt forest in East Gippsland (Low 1999). As a soil borne pathogen it is important that Council procedures are put in place to identify where it occurs and to eliminate the further spread of the disease. A - 7.6 Companion Animals Domestic cats and dogs can also be predators of native animals and can interfere with and impact on native animals and ecosystems. They may prey on animals for food or out of instinct or for sport. Even well fed cats can still have the desire to hunt and kill for fun. Whilst the impact of feral cats is well documented (Dickman 1996) the impacts of domestic cat predation on native species has been the subject of some dispute. One difficulty in determining possible impacts is that domestic cats may from time to time roam or be partially feral. Domestic cats and dogs can also become feral as a result of being abandoned. Some studies that have found that there was significant predation from domestic cats (Robertson 1998). Robertson’s study was based on a telephone survey of cat owners. He found that the frequency of predation of domestic cats was influenced by the amount of time that the cat spent outside, the agility of the cat and whether deterrents such as bell collars were used (Robertson 1998). Also Turner and Meister (1988), as quoted by Robertson, found that house cats have shifted their instinctive behaviour for nocturnal activity and that they were as active in preying on animals during the day as at night time. Turner and Meister also found that mammals were either eaten near the place of capture or carried home, whilst invertebrates and smaller animals were devoured at the place of capture. Figure 7.7 A baby blue tongue lizard that was attacked by a cat and required antibiotics. It was cared for by a volunteer wildlife carer. (A. Simpson). Figure 7.8 Cats can prey on native animals for sport but the consequences are often fatal as prey can die from shock and secondary impacts such as infection. (R. Lonie) Biodiversity - Technical Report Page 158

Low (1999) surmised that this fungus may emerge as a ‘greater agent of extinction in Australia<br />

than any feral animal, except perhaps the fox’.<br />

<strong>Council</strong> needs to ensure that it can identify emerging disease issues that threaten local diversity<br />

and collaborate with other lead agencies to effectively manage disease risks. The fact that<br />

Australia is an island continent and that native plants and animals have evolved in isolation<br />

means that they have no natural immunity or resistance to introduced diseases. Disease may<br />

be a secondary factor but when compounded with others such as habitat loss, climatic stress,<br />

reduced food resources and competition with other species, diseases may be the tipping point<br />

for species extinction. Phytophthora, which is a root borne disease that results in serious<br />

dieback in plants, is also a serious issue for <strong>Gosford</strong>. It was responsible for example for the loss<br />

of 6,000 hectares of eucalypt forest in East Gippsland (Low 1999). As a soil borne pathogen it is<br />

important that <strong>Council</strong> procedures are put in place to identify where it occurs and to eliminate<br />

the further spread of the disease.<br />

A - 7.6<br />

Companion Animals<br />

Domestic cats and dogs can also be predators of native animals and can interfere with and<br />

impact on native animals and ecosystems. They may prey on animals for food or out of instinct<br />

or for sport. Even well fed cats can still have the desire to hunt and kill for fun. Whilst the impact<br />

of feral cats is well documented (Dickman 1996) the impacts of domestic cat predation on native<br />

species has been the subject of some dispute. One difficulty in determining possible impacts is<br />

that domestic cats may from time to time roam or be partially feral. Domestic cats and dogs can<br />

also become feral as a result<br />

of being abandoned.<br />

Some studies that have found that there was significant predation from domestic cats<br />

(Robertson 1998). Robertson’s study was based on a telephone survey of cat owners. He found<br />

that the frequency of predation of domestic cats was influenced by the amount of time that the<br />

cat spent outside, the agility of the cat and whether deterrents such as bell collars were used<br />

(Robertson 1998). Also Turner and Meister (1988), as quoted by Robertson, found that house<br />

cats have shifted their instinctive behaviour for nocturnal activity and that they were as active in<br />

preying on animals during the day as at night time. Turner and Meister also found that mammals<br />

were either eaten near the place of capture or carried home, whilst invertebrates and smaller<br />

animals were devoured at the place of capture.<br />

Figure 7.7 A baby blue tongue lizard that was attacked by a cat and required antibiotics. It was cared for<br />

by a volunteer wildlife carer. (A. Simpson). Figure 7.8 Cats can prey on native animals for<br />

sport but the consequences are often fatal as prey can die from shock and secondary<br />

impacts such as infection. (R. Lonie)<br />

<strong>Biodiversity</strong> - Technical Report Page 158

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