Vol, 98, No. 1 January/February 1981 Special Issue: Introduced Animals and BINDER - FIX TO FIRST PAGE a. 6 se 6s © « ete) eee eS 4+ oon we 5 66 o = Sane ee ee Plants Pubuched by the FIELD NATURALISTS CLUB OF VICTORIA in which Is incorporated the Microscopical Society of Victoria $ { f5 —_ - —~ =o i = ome ee tL eee FNCV DIARY OF COMING EVENTS GENERAL MEETINGS At the National Herbarium, the Domain, South Yarra. Monday, 9 February, 8.00 p.m. The Conservation Council of Victoria and its activities, Speaker: G. Westcott, Director, C.C.V. Monday, 16 March, 8.00 p.m. Victorian opisthobranch molluscs. Speaker: Mr R. Burn, National Museum of Victoria. Monday, 13 April, 8.00 p.m. Otway study night, There will be several keynote speakers, and all groups are asked to prepare a short address. New Members — January/February meetings. Ordinary J. Bagles, 25 Hodgson St., Lower Templestowe. Miss Georgie Hodges, 1/11 Union Rd., Surrey Hills. Mrs. K. Hoogeduere, 4/6A Erclidoune Ave., Hawthorn. Bertram Lobert, 29 Aubrey Grove, Boronia. Merryl Martindale, 2 Sellwyn St., Canterbury. Joan Miller, 29 Rochester Rd., Canterbury, Ann Payne, 3/1 Lawson Grove, South Yarra. Nicolette Robson, 30A Dixon St., Malvern, Joint E, & J, Moorhouse, P.O. Box 379, Deniliquin. Mr and Mrs John Stuwe, Botany Dept., Latrobe University. M. Vanderzee & J. Phillips, 136 Macpherson St., North Carlton, Counry Michael Dexter, “‘Springhill"’, Yarra Glen Rd., Coldstream. Peter Matthews, P.O, Box 249, Mornington Ron Walsh, $4 Murray Anderson Rd., Rosebud. FNCV EXCURSIONS Saturday, 7 — Monday, 9 March, Castlemaine. This is the weekend of the annual meeting and get- together of the Victorian Field Naturalists Clubs Association, which will be hosted by the Castle- maine FNC, This year members of the Western Vic- torian Field Naturalist Clubs will attend. There will be a selection of half-day trips leaving the car park in Downes St., next to the Botanic Gardens at 9,30 a.m. and 1.30 p.m, on Saturday, Sunday and Mon- day. Saturday evening programme: 6,30 p.m. Business meeting W.V.F.N.C.A., 8.00 p.m. Laun- ching of Cliff Beauglehole'’s ‘Distribution and con- servation of vascular plants of the alpine area, Vic- toria’’. 8.15 p.m. Propagating native plants; birds of the north-central area. Sunday evening pro- gramme: 6.30 p.m. Annual meeting V.F.N.C.A. 8.00 p.m, the Castlemaine district, by C.F.N.C. members. Both meetings at the Uniting Church Hall, corner Baker and Campbell Sts. A coach has been chartered for the weekend and motel ac- commodation booked, B&B, at the cost of $60.00 per person for a limited number. Many will be cam- ping. The coach will leave Flinders St. at the Gas and Fuel at 8.30 a.m, Bring a picnic lunch. A deposit of $10.00 should be paid to the Excursion Secretary when booking by those who require motel accommodation, Sunday, 5 April. Organ Pipes National Park. The coach will leave Batman Avenue at 9.30 a.m.; fare $5.50. Bring a picnic lunch. A great amount of work has been done on this Park and it is worth a visit if you have not been there recently. Sunday, 3 May. Pirianda Gardens, The coach will leave Batman Avenue at 9.30 a.m.; fare $6.00, Bring a picnic lunch. Preliminary notices: Saturday, 17 October — Friday, 6 November. New Zealand, North Island. This is dependent of sufficient members being interested, but many places on this itinerary are not included in most of the regular tours. Tentative programme is: Oct. 17 fly to Auckland; Oct. 18 Auckland/Coromandel/- Whitianga; Oct. 19 Whitianga/Tauranga; Oct. 20 Tauranga/Rotorua; Oct. 21 Rotorua/Whakatane; Oct, 22 Whakatane/Hicks Bay; Oct. 23 Hicks Bay/- Gisborne; Oct. 24 Gisborne/Wairoa; Oct. 25 Wairoa/Napier, visiting Urewera National Park; Oct. 26 Cape Kidnappers/Napier; Oct. 27 Napier/- New Plymouth; Oct. 28 New Plymouth; Oct. 29 New Plymouth/Tongariro National Park; Oct, 30 National Park; Oct. 31 National Park/Auckland; Nov. | Auckland/Kaitaia; Nov. 2 Cape Reinga/- Kaitaia; Nov. 3 Kaitaia/Bay of Islands; Nov. 4 Bay of Islands; Nov. 5 Bay of Islands/Auckland; Nov. 6 Auckland/Melbourne. Cost would vary according to numbers going and possibly rise but it is expected to be approximately $1250. Please let Excursion Secretary know if you are interested. Special study trips: Contact Wendy Clark for details (AH 859 8091) Saturday, 21 — Sunday, 22 February. Bat-catching expedition to Daylesford region. Bring all camping gear and food. Sunday, 22 March. Fossil excursion to limestone quarry at Geelong, The Victorian Naturalist Vol. 98, No. 1 January/February, 1981 ISSN 0042-5184 Editor: Robert L. Wallis Assistant editor: F. Dane Panetta Editorial Committee: H. Cohn, R. Kent, B. Smith Introduced Mammals in Victoria by H. Brunner, P.L. Stevens and GIR MSAGKIPOLelmnas.8ig teed At. 6 leet Aer). Sond saety feta lene by: oe eben aes 5) Trout Introduced into South-Eastern Australia: Their Interaction wath Native fisnes Dy Py Ds Jackson ..::2...4. creates ethes ned cas da 18 Introduced Non-marine Molluscs in Australia by B.J. Smith..... 24 The Effects of Introduced Aquatic Plants in Australia by H.I. PAE RUCMNS S752, "cto rae oe Se eee OE ern Ce pe eh av Boneseed in the Bushland of Victoria by D. Lane............... 28 The Rehabilitation of Weed Dominated Communities by F.D. PATS BEA eas eerste eA Br A eee, ec ieee Las Oot seees och leat date witeleyed 31 Some Notes on Feral Pigs and Their Distribution in Victoria by SSM O Wi SEM etre ote ats eno eres Airs Secrest ey: Grae eo daed tal 37 Bush-peas of Victoria — Genus Pultenaea 15 by M.G. Corrick ... 42 ENGV-— Reports of @lub Activities. (juss pees peg see ner 45 Cover illustration: An unusual malformed shell (cornucopiae) variant of the common introduced garden snail, Helix (Cryptomphalus) aspersa. Specimen found at Lakes Entrance. Club Awarded Victorian Conservation Prize for 1980 The Victorian Conservation Prize for 1980, awarded annually by the Conservation Council of Victoria for outstanding contributions in the field of conservation, was awarded to the Field Naturalists Club of Victoria. The prize, a large oil painting by the conservation artist Mr Neil Douglas, was presented to the President of the Club by The Honorable Rupert Hamer, M.P., Premier of Victoria in the Melbourne Room, Treasury Place on Monday, 8 December 1980. The presentation was made in the presence of a large gathering of specially invited guests from conservation bodies and research institutions from throughout Victoria. The citation with this year’s prize reads as follows:— “The Victorian Conservation Prize (Neil Douglas Award) for 1980 has been awarded to the Field Naturalists Club of Victoria. Since its inception in May 1880 the Club has been in the forefront of organisations devoted to the study and preservation of Victoria’s heritage of plant and animal life. The diversity and specialisation of the Club’s activities may be seen in the work of its various sub-groups of Mammal Survey, Botany, Geology, Microscopy, Marine Biology and Entomology. Publication of the bi-monthly journal, ‘‘The Victorian Naturalist’, and an impressive list of standard reference texts has provided Victoria, and indeed the world, with a wealth of scientific data. Together with such other societies as the Victorian National Parks Association, the Native Plants Preservation Society, the Mammal Survey Group and the Society for Growing Australian Plants which all grew from the F.N.C.V., the Club continues to make lasting and valuable contributions to Victoria’s natural history.”’ The receiving of this prize rounded off a very successful Centenary Year for the Club. I would like to thank the Council and members of the Club for their magnificent support during the Club’s centenary year. Brian J. Smith President Symposium on the Effects of Introduced Animals and Plants in Australia This one-day symposium, on the effects of introduced animals and plants in Australia, was held on Sunday 27 July at the State College of Victoria — Rusden. Jointly sponsored by the F.N.C.V. and the State College, the symposium was organised by the Senior Lecturer in Environmental Studies at the College, Mr Rob Wallis. The symposium was attended by over 80 students and club members and members of various natural resources research bodies. Following the opening address by Senior Lecturer in Zoology at Latrobe University, Mr Peter Rawlinson, 12 papers were presented on all aspects of the topic and lively discussions were generated by these papers. Six of the papers, covering the field are reproduced in the issue of this Naturalist. The texts of all the papers presented will be published as a separate publication by Rusden State College. 4 Vic. Nat. Vol. 98 Introduced Mammals in Victoria By HANS BRUNNER¢ P, L. STEVENS and J, R. BACKHOLER+ Introduction Since the advent of white man in Australia, many species of mammals have been introduced into this country. Some of these species were brought in as domestic livestock for the supply and production of meat and wool, while other species were introduced for sport and recreation, as pets, and for the misguided endeavours of the Victorian Acclimatization Society. A few species such as rats and mice were introduced accidentally, presumably with infested ships cargo, Unfortunately, many of these species have been able to escape into our wilderness, farming and urban areas, and have successfully managed to breed and establish colonies in a wide range of habitats. In Victoria, about twenty species of introduced mammals are living in the wild, some of course more successfully than others (Table 1). Most of these have since been declared as pest or vermin animals. Surprisingly, the release of exotic mammal species is still continuing. Two species of deer, the hog deer (Axis porcinus) and the fallow deer (Dama dama) have recently been released into Victorian forests and bushland for future sport. Unconfirmed reports to the Victorian Deer Advisory Council Suggest the presence of yet another species, Japanese sika (Cervus nippon) in the Mallacoota area (Anderson 1978), At least four species of deer: hog, sambar, red and fallow are now roaming wild in large numbers in the Eastern Highlands where they may _ exert pressure on the already oppressed native fauna and flora by competing for food and shelter. In New South Wales’ Royal National Park, culling of rusa has been necessary because of their high numbers (Anderson 1978). Because of damage done to vegetable crops by sambar deer in the Upper Yarra area, they were declared vermin in three Shires from 1951-61. Deer are also a potential host for various viral and bacterial diseases and can harbour helminth parasites and roundworms which are found in sheep Table 1. Mammals introduced into Victoria, which are capable of living in the wild Rattus rattus R. norvegicus Mus musculus eee errs Black rat, Ship rat Brown rat, Norway rat House mouse Oryctolagus cuniculus Rabbit Lepus capensis Hare Canis familiaris Domestic dog Vulpes vulpes Fox Mustela putorius Ferret Felis catus Cat Equus caballus Horse * Sus scrofa Pig + Dama dama Fallow deer + Axis porcinus Hog deer + Cervus unicolor Sambar + C. elaphus Red deer + C. timorensis Rusa + Axis axis Chital Bos taurus European cattle Capra hircus Goat Ovis aries Sheep - = control is legislated under Health Act 1958 *= control is legislated under Vermin and Noxious Weeds Act 1958 + = protected under Wildlife Act 1976. 7 Department of Crown Lands and Survey, Keith Turnbull Research Institute, Frankston, Victoria, 3199. January/February and cattle (Anderson 1978). Military- like hunting operations with four-wheel drive vehicles and packs of dogs are often even more destructive than the deer themselves. Whilst considerable effort is spent on the management and protection of deer for the benefit of only a smal section of the community, it is ironical that the native wombat (Vombatus ursinus), doing relatively little harm other than to rabbit fences, is still declared vermin. It has been suggested that goats may be used to control blackberry in timber crops. Will Australia eventually become an open zoo? A number of the species in Table | are considered to be important in terms of economics, disease and _ wildlife conservation, Thus, feral dogs and cats, foxes, pigs and rabbits are treated separately and aspects of their distribution, breeding, diet and control are discussed below. However, mice, particularly in plague years, and rats in urban and farm areas, are also of economic and public health significance. Any detailed studies on the effects of introduced species in wilderness areas would be extremely complex. In most situations, scientists are asked to ‘‘focus in’’ on one species at a time, and so wider interpretations of their specific findings can often be expressed only in general terms. It is important to realize that when attempts are made to assess the impact these exotic intruders make on our native fauna and flora, we give consideration to all factors that may affect the latter. This should include all introduced animals, plants and, of course, man. The disappearance or reduction in numbers of indigenous predators such as the thylacine (Thylacinus cynocephalus), the tiger quoll (Dasyurus maculatus) and the eastern quoll (Dasyurus viverrinus) have only added to our speculation regarding the impact that introduced predators may have exerted on them. FOXES General The first introductions of the European red fox ( Vulpes vulpes L.) to Australia took place in the 1860s and 6 1870s with most releases being near Melbourne (Rolls 1969), The main purpose of the releases was to provide sport for ‘Colonial Gentlemen’’ and there was generally little thought as to the possible harmful effects of fox introduction. The subsequent spread of the species was rapid. Foxes are able to survive and indeed flourish in a large variety of habitats ranging from rain forest to semi-desert but it would seem that they prefer to live in areas disturbed by man. Studies in America and Europe indicate that a family of foxes establishes a home range of about 5-7 square kilometres. The territorial boundaries are generally well established and often conform to natural physical boundaries such as roads, streams and lake shores. Distribution Foxes range over some two-thirds of the continent, their northern limit being within 100 miles of the Gulf of Carpentaria. In Victoria, the density of foxes appears to be greater in closely settled agricultural areas and this is undoubtedly linked to food supply. Even large towns and cities support a resident fox population. Breeding Vixen are mono-estrus and are receptive to the male fox for only a few weeks of the year. In Australia adult males are probably infertile from September to March of the following year. Both vixen and male foxes are sexually mature at ten months of age and according to overseas work, nearly all healthy vixen produce a litter every year. In Australia, only few adult vixen are barren. This, combined with an average litter size of 4-5 viable young, accounts for the very high rate of reproduction amongst foxes in the field. According to overseas studies, the gestation period is usually 51-52 days. The young are born and reared in a den, which is usually an enlarged rabbit burrow. However stone heaps, hollow logs and natural caverns are frequently utilized as breeding sites. The vixen establishes the den site and may scratch out several dens. The young often utilize two or three dens in a confined area. Vic, Nat. Vol. 98 Weaning takes place after the first month or so and the young may frequent the natal den (or neighbouring dens) for several months thereafter. Dispersion usually takes place in late summer or early autumn. The sex ratio in Victoria and New South Wales shows a preponderance of males over females (Coman 1973a; Croft and Hone 1978). Diet Extensive investigations on the diet of foxes in Victoria indicate that the fox is an opportunist predator and scavenger, consuming an extremely wide variety of foods, The importance of any particular food item in the diet is heavily dependent on the relative availability of that food. Hence, there are marked differences in the diet of foxes from various habitat types and _ seasonal changes in diet are quite evident. In areas of agricultural or pastoral land, rabbits, house mice and sheep are the most important mammalian foods eaten. However, in heavy forest areas, largely undisturbed by man, native mammals are consumed in _ large quantities and they appear to compen- sate for the lack of rabbit, sheep and house mice in these situations (Coman 1973a; Brunner et al. 1975, 1976, 1977). The seasonal variation in incidence of various food items is marked. During summer, large numbers of insects and fruits (particularly blackberries) are eaten. At times, insects or wild fruits account for the bulk of the fox’s dietary intake. Nevertheless, the fox is primarily a carnivore preying on smaller mammals and feeding on carcasses of larger ones. Disease In Australia, we are fortunate that our fox population is probably not involved in the spread or persistence of any disease which has a major economic or public health significance. Nevertheless, foxes harbour a wide range of viral, bacterial, protozoan, helminth and arthropod organisms which may or may not exert some pathogenic affect upon their host. Distemper, hepatitis and mange appear to be the major disease conditions in Australian foxes, although there is no documented evidence of the January/February effects of these diseases on the fox population. Disease outbreaks appear to be sporadic and follow no definite pattern. However, there is some presumptive evidence that serious disease outbreaks amongst foxes occur only when the fox population in a particular area is high. The helminth parasites of foxes in Australia have been investigated in detail and at least four species of tapeworms and six species of roundworms are known to parasitize the animals (Coman 1973b). We are fortunate that the fox in Australia does not act as a carrier for the hydatid tapeworm, Echinococcus granulosus. In some other parts of the world, foxes are important hosts for this parasite. Foxes harbour a number of external parasites, the most important of which are the mange mites. Species of fleas, lice and possibly ticks also occur on foxes. The viral and bacterial diseases of foxes have been poorly studied, but leptospirosis and toxoplasmosis are known to occur in foxes. Economic damage Although foxes have often been considered responsible for heavy losses in lambs, there is little evidence to support this. Investigations indicate that, although large amounts of sheep material may be eaten, most of this is in the form of carrion. Lamb mortality studies suggest that the fox has probably been over-rated as a predator of viable lambs (McFarlane 1964). Despite this, one cannot deny that individual farmers sometimes suffer heavy lamb losses because of the activities of individual “rogue’’ foxes. A bounty payment system which was introduced in Victoria in 1949 has now been revoked. The payment per scalp was 75c and in 1977 a peak annual return of over 100,000 scalps was achieved. The current value of fox skins compensates hunters well for their efforts. Environmental aspects The Victorian studies on fox diet indicate that substantial predation upon indigenous fauna occurs in areas of heavy forest or scrub. It is commonly 7 believed that this poses a serious threat to the existence of many of our smaller indigenous fauna species. However, as foxes have become dependent on small native mammals in these areas as their staple food, it should be remembered that, after more than a century of this predator-prey relationship, there ap- pears to be still an abundance of most of the small indigenous fauna _ species throughout these areas. The disap- pearance of certain prey species in more vulnerable areas such as small and isolated reserves or in desert lands, is possibly the result of additional pressure on those species by cats, dogs and by man. Nevertheless, the wisest policy is to take the view that fox predation on in- digenous fauna is undesirable and should be minimized. Foxes with mange could spread this disease to wombats and if rabies came to Australia, foxes would most likely be the principal agent in the spread of this disease to mammals, including man. In late summer foxes eat large quantities of blackberries. The seeds in the droppings germinate readily and so the fox assists in the spread of this weed (Brunner et al. 1976). Control A variety of means have been used to control foxes in Victoria. These include poisoning, daylight drives, fumigation of dens and night spotlighting. The most efficient technique is probably that of poisoning, as foxes are extremely susceptible to 1080 poison. Fumigation of dens with chloropicrin or similar products is a useful control measure in summer, when juveniles and vixen are still in the dens. It is probably unwise to destroy established dens by digging or explosives, since the foxes will then establish new den sites in other areas. It is better to have the animals using the same known dens year after year and to fumigate these every breeding season when signs of activity are obvious. Night spotlighting is often employed in fox control, particularly during lambing time, when control of individual ‘‘killer’’ foxes is desired. DINGOES AND FERAL DOGS General The dingo (Canis familiaris dingo Blumenbach, 1780) is generally considered to be a native mammal, although it may have been in the country for only some 10,000 years or so. The origin is unknown but it is thought to be in the ancestral line from primitive dog to present domestic dog. Indeed, it is very difficult to separate dingoes from ordinary domestic dogs on the basis of blood tests, skull measurements etc. Many people use the coat colour of the animal as a means of discrimination, but black and tan as well as yellow dingoes may be recognized. Feral domestic dogs (Canis familiaris familiaris) or hybrid animals resulting from inter-breeding with dingoes are a more recent addition to our bushland, They undoubtedly originated from straying farm dogs in the early days of settlement. Domestic dogs and dingoes inter-breed freely so that we now have dingoes, cross-breeds and feral domestic dogs roaming the bush. Distribution Dingoes and feral dogs are in all States except Tasmania but are of most concern in the more arid pastoral zones of Western Australia, South Australia, Northern Territory and Queensland as well as the heavily forested Eastern Ranges of New South Wales and Victoria. They are usually in areas remote from human habitation and are by nature rather shy animals. In Victoria they are found throughout the Great Divide from the New South Wales border to the area about Healesville and Marysville. They are also in extensive areas of the more rugged country in the north-east of the State. Dingoes may still be present in the north-west of the State (Little Desert — Big Desert) and an animal assumed to be a dingo was killed near Natimuk recently. However, ene from the north-west region are ew. Dingoes are not found in the wild outside Australia but recently dog fanciers in other countries have shown great interest in breeding the dingo as a “‘show"’ dog. Vic. Nat. Vol. 98 Breeding Dingoes differ from feral dogs in that they breed only once a year. Domestic dogs can breed at least three times in two years. Dingoes mate between April and June and have their young between June and August. Like domestic dogs, the gestation period is about 63 days. Not all bitches breed in their first year and this is often taken to indicate social subordination of these younger animals by older animals. Males have an annual sexual cycle and very few sperm are produced in summer. The dingo bitch produces an average of five pups usually in places such as large hollow logs, natural caverns etc. According to some recent research work, there is evidence to suggest that not only parents, but also non-breeding young animals (first year) help rear the young (Newsome et al. 1973). Diet Dingoes and feral dogs eat a great variety of food, ranging from large native mammals through to insects, fruits and herbs. The introduction of livestock and rabbits to Australia has extended their range of food items. The results of a dietary study of Victorian dingoes and feral dogs are shown in Table 2. On a volume basis, wallabies and wombats are the major food items. It can be seen from the Table that sheep and cattle form only a small part of the diet. Nevertheless, it must be remembered that individual dogs can cause heavy stock losses from time to time (Coman 1972a). In Western Australia the most common food for dingoes was found to be the red kangaroo (Macropus rufus) and the common wallaroo (M._ robustus) (Whitehouse 1977). In Central Australia the major items in their diet are the rabbit, the long-haired rat (Rattus villosissimus), the house mouse (Mus musculus), the spinifex hopping-mouse (Notomys alexis) as well as lizards and birds (Newsome et al. 1973). Parasites and diseases The most important parasite of dingoes and feral dogs in south-east Australia is, undoubtedly, the hydatid tapeworm. This worm is probably pre- sent in 80-90% of these dogs, but is very rare in domestic farm dogs in the same areas. The hydatid worm is important because its intermediate stage (hydatid cyst) is found in man, domestic animals and native animals. The disease in man can be fatal and it may well kill some native mammals. Recent Victorian research has shown that the high in- cidence of hydatid worms in dingoes and feral dogs is probably due to the fact that dogs eat large numbers’ of infected wallabies (i.e. wallabies with hydatid cysts) (Coman 1972b), This is a self- perpetuating cycle, the wallabies picking up hydatid eggs from grass and herbage around dog faeces. Man can become in- fected by handling dingoes or feral dogs and strict hygiene should be practised. In addition to hydatid tapeworms, Table 2. Food items in stomach contents of 166 dingces and feral dogs in Victoria (Coman 1972) Food items Percentage occurrence in diet MAMMALS Wallaby ( Wallabia bicolor) 23 Wombat ( Vombatus ursinus) 20 Eastern grey kangaroo (Macropus giganteus) 7 Possum (chiefly Trichosurus vulpecula) 7 Echidna (Tachyglossus aculeatus) 6 Rabbit (Oryctolagus cuniculus) 6 Sheep (Ovis aries) 4 Cattle (Bos taurus) 3 BIRDS 5 REPTILES 6 INSECTS 33 HERBAGE 85 January/February dingoes and feral dogs harbour a number of other helminth parasites such as the sheep and cattle bladderworm (a tapeworm of dogs of which the in- termediate stage is seen as large watery bladders attached to the gut of sheep and cattle) and also roundworms and hookworms (Coman 1972a). Dogs can also become infected with mange, distemper, hepatitis and a varie- ty of other diseases, and if rabies came to Australia, dogs could be important carriers. Generally the animals seem to have little influence in the spread of im- portant livestock diseases. The possible exception to this could be hydatid disease. Economic importance Despite a huge amount of folklore and over 150 years of control work, we still have little idea of the real damage caused by dingoes and feral dogs. There can be no doubt that severe losses of livestock occur from time to time. A re- cent survey shows that livestock preda- tion in Victoria is confined almost entirely to sheep flocks (Stevens and Coman unpublished data). Control of dogs itself is a fairly expen- sive operation. Each year the Victorian Department of Crown Lands and Survey alone spends some $300,000 on dog control, Aerial poisoning of dogs has not been carried out in Victoria for a number of years as it is considered to be relatively non-specific, Also the success of such poisoning is difficult to measure. It is unlikely that aerial poisoning of dogs will be considered in the future. Ground poisoning of dogs, using carefully prepared poison doses and well placed baits appears to be more promis- ing. Dogs are extremely susceptible to 1080 poison and, using this fact, it may be possible to produce a bait which is ef-: fective on dogs but less dangerous to desired wildlife species (Rathore 1980). Combining this selectivity with carefully placed baits could very well result in the control of many dogs with a minimum tisk to other animals. However, it ap- pears that not all dogs will take baits and, therefore, poisoning cannot com- pletely replace trapping, 10 FERAL CATS General A feral cat is best defined as a cat (Felis catus L.) which obtains its own food by hunting and scavenging. Feral cats may live in close proximity to human habitation or may be completely isolated in the bush. Since cats kept as pets also roam and hunt, a_ precise distinction between feral and straying animals can sometimes prove difficult. The cat was first domesticated in Egypt about 3,500 years ago and now has a world-wide distribution. It is pro- bably true that most countries having domesticated cats also have a feral population. Despite a pronounced coat colour polymorphism, cats show little variation in size and average females weigh 2.3 — 3.0 kg and average males 3.5 — 6.0 kg. There is no sound evidence to Suggest that the average feral cat is larger than the average cat kept as a pet. They are both the same species (Scott 1972; Jones and Coman personal communication). Distribution Feral cats occur in all habitats in Australia (Anon. 1977; Bolton and Latz 1978; Marshall 1966). They are found in the Gibson Desert, the Kimberleys and Cape York Peninsula and even on sub- antarctic Macquarie Island. In the more densely settled areas feral cats appear to be concentrated about garbage dumps, picnic sites and camping grounds. The density of cats in various parts of Australia is unknown but at Macquarie Island densities may reach up to seven cats per square kilometre (Jones 1977). Breeding Female cats may have from | to 8 kit- tens per litter, but the usual litter size is from 3-5, Gestation lasts for 65 days and kittens are born between spring and late summer, Each breeding cycle takes a minimum of 444 months and one female may produce two litters per year. Kittens weigh an average of 100g at birth and are weaned after six weeks. Preliminary observations suggest that litters are born and raised in rabbit burrows, rock piles and, possibly, hollow logs. In all other Vic. Nat. Vol. 98 respects, breeding of feral cats is likely to be the same as breeding in domestic cats. Diet Research in Victoria suggests that feral cats will eat a wide variety of food and their prey at any time of the year consists largely of those species which are most abundant and easily caught (Coman and Brunner 1972). Mammals (particularly rodents and lagomorphs), birds, reptiles, amphibians, fish, insects, carrion, human garbage and plant material are all eaten. In areas of high rabbit density, rabbits are by far the most important food item. Similar results have been obtained in a more re- cent dietary study on feral cats (Jones and Coman personal communication). Usually cats hunt at night and peak ac- tivity is thought to be at evening or early morning. The diet of feral cats in Vic- toria varies markedly depending on the habitat. The results of a dietary survey carried out in 1969-70 in agricultural and forest areas are summarized in Table 3 (Coman and Brunner 1972). The greater reliance on native mam- mals in heavy forest is, no doubt, linked to the fact that such animals are usually more common in bush areas whilst mice and rabbits are less common. Disease Probably the most important disease transmitted to man and to domestic and free living animals by cats is tox- oplasmosis (Toxoplasma gondii). It can lead to serious foetal damage (rare in humans) if the mother is infected during pregnancy. It is also a fairly serious disease of livestock especially sheep in New Zealand and Tasmania and it must be assumed that feral cats play some part in its transmission. A wide range of native animals have been found to be infected with toxo- Table 3. Food items of 80 feral cats in Victoria expressed both as percentage by volume and as percentage occurrence Food item Agricultrual and Heavy forest pastoral land 2 Volume Occurrence Volume Occurrence MAMMALS 91.5 81.5 85.7 60.6 Introduced spp. Oryctolagus cuniculus 62.0 29.6 20.5 11.3 Mus musculus 27.0 40.7 11.8 TESS Ovis aries 1,5 3.7 0.0 0.0 Native spp. Pseudocheirus peregrinus 0.0 0.0 11.4 Lap Esha vulpecula and ) 0.0 0.0 6.6 1.6 Tichosurus caninus ) Rattus fuscipes 0.0 0.0 6.6 8.7 Rattus lutreolus 0.0 0.0 6.8 4.6 Macropus spp. 0.0 0.0 9.7 1.9 Schoinobates volans 0.0 0.0 4.0 1.9 Antechinus spp. 0.0 0.0 0.8 1.9 Sminthopsis spp. 0.0 0.0 0.3 1.9 Perameles nasuta 0.0 0.0 T 1.9 Unidentified 3.0 14.8 vi: Sa VEGETABLE MATTER F 25.9 28 52.8 INSECTS rT 14.8 0.8 15.1 BIRDS a TY 5.8 5.7 LIZARDS T 3.7 ih 1.9 FROGS 1.0 7.4 0.0 0.0 OTHER ITEMS 6.0 29.6 3.5 26.4 CAT FUR 3.0 14.8 0.2 20.7 HOUSEHOLD SCRAPS 0.0 0.0 Ys be T = trace January/February "1 plasmosis. The original spread of this disease is commonly linked with the presence of feral cats. The sexual stage of T. gondii can only mature in members of the cat family and the infec- tive oocysts are shed in their faeces (Butler 1979). Subsequently, these oocysts are picked up by grazing animals. This disease, found in sheep and other domestic animals, has also been found in several species of macropods, rodents, bandicoots, possums, dasyurids and in wombats, rabbits and birds (Attwood et al. 1975; Gibb et al. 1966; Munday 1972, 1978). The disease can kill infected animals when they are under stress, such as when food is in short supply (Arundel personal communication). Sparganosis is a disease caused by the larval stage of a tapeworm which is commonly found in feral cats. The intermediate stage of the parasite, called the sparganum, is very common in wild pigs and is also frequently encountered in smaller native animals. Man can get this disease but it is uncommon. If rabies ever came to Australia, the feral cat could act as a carrier but dog and fox would probably be more important in this regard. Economic damage Besides the transmission of various diseases, feral cats appear to cause little or no economic damage in the agricultural situation. Environmental aspects It is generally known that feral cats prey heavily on small indigenous mammals and birds in wildlife habitats. It is possible that feral cats may exert a detrimental effect on other small carnivores such as the tiger quoll, eastern quoll and the brush-tailed phascogale (Phascogale tapoataga) by direct competition for food. Certainly, the range and number of some of our smaller indigenous carnivores has decreased markedly since the advent of white man. The impact of predation by cats is difficult to assess, particularly in complex wilderness areas where foxes and feral dogs pose a similar threat. Ina relatively simple ecological system on Macquarie Island, cats caused the local 12 extinction of a ground nesting parakeet and it has been computed that the Macquarie Island cat population eats in excess of 50,000 birds per annum (Jones 1977). In areas containing endangered mammal or bird species every effort should be made to eradicate feral cats or limit their numbers. Control Although feral cats are not declared vermin under the Vermin and Noxious Weeds Act 1958, they are widely regarded as a pest animal and in some situations such as National Parks and Wildlife Reserves, active control has been attempted. Usually cage trapping has been used, but little research has been done on the effectiveness of this technique. At the moment various trap types and trapping methods are being evaluated. Cats may be poisoned using 1080 meat baits, but there are probably some hazards to other carnivores. In dense bush areas some success has been achieved by suspending small baits some 500 mm above the ground where raptores and small carnivores have less access. Like foxes, cats may be killed by shooting in conjunction with night spotlighting. The eyes shine very brightly at night and since the animals are mainly nocturnal in habit this technique can be used with some success. THE EUROPEAN RABBIT General Attempts were made to establish rabbits (Oryctolagus cuniculus L.) in Australia right from the commencement of European settlement. Five domestic rabbits were listed amongst the livestock brought by the First Fleet in 1788 (Stead 1935), Rabbits were mentioned in early reports from Fawkner’s settlement on the Yarra River at Port Phillip (Rolls 1969). Rabbits were also released on several islands around the Victorian coastline to provide food for shipwrecked sailors (Stokes 1846). The Henty family brought rabbits from Tasmania to Portland, in western Vic. Nat. Vol. 98 Victoria (Bassett 1954), long before the more well-known episode which followed. In 1859 about twenty-four wild and domestic rabbits were brought to Melbourne from England and established at ‘‘Barwon Park’’, the property of Thomas Austin, near Winchelsea. Although the details are uncertain, it is clear that these rabbits became established very well indeed. Of all our introduced mammals, the rabbit has probably had the greatest ecological impact in Australia. Distribution Rabbits are found virtually throughout the Australian mainland south of the tropic of Capricorn, in Tasmania and on numerous coastal islands. Isolated colonies of unknown status occur further north in Western Australia, the Northern Territory and Queensland. Rabbits are found in a wide range of environments including arid stony deserts, sub-alpine valleys, sub- tropical grasslands, wet coastal plains and a wide variety of Mediterranean- type habitats, In Victoria, they occur in habitats associated with nearly all types of land use including areas reserved for conservation purposes. Breeding The gestation period is about 28-30 days and mating can occur immediately after parturition. The kittens are born blind, without fur and in a nest which the doe prepares in a burrow. Young kittens first emerge at an age of about 15-20 days. Females become sexually mature at about four months of age and males at about five months. The following generalizations concerning rabbit reproduction are drawn from data collected by the C.S.1.R.O. Division of Wildlife Research from five environments (Myers 1970). The shortest and most sharply defined breeding season occurs in the sub-alpine region where reproduction is limited to the late spring and early summer months. In Mediterranean-type climates, however, reproduction occurs January/February in most months of the year with a prominent peak in spring. The average productivity of young per female per year ranged from 13.1 (sub- alpine N.S.W.) to 29.4 (Mediterranean N.S.W.) and the mean numbers per litter (in embyro stage) ranged from 4.49 (arid N.S.W.) to 5.65 (Mediterranean N.S.W.). In summary, the population in the Mediterranean habitat exhibited a markedly higher capacity for increase — almost twice that of the next highest site (sub-tropical Queensland) and approximately eighteen times that of the lowest site (sub-alpine N.S.W.). Food and feeding Rabbits are more selective than sheep in their grazing habits (Myers and Poole 1963; Farrington and Mitchell 1971). Their natural choice is for soft, green grass but when this becomes unavailable they choose food which is easily eaten and masticated, avoiding plants with disagreeable aromatic odours and tastes. In most instances such feeding coincides with a high protein intake. In drought conditions their diet becomes protein and energy deficient and this imposes a considerable stress on the animals. Diseases Diseases in wild rabbits are no direct threat to humans. Dogs, however, can become infected with the helminth parasites Taenia pisiformis and Taenia serialis by eating infected rabbits (Coman 1972a). The cysts of the latter parasite in rabbits are often mistakenly identified as hydatid cysts (Davies and Nicholas 1977). Hydatids has not been reliably recorded in rabbits in Australia. Occasionally ectoparasites of rabbits are capable of transmitting microbial pathogens to man. The associated diseases include mange, scabies, dermatitis and plague (Yunker 1964; Pegg 1970). The most famous disease associated with rabbits is the viral disease myxomatosis. Beginning from an experimental site near Corowa in 1950, a spectacular epizootic decimated rabbit populations and for the first time brought rabbits under control (Ratcliffe et al. 1952; Brereton 1953). It is expected 13 that myxomatosis will continue as a moderately severe disease of rabbits for some time to come (Edmonds 1972), Economic damage Although generally acknowledged, the economic damage caused by rabbits has not been well documented. However, the real extent of earlier losses was clearly revealed by the enormous increase in wool and meat production which followed the suppression of rabbits by myxomatosis (Reid 1953). Even though the rabbit problem has been greatly reduced, the resources still required for control demonstrate the continuing economic impact of this species. Some commercial benefit is derived from the sale of carcasses and skins of wild rabbits, but the commercial production of domestic rabbits is still not permitted in Victoria. Environmental damage The impact of rabbits on the Australian environment could well be described as disastrous. Rabbits have significantly altered the botanical composition of extensive areas of natural habitat. This is mainly because they feed on certain species of plants at critical stages of development such as seeding and _ seedling establishment (Myers and Poole 1963). These findings have been supported and extended by subsequent studies (Cochrane and McDonald 1966; Churchill 1972). Because of these ecological changes associated with high population numbers, rabbits have been blamed for the disappearance of the greater bilby, Macrotis lagotis, and the pig-footed bandicoot, Chaeropus ecaudatus, and for putting many other species under stress. Studies have shown that rabbits have had a drastic effect on the ecology of islands and that significant regeneration of the original vegetation can occur after the removal of rabbits (Norman 1967, 1970). A further concern is the severe soil erosion which has occurred due largely to the grazing and burrowing activities of rabbits. 14 The control of rabbits in natural areas without undue disturbance of native flora and fauna presents a major challenge to those who manage land for conservation purposes. Control It was not long after the initial rapid spread of rabbits that their threat as a pest species became obvious. By 1869 it had been suggested that rabbit control be made compulsory in Victoria, and in 1880 the Rabbit Suppression Act was drawn up (Rolls 1969). Today, the main methods of rabbit control are poisoning, fumigation, warren-ripping, harbour destruction, night shooting and exclusion fencing. Biological control through myxomatosis continues to be of great assistance (Edmonds 1972; Tighe ef al, 1977; Shepherd et a/. 1978). In recent years the European rabbit flea (Spilopsyllus cuniculi Dale) has been introduced as an additional vector of the myxoma virus (Shepherd and Edmonds 1976, 1979). Advice on the most suitable methods of control in particular situations is readily available from local Inspectors of Lands throughout Victoria and from the Keith Turnbull Research Institute at Frankston. FERAL PIGS General Feral pigs (Sus scrofa) in Australia are derived from domestic stock and they have established populations of high density in a wide range of habitats, chiefly in New South Wales, Queensland and the Northern Territory. Some feral pig colonies were established prior to 1870 but most are more recent in origin. Feral pigs are a declared pest species in Victoria, New South Wales, Western Australia and Queensland. Elsewhere in Australia there is no legislation on feral pigs. Distribution Although feral pigs can be found in all States, they are of major significance only in New South Wales, Queensland and the Northern Territory. In New South Wales the greatest density of pigs Vic. Nat. Vol. 98 is located on the north-western river systems, flood plains and marshes. Populations of up to eighty pigs per square kilometer have been recorded (O’Grady and Hone personal communication). High population densities also occur in large areas of Queensland but there is no detailed information on distribution. In the Northern Territory, feral pigs are found only in the north of the State. There, the distribution of pigs is mainly restricted to the river systems. In Victoria, two main population groupings can be recognized. The majority of animals are found in flood country adjacent to the Murray River in northern Victoria. The other main habitat is in the Eastern Ranges. Smaller colonies are also found is confined situations throughout the remainder of the State. Breeding The breeding season of feral pigs in Australia is generally unrestricted. Sows begins breeding between 6 and & months of age if their live-weight exceeds 30 kg. The mean number per litter at birth is 6.5 and the mean number weaned varies from 0 — 4,5 depending on seasonal conditions. Two litters can be weaned in 12-14 months. Populations of pigs studied in New South Wales have a potential rate of increase of about 300% per annum if resources are not severely limiting. This figure allows for normal hunting pressures. Food and Feeding Feral pigs have definite food preferences. Succulent green vegetation forms the bulk of the diet but if this becomes unavailable they become increasingly dependent on plant roots and animal material. Grain crops are particularly attractive even when there is an abundance of green vegetation. The animal tends to be nocturnal particularly during hot weather or when the population is disturbed. Like domestic pigs, the feral pig has a poor tolerance of high temperature and when temperatures exceed 30°C it must drink water daily. January/February Disease The major importance of feral pigs is their potential as a reservoir of exotic diseases particularly foot and mouth disease, swine fever, rinderpest, and trichinosis. This importance is compounded when the distribution of feral pigs is considered, particularly in northern Australia near possible points of entry of diseases from Asia. Economic damage Feral pigs cause losses in the pastoral industry and in grain and sugar production. In the pastoral industry the main pig problem occurs during the lambing season particularly in north- western New South Wales. Moule (1954) and Plant et al. (1978) have attributed fairly heavy lamb losses in particular flocks in Queensland and New South Wales to feral pig predation. In the investigation by Plant et al. (1977), it was estimated that in one season a total of over 600 lambs was killed by feral pigs from 1,422 lambing ewes. Pigs also ruin pastures by grazing and rooting, they break down fences and cause damage to water installations and bore drains. Pigs have a significant effect on grain production in New South Wales and Queensland. In Victoria crop damage occurs to a lesser extent. Individual farmers may suffer heavy losses from time to time. Losses result not only from consumption of grain and foliage but also because areas of crops are destroyed by trampling. Losses in sugar production are mainly reported from northern Queensland. Environmental aspects There is little information available on the effects of feral pigs on the natural environment. Pigs living in forests and swamps can cause considerable damage rooting and wallowing and by spoiling water. There may be a significant effeci on ground nesting birds because of damage to nesting sites and habitat. Although studies of pig food habits have not yet indicated predation on wildfowl or eggs, such damage may occur (Giles personal communication). In the high plains of Kosciusko, pigs feed 15 extensively on tuberous plants and this may cause damage to individual species and plant communities. Furthermore, these disturbances are usually followed by an invasion of weedy exotic plants (Wimbush personal communication). Pigs preying on lambs are likely to prey also on native animals for food. Tufts of hair of possum, koala and kangaroo have been found in droppings of pigs. It is likely that pigs pose a_ serious ecological problem in many areas and there is a definite need to investigate this possibility. Control Useful methods of control are trapping, poisoning and shooting. Traps are simply small yards constructed of weld-mesh supported by steel fencing posts. Bait is used to attract the pigs into the traps and various devices are used to prevent the pigs from escaping. For poisoning, pellets or grain are us- ed as bait material. Meat bait injected with poison is also effective. Shooting is best applied where small populations are restricted to certain watering points or as an ancillary to trapping and poisoning. Acknowledgements The authors wish to thank colleagues Dr. B. Coman and Messrs. J. Edmonds, E. Jones and I. Nolan for their assistance with contributions of in- formation, helpful discussions and critical reading of the manuscript. References Anderson, R. (1978), Gold On Four Feet. Ronald Anderson and Associates: Melbourne. Anon. (1977). Domestic animals gone bush. Ecos No. 13: 10-18. Attwood, H.D., Woolley, P.A. and Rickard, M.D. (1975). Toxoplasmosis in dasyurid marsupials. J, Wildl. Dis. 11: 543-551, sa M. (1954). The Hentys, Oxford University Tess. Bolton, B.L. and Latz, P.K. (1978). The western hare-wallaby, Lagorchestes hirsutus (Gould) (Macropodidae), in the Tanami Desert. Aust. Wildl. Res. 5 (3): 285-293, Brereton, J, Le Gay (1953). Initial spread of myxomatosis in Australia. Nature 172: 108, 16 Brunner, H., Lloyd, J.W. and Coman, B.J. (1975). Fox scat analysis in a forest park in South- Eastern Australia. Aust. Wildl. Res. 2: 147- 154. Brunner, H., Harris, R.V. and Amor, R.L. (1976). A note on the dispersal of seeds of blackberry (Rubus procerus P.J. Muell.) by foxes and emus. Weed Res. 16: 171-173. Brunner, H., Amor, R.L. and Stevens, P.L. (1976). The use of predator scat analysis in a mammal survey at Dartmouth in North-Eastern Vic- toria. Aust. Wildl. Res. 3: 85-90. Brunner, H., Wallis, R.L. and Voutier, P.F. (1977). Locating and trapping the Broad-toothed rat (Mastacomys fuscus Thomas) at Powelltown. Vic. Nat. 94: 207-210. Butler, R. (1979). Toxoplasmosis in Parma Wallabies (Macropus parma) at the Royal Melbourne Zoo, Aust. Mammal Soc. Inc. Bull. 5 (2): 29, Churchill, D.M. (1972). Report on Rabbit Grazing in Wyperfeld National Park. National Her- barium, Melbourne. 2 pp. Cochrane, G.R. and McDonald, N.H.E. (1966). A regeneration study in the Victorian Mallee. Vic. Nat. 83 (9): 220-226. Coman, B.J. (1972a). Helminth parasites of the dingo and feral dog in Victoria with some notes on the diet of the host. Aust. Vet. J. 48; 456-461. Coman, B.J. (1972b). A sylvatic cycle for the hydatid tapeworm (Echinococcus granulosus) in remote areas of eastern Victoria. Aust. Vet. J, 48: 552-553. Coman, B.J, and Brunner, H. (1972). Food habits of the feral house cat in Victoria. J. Wildl. Manage. 38: 848-853. Coman, B,J. (1973a). The diet of red foxes, Vulpes vulpes L., in Victoria. Aust. J. Zool. 21: 391-401. Coman, B.J, (1973b). Helminth parasites of the fox (Vulpes vulpes) in Victoria. Aust. Vet. J. 49: 378-384. Croft, J.D. and Hone, L.J. (1978). The stomach contents of foxes, Vulpes vulpes, collected in New South Wales. Aust. Wildl. Res. 5: 85-92. Davies, P. and Nicholas, W.L. (1977). The helminth parasites of dogs in the Goodradigbee Shire of New South Wales, Aust. Ver. J. 53: 247-248. Deer Advisory Council of Victoria (1979). Deer in Australia, Fisheries and Wildlife Division, Ministry for Conservation, Victoria, Edmonds, J.W. (1972). Myxomatosis in rabbit con- trol. Vic. Res. Vol. 14, No. 4, December 1972 — February 1973, 1 p. Farrington, P. and Mitchell, A. (1971). The Effects of Grazing by Sheep and Rabbits in a Victorian Forest 1961-1971. Soil Conservation Authori- ty, Melbourne. Gibb, D.G.A., Kakulas, B.A., Perret, D.H. and Jenkyn, D.J. (1966). Toxoplasmosis in the Rot- (nest Quokka (Setonix brachyurus), Aust. J. exp. Biol. med. Sci. 44: 665-672. Jones, E. (1977). Ecology of the Feral Cat, Felis catus (L.), (Carnivora:Felidae) on Macquarie Island, Aust. Wildl. Res. 4: 249-262. McFarlane, D. (1964), The effect of predators on perinatal lamb losses in the Monaro, Oberon and Canberra districts. Wool Technol. Sheep Breed. 11: 11-14, Marshall, A.J, (1966). Unknown Australia. Aust. Nat. Hist. 15: 169-173. Vic. Nat. Vol. 98 Melbourne and Metropolitan Board of Works (1977), Metropolitan Farming Study by Aber- deen, Hogg and Associates Pty. Ltd., Melbourne. Aberdeen, Hogg, 1977, p. 81-83, Munday, B.L, (1972). A serological study of some infectious diseases of Tasmanian wildlife. J. Wildl. Dis. 8: 169-175. Munday, B.L. (1978), Marsupial Disease In. Sydney University. Post graduate Committee in Veterinary Science. Proceedings No. 36 of a course for Veterinarians. (The J.P. Stewart Course for 1978) Sydney, 1978. p, 335-385. Myers, K. and Poole, W.E. (1963). A study of the biology of the wild rabbit, Oryctolagus cuniculus (L.), in confined populations. IV. The effects of rabbit grazing on sown pastures. J. Ecol. $1: 435-451. Myers, K. (1970). The rabbit in Australia. In. Dynamics of populations. Proceedings of the Advanced Study Institute on ‘Dynamics of Numbers in Populations’ Oosterbeek, the Netherlands, 7-18 Sept, 1970. Centre for Agricultural Publishing and Documentation, Wageningen. pp. 478-506, Newsome, A.E., Corbett, L.K., Best, L.W. and Green, B. (1973). The dingo. A.M.R.C. Review No. 14: 1-11. Norman, F.1. (1967). The interactions of plants and animals on Rabbit Island, Wilson's Promontory, Victoria. Proc. Roy. Soc. Vic. 80: 193-200. Norman, F,1I. (1970). Ecological effects of rabbit reduction on Rabbit Island, Wilson’s Promon- aes Victoria. Proc, Roy. Soc. Vic, 83: 235- Pegg, E.J. (1970). Three ectoparasites of veterinary interest communicable to man. Med. Biol. Illus. 20: 106-110, Plant, J.W., Rees, D., Marchant, R.S. and Mit- chell, T.D. (1977). Feral pigs, predators of lambs. Agric. Gaz. N.S. W. 88 (5): 11-13. Ratcliffe, F.N., Myers, K., Fennessy, B.V. and Calaby, J.H. (1952). Myxomatosis in Australia. A step towards the biological control of the rabbit, Nature 170: 7. Rathore, A.K. (1980). Assessment of an improved method of delivery system of Compound 1080 for wild canid pest control. Aust. Mammal Soc. Bull. 6 (2):58. Reid, P.A. (1953). Some economic results of myx- omatosis. Quart. Rev. Agric. Econ. 6:93. Rolls, Eric C, (1969). They AJ] Ran Wild. Angus and Robertson, Sydney. Scott, P.P. (1972), The cat. Chapter 33 In The UFAW Handbook on the Care and Mange- ment of Laboratory Animals. Fourth edition. bri Livingstone: Edinburgh and Lon- ion. Shepherd, Rosamond C.H. and Edmonds, J.W. (1976). The establishment and spread of Spilopsyllus cuniculi (Dale) and its location on the host, Oryctolagus cuniculus (L.), in the Mallee Region of Victoria, Aust. Wildl. Res. 3: 29-44, Shepherd, Rosamond C.H., Edmonds, J.W., Nolan, I.F. and Gocs, A. (1978). Myxomatosis in the Mallee region of Victoria, Australia. J. Hyg, Camb. 81: 239-243. Shepherd, Rosamond C.H. and Edmonds, J.W. (1979). Myxomatosis: the release and spread of the European rabbit flea Spi/opsyllus cuniculi (Dale) in the Central District of Victoria, J. Hyg. Camb, 83: 285-294. Stead, D.G, (1935), The Rabbit in Australia. Winn and Co., Sydney. Stokes, J.L. (1846). Discoveries in Australia. Vol. Il, London. Tighe, F.G., Edmonds, J.W., Nolan, I.F., Shepherd, Rosamond, C.H. and Gocs, A. (1977). Myxomatosis on the Western Plains of Victoria. J. Hyg, Camb. 79: 209-217. Whitehouse, S.J.O. (1977). The diet of the dingo in Western Australia. Aust. Wildl. Res. 4: 145-150. Yunker, C.E. (1964). Infections of laboratory animals potentially dangerous to man: ec- toparasites and other arthropods, with em- phases on mites. Lab, anim. Care 14 (5): 455- 465. LT Victorian Naturalist Subject Index This 286 page comprehensive index to the subjects covered in the Naturalist from Vol. 1. to Vol. 95, 1884-1978 is available from the Book Sales Officer at meetings or by writing to:— Naturalist Subject Index, F.N.C.V., National Herbarium, Birdwood Avenue, South Yarra, Victoria. Price $10 (members); $14 to others. TY NEW BOOK DECEMBER 1980 ‘*& Field Guide to Birds of Australia.” by Graham Pizzey. Illustrated by Roy Doyle 460 pages. 700 Species illustrated. Distribution Maps. Price $25.00 (Discount to Members) Postage 50km $1.00 Vic. $1.40 Order from Sales Officer F.N.C.V. January/February 17 Trout Introduced into South-eastern Australia: Their Interaction with Native Fishes By P.D, JACKSON* Introduction The practice of introducing non- indigenous animals into North America and Australasia was particularly characteristic of the 19th Century when people migrated from Europe in huge numbers (McDowall 1968). Fishes were selected by these settlers for those spor- ting or food qualities thought to be lack- ing in fishes of the new lands and with no thought to the possible effects of in- troduced fishes on the native species of fish. Indeed only recently have some biologists questioned the wisdom of in- troducing exotic species of fish and begun to provide data on the relation- ships between native and introduced fishes (e.g. McDowall 1968). In the present paper, the introduc- tions of brown trout Salmo trutta and rainbow trout S. gairdneri from the Northern Hemisphere into Australia are documented, and the effects of these in- troduced species on the native fish populations are reviewed. History of Trout Introductions Five species of salmonid have been in- troduced into Australia: the brown trout; rainbow trout; brook trout (Salvelinus fontinalis); Atlantic salmon (Salmo salar); and quinnat salmon (Oncorhynchus — tshawytscha). Although populations of all these species still exist in Australian hat- cheries, only brown trout and rainbow trout have established self-reproducing populations in the wild. The introduction of brown trout to Australia is the earliest known introduc- tion of the species beyond its native range in Europe (MacCrimmon and Marshall 1968). Trout ova were first successfully shipped to Tasmania in 1864 after four attempts between 184] * Sport Fisheries Section, Fisheries and Wildlife Division, Arthur Rylah Institute for Environmental Research, 123 Brown Street, Heidelberg, Vic, 3084, 18 and 1862 (Roughley 1951). Three hun- dred brown trout were hatched from about 1000 ova and 38 were liberated in the Plenty River. The remainder were re- tained in the hatchery pond, and their progeny have been used to stock the rivers of Tasmania and mainland Australia, Rainbow trout were first introduced in 1894 (Roughley 1951) when fertilized ova were transferred from New Zealand to New South Wales. The species had been introduced to New Zealand from their native range on the Pacific coast of North America in 1883. Biology and Present Distribution of Trout in South-eastern Australia. Brown trout is a_ thick-bodied, streamlined species known to reach at least 900 mm in length and 14 kg in weight in Australia (McDowall 1980). It occurs most commonly in cool (upper lethal temperatures occur between 22.5 and 25.3°C according to Frost and Brown 1967) and well oxygenated waters of both rivers and lakes. However it re- quires clear, flowing water and a gravel substrate for reproduction. Eggs are deposited in depressions in the gravel in late autumn to winter (May to August). Recently hatched young initially form shoals in shallow fast-flowing sections of river but soon become solitary and strongly territorial. Brown trout are car- nivorous, feeding on a variety of in- vertebrates and small fishes. Rainbow trout is similar in shape to brown trout and reaches about 775 mm in length and 8 kg in weight in Australia (McDowall 1980). Its biology is essen- tially similar to brown trout. Rainbow trout may spawn a little later and tend to be more successful in lakes than rivers. Where the two species occur together brown trout dominates. As the biology of brown and rainbow trout is essentially similar, previous Australian authors (e.g. Weatherley and Lake 1967, Tilzey 1977) have grouped Vic. Nat. Vol. 98 them together under the single heading ‘trout’. The same convention is followed here except where specific examples are given. Trout were first introduced into rivers and lakes by acclimatisation societies. To quote Tilzey (1977), ‘‘Such was the zeal of early acclimatisationists that trout were introduced into most suitable river catchments before 1900’’. Later, and with equal fervour, the State fisheries departments continued stock- ing streams, lakes and reservoirs with trout. Trout are still reared in govern- ment hatcheries and many waters are still stocked regularly. The success of such stockings is debatable. The survival rate of trout in streams already contain- ing wild trout is very low. Nicholls (1958) showed that in a Tasmanian stream only about 2% of hatchery- released fish reached the age of 3 years. Lake (1957) found the situation to be similar in New South Wales waters. Recently, Cadwallader and Tilzey (1980) have questioned the wisdom of stocking many of the reservoirs in Victoria and New South Wales, particularly those below 900 m in altitude, where mortality rates are often high and returns to anglers low. Due to the spawning requirements and temperature tolerances of trout, self-reproducing populations now occur mainly in streams of the south-eastern highlands of mainland Australia, at altitudes above about 600 m and in most highland streams in Tasmania (Fig. 1). Sound arguments for the success of trout in the Australian environment are reviewed by Weatherley (1974) and Tilzey (1977). Briefly, the main reasons according to Tilzey (1977) are: the physicochemical and _ biological similarities between certain Australian waters and the trout’s ancestral waters, the availability of food, the virtual absence of parasites and diseases, and minimal competition from native fishes (see below). The distribution of trout is still expan- ding because weirs and impoundments provide cool waters which enable trout to survive in streams where summer water temperatures would normally be lethal to them. Water released from January/February WA Trout distribution Fig. 1. Distribution of trout in South-eastern Australia. deep impoundments during summer can be as much as 11°C colder than ambient water temperature, which it may not re- join for up to 100 km (Buckmaster et al 1979). It may be noted here that such alterations of temperature and flow regimes have markedly depleted native fish stocks (Cadwallader 1978). Interaction with Native Fishes Whilst a decline in numbers and distribution of native fishes is widely acknowledged (Frankenberg 1966, Lake 1971) opinions are divided as to the reasons. Some (e.g. Weatherley and Lake 1967, Lake 1971) have contended that man-made changes to the environ- ment, for example, alterations to the hydrological regimes of rivers, clearing of snags, pollution and so on have been the main factors. Others (e.g. Frankenberg 1966, Jackson 1975, Tilzey 1976), whilst acknowledging that man’s modifications of the environment have had a deleterious effect on native fishes, have maintained that the effects of fish introductions have also been con- siderable. In the present paper the detrimental effect of environmental 19 modifications other than the introduc- tion of trout is accepted, and the discus- sion is limited to a review of the evidence of interactions between trout and native fishes. Table | lists the most common native species recorded from tableland waters above 600 m on the mainland and from what are now considered the trout waters of Tasmania. Of these, only river blackfish, Macquarie perch and galax- iids have been reported to spawn in such waters. Murray cod, tupong, Australian and Tasmanian smelt and pigmy perch inhabit these waters only occasionally, generally occurring further downstream. Thus of the native species that attain a moderate size, only five are found in what are now trout waters; short-finned eel, long-finned eel, river blackfish, Australian grayling and trout cod, Both species of eel are piscivorous (Beumer 1979). Butcher (1945) found river blackfish to be mainly insectivorous and Jackson (1978a) concluded that fish did not form a significant part of the river blackfish’s diet. The Australian grayling is probably omnivorous, feeding on in- sects (Jackson 1976) and on algae (Bishop and Bell 1978). Consequently introduced trout were probably preyed on by few indigenous fishes other than eels. Murray cod and tupong have been reported to eat fish (Lake 1971, Nicholls 1958) and may have preyed on trout in waters at lower altitudes (Tilzey 1977). This comparative lack of indigenous piscivorous fishes has probably led to several species being highly susceptible to predation, through not having evolv- ed or retained predator escape mechanisms (Tilzey 1977). When trout were introduced into rivers, native fishes were freely available to them as prey and trout had little competition from larger native fishes. Frankenberg (1966) was the first to comment on the fragmented distribution of galaxiids and to suggest that this was due to trout. Specifically he cited the headwaters of the Kiewa river where trout occupied the main body of the stream and galaxiids occupied places in- accessible to trout, such as above water- falls. However, there are very few data on the relationships between trout and galaxiids in general. Evidence is strong for only one species, the mountain galaxias (Galaxias olidus). The mountain galaxias is a small species, reaching only about 10-13cm in length (McDowall 1980), with a widespread, if fragmented distribution in highland streams. It is most common- ly found in small headwater tributaries where it occurs in loose shoals in pool areas or solitarily amongst rocks in more shallow areas. It is largely insectivorous Table |. Native Fishes occurring in Trout Waters in Australia Common name Scientific name + Maximum recorded : i. length (mm) *River blackfish Gadopsis marmoratus Richardson 625 *Short-finned eel Anguilla australis Richardson 900 *Long-finned eel Anguilla reinhardtii Steindachner 1500 Macquarie perch Macquaria australasica Cuvier and Valenciennes 370 Trout cod Maccullochella macquariensis (Cuvier and Valenciennes) 685 Murray cod Maccullochella peeli (Mitchell) 1800 *Australian grayling Prototroctes maraena Gunther 300 *Tupong Pseudaphrites urvilli (Cuvier and Valenciennes) 300 Silver perch Bidyanus bidyanus (Mitchell) 400 *Galaxias spp. e.g. Mountain galaxias Galaxias olidus Gunther 130 Climbing galaxias G. brevipinnis (Gunther) 278 Spotted mountain G, truttaceus Valenciennes 200 galaxias Australian smelt Retropinna semoni Weber 100 *Tasmanian smelt Retropinna tasmanica McCulloch 67 *Pigmy perch Nannoperca australis Gunther 82 + Measurements taken from McDowall (1980) * Occurring in Tasmanian trout waters (All species apart from R. tasmanica occur on the mainland) 20 Vic. Nat. Vol. 98 feeding on both aquatic and terrestrial insects and appears to spend its entire life cycle in freshwater (Fletcher 1979). Jackson and Williams (1980), in a study of the distribution of brown trout and native species in the upper reaches of the Yarra River, showed that moun- tain galaxias were present only in those tributaries where brown trout were ab- sent. Furthermore, in many _ small tributaries trout were the only fish pre- sent, suggesting the elimination by this species of all native fishes. There is no evidence to suggest that such habitats cannot support native fishes. Other authors (e.g. Tilzey 1976, Cad- wallader 1979, Fletcher 1979) have also documented the mutually exclusive distributions of trout and mountain galaxias in highland streams on mainland Australia. Tilzey (1976) was able to document the invasion by rain- bow trout of a small stream flowing into Lake Eucumbene, New South Wales. In 1971 the stream contained only moun- tain galaxias upstream and downstream of a waterfall. By 1974 rainbow trout had invaded the section downstream of the waterfall and were the only fish pre- sent. The mountain galaxias population upstream of the falls was similar to that present in 1971 suggesting that the presence of rainbow trout was the sole environmental factor causing the disap- pearance of mountain galaxias. Fletcher (1979) has attempted to fur- ther investigate the interactions between trout and mountain galaxias by ex- perimentally introducing brown trout into an enclosed section of Watchbox Creek, Strathbogie Ranges. Both the ex- perimental and a control section con- tained only mountain galaxias of similar numbers and size range at the com- mencement of the experiment. After four months, the galaxias population in the experimental section was con- siderably depressed, both in terms of numbers and weight, in comparison with the control section. There is thus growing evidence to sug- gest that trout is incompatible with mountain galaxias. The mechanisms of this negative interaction are not clear. Certainly, the two species show con- siderable overlap in diet (Fletcher 1979) January/February and competition for food must occur. Furthermore, mountain galaxias feeds on the bottom and in the water column in a similar manner to trout and direct competition, where there is direct con- tact between individuals of the two species, may occur. Trout may therefore inhibit the mountain galaxias from feeding. Mountain galaxias also occurs in the diet of trout (Bishop and Tilzey 1978, Fletcher 1979) and direct preda- tion may be an important factor. Flet- cher (1979) has suggested that the moun- tain galaxias lacks any predator avoidance mechanisms but more work is needed to determine this fully. The relationships between trout and other galaxiid species are much less clear. There is some evidence to suggest that the distribution of the climbing galaxias (G. brevipinnis) has been af- fected by trout (Andrews 1976, Jackson and Williams 1980). The only known locality of the Swan galaxias (G. fontanus), a recently described species from Tasmania, is above a waterfall barrier which separate the population from brown trout (Fulton 1978). Data are few on the relationships be- tween trout and native fishes other than galaxiids. Jackson (1978a) has discussed the relationship between brown trout and river blackfish, a species that ap- pears able to co-exist with trout, (Frankenberg 1974, Jackson and Williams 1980). Although the diets of the two species are very similar they may avoid direction competition because the two species occupy somewhat different habitats, river blackfish preferring the slower-flowing stretches of river. The decline of river blackfish in recent years may, at least in part, be explained by the de-snagging of rivers because the species spawns in submerged hollow logs (Jackson 1978b). The short-finned eel also appears able to co-exist with trout (Jackson and Williams 1980). Although there are no data on the relationship between trout and eels in the Australian environment, considerable research done in New Zealand, where short-finned eels also occur (e.g. Burnet 1968, 1969, Hopkins 1970, Skrzynski 1974) has shown that the relationship is complex and varies 21 from river to river. However, there was no evidence to suggest that the introduc- tion of trout had been detrimental to eel stocks; in fact some evidence was presented to show that the removal of eels from a section of river may lead to an increase in the number of trout. Studies of feeding habits (Burnet 1968) showed that larger eels did include trout in their diet. The relationships between trout and any of the other native species, Mac- quarie perch, Australian grayling and trout cod, are difficult to ascertain because all three are now rare and few biological studies were made when these fishes were much more abundant. Macquarie perch were once common in the upper reaches of the Murray- Darling System but their distribution and abundance is now greatly reduced (Cadwallader 1977, 1978), Macquarie perch and trout have similar diets (McKeown 1934, Butcher 1945). Adult Macquarie perch in aquaria obtain food by a sucking action and normally at- tempt to take only items within their im- mediate vicinity (Cadwallader and Eden 1979). Examination of the stomach con- tents of Macquarie perch collected from the wild indicated that they are basically bottom feeders which obtain only a small portion of their food at the water surface. As such they are less ag- gressive feeders than trout which seize their prey and feed in the water col- umn as well as on the bottom (Frost and Brown 1967). Therefore Macquarie perch may not have been able to com- pete successfully with trout for food. Furthermore trout eat small Macquarie perch (Butcher 1967). Australian grayling were once com- mon (Tunbridge 1972) and often taken by anglers, but even early this century the species was rare in New South Wales and although once exceedingly plentiful in the Yarra River, Victoria, had become very scarce (Stead 1903). Since that time their numbers have continued to decline. Recent surveys undertaken by the fisheries departments of New South Wales, Victoria and Tasmania have located several previously unrecorded populations but the species must still be regarded as rare. The 22 reasons for its decline are unknown, but its disappearance corresponds closely with the introduction of trout and with man’s concurrent modifications to the stream habitat. In particular, the damm- ing of rivers must be detrimental to the Australian grayling which is probably anadromous (spends part of its life cycle at sea and migrates to freshwater to spawn) and needs an_ unrestricted passage up and down the river systems it inhabits. Trout cod were formerly found in many waters throughout the Murray- Darling River system (Berra 1974), but are now collected consistently in only one stream, Seven Creeks, a small tributary of the Goulburn River near Euroa, Victoria. Although little is known of the biology of the species, Cadwallader (Fisheries and Wildlife Division, pers. comm.) believes that the introduced trout have had a detrimental effect on trout cod, particularly in north-eastern Victoria where trout now dominate streams previously the domain of trout cod. Cadwallader’s (1978) observations of young (1-6 months old) trout cod in aquaria indicate that the species establish territories in a similar manner to trout, and field observations indicate that both species have similar habitat requirements. What little data are available on the food of trout cod in- dicates an overlap with the diet of trout. Conclusions With few exceptions, information on the relationships between trout and native fishes is fragmentary and in- conclusive. So little is known about the biology and previous distribution of native fishes that it is difficult to say ex- actly what the effects of trout have been. Perhaps one of the most obvious detrimental effects is that until recently, the resources of State fisheries depart- ments were channelled only in one direc- tion and at the expense of research of native fishes. Consequently little work was done on native species when they were still abundant. Although information on the relation- ships between trout and native species is scarce, clearly the mountain galaxias is particularly susceptible to displacement by trout. Galaxiids appear to be suscep- Vic, Nat. Vol. 98 tible to displacement by predatory game fish throughout their natural range. McDowall (1968) concluded that trout were incompatible with several New Zealand galaxiids, and Jubb (1965) reported that populations of South African species of galaxiids had been detrimentally affected by the introduc- tion of predatory game fish. No data are available from South Ameria where trout have been introduced into waters where galaxiids occur. Acknowledgements I would like to thank Drs D. Evans and J. Beumer (Fisheries and Wildlife Division, Victoria) for their comments on the manuscript. Alicia McShane prepared the figure. REFERENCES Andrews, P.A. (1976). A revision of the Family Galaxiidae (Pisces) in Tasmania. Aust. J. Mar. Freshwater. Res. 27; 297-349. Beumer, J. P. (1979). Feeding and movement of Anguilla australis and A. reinhardtii in Macleods Morass, Victoria, Australia. J. Fish Biol. 14: 573-592. Berra, T. M. (1974). The trout cod, Maccullochella maquariensis, a rare freshwater fish of eastern Australia, Biol. Cons, 6: 53-56. Bishop, K. A. and Bell, J. D. (1978). Aspects of the biology of the Australian gray- ling Prototroctes maraena Gunther (Pisces: Prototroctidae). Aust. J. Mar. Freshwater Res. 29: 743-761. Bishop K. A. and Tilzey, R.D.J. (1978). Welcome Reef Project Environmental Study: Aquatic Life, M.W.S.D.B., Sydney. Buckmaster, D. E., Hastings, |. and Rogan, P.L. (1979). Inquiry into water allocations in nor- thern Victoria. Fish. Wild/. Pap. No. 21. Burnet, A. M. R. (1968). A study of the relationship between trout and eels in a New Zealand stream. Fish. Tech. Rep. N.Z. No. 26. Burnet, A. M. R. (1969). A study of the interrela- tion between eels and trout, the invertebrate fauna and the feeding habits of the fish. Fish. Tech. Rep. N.Z. No. 36. Butcher, A. D. (1945). The food of indigenous and non-indigenous freshwater fish in Victoria with 2 te teference to trout. Fish, Pamphl. Vic. 0. 2. Butcher, A. D. (1967). A changing aquatic fauna in a changing environment. JUCN Publs., New Series, 9: 197-218. Cadwallader, P. L. (1977). J. O. Langtry’s 1949 — 50 Murray River investigations. Fish. Wildl. wap. Victoria. No. 13. Cadwallader, P. L. (1979). Distribution of native and introduced fish in the Seven Creeks River System, Victoria. Aust. J. Ecology, 4: 361- 385. January/February Cadwallader, P. L. and Tilzey, R. D. J. (1980), The role of trout as sport fish in impoundment waters of Victoria and New South Wales, Aust. Soc. Limnol. Bull. 7: 17-29. Fletcher, A. R. (1979). Effects of Salmo trutta on Galaxias olidus and macroinvertebrates in stream communities, M.Sc. thesis, Monash University. Frankenberg, R. (1966). Fishes of the family Galax- iidae. Aust. Nat. Hist, 15; 161-164. Frost. W. E. and Brown, M. E. (1967). The Trout, (Collins: London). Fulton, W. (1978), A new species of Galaxias (Pisces: Glaxiidae) from the Swan River, Tasmania. Records of the Queen Victoria Museum. 63; 1-8. Hopkins, C. L. (1970). Some aspects of the bionomics of fish in a brown trout nursery stream. Fish. Res, Bull, N.Z. No. 4. Jackson, P. D, (1975), Bionomics of brown trout (Salmo trutta Linnaeus 1958) in a Vic- torian stream with notes on interactions with native fishes. Ph.D, thesis, Monash University. Jackson, P. D. (1976). A note of the food of the Australian grayling, Proftotroctes maraena Gunther (Galaxioidei: Prototroctidae). Aust. J, Mar, Freshwater Res, 27: 525-528. Jackson, P. D. (1978a). Benthic invertebrate fauna and feeding relationships of brown trout. Salmo trutta Linnaeus, and river blackfish, Gadopsis marmoratus Richardson, in the Aberfeldy River, Victoria. Aust. J. Mar. Freshwater Res. 29: 725-742. Jackson, P. D. (1978b). Spawning and early development of the river blackfish, Gadopsis marmoratus Richardson (Gadopsiformes: Gadopsidae), in the McKenzie River, Vic- toria. Aust. J. Mar. Freshwater Res. 29: 293- 298, Jackson, P. D. and Williams, W. D. (1980). Effects of brown trout, Sa/mo trutta Linnaeus, on the distribution of some native fishes in three areas of southern Victoria, Australia. Aust. J. Mar. Freshwater Res, 31: 61-67. Jubb, R. A, (1965). Freshwater fishes of the Cape Province. Ann. Cape. Prov. Mus. 4:1-72. Lake, J. S. (1957). Trout populations and habitats in New South Wales. Aust. J. Mar. Freshwater Res. 8: 414-50. Lake, J. S. (1971), Freshwater Fishes and Rivers of Australia. (Nelson: Melbourne), Lake, J. S. (1978). Australian Freshwater Fishes. An illustrated Field Guide. (Nelson: Melbourne). MacCrimmon, H. R. and Marshall, T. L. (1968). World distribution of brown trout, Salmo trutta. J, Fish. Res. Bd. Canada, 25: 2527- 2548. McDowall, R. M, (1968). Interactions of the native and alien faunas of New Zealand and the pro- blem of fish introductions, Trans. Am. Fish, Soc. 97: 1-11. McDowall, R. M. (1980), Freshwater Fishes of South-eastern Australia. (Reed: Sydney). McKeown, K. C. (1934). Notes on the food of trout and Macquarie perch in Australia. Rec. Aus, Mus. 19(2): 141-152. Nicholls, A. G. (1958). The population of a trout stream and the survival of released fish. Aust. J. Mar. Freshwater Res. 9: 319-350, Roughley, T. C. (1951). Fish and Fisheries of Australia. (Angus and Robertson: Sydney). 23 Skrzynski, W. (1974). Review of biological knowledge of New Zealand freshwater eels (Anguilla spp.). Fish. Tech. Rep. N.Z. No. 9. Stead, D. G. (1903). The Australian grayling — Prototroctes maraena Gunther. Rep. Dep. Fish. N.S. W. 1902: 34-35. Tilzey, R. D. J. (1976). Observations on interac- tions between indigenous Galaxiidae and in- troduced Salmonidae in the Lake Eucumbene catchment, New South Wales. Aust. J. Mar. Freshwater Res. 27: 551-564. Tilzey, R. D. J. (1977). The key factors in the establishment and success of trout in Australia. Proc. Ecol. Soc. Aust, 10: 97-105, Tunbridge, B. R. (1972). The elusive grayling. Freshwater Fisheries Newsletter, No. 2: 20-21. Weatherley, A. H. and Lake, J. S. (1967). Introduc- ed fish in Australian inland waters. In: Australian Inland Waters and their Fauna. Ed. A. H. Weatherley. (A.N.U. Press: Canberra). Weatherley, A. H. (1974). Introduced freshwater fish. In Biogeography and Ecology in Tasmania. Ed. W. D. Williams (Junk: The Hague). Introduced Non-marine Molluscs in Australia B BRIAN J. Terrestrial molluscs are probably the best known invertebrate animals in- troduced into Australia. The majority of snails and slugs with which most people are familiar in southern Australia are species introduced into Australia, main- ly from Europe. These were almost all accidental introductions on tools and machinery or on plants being brought over by the early European settlers. Several of the species are now very widespread throughout most of temperate southern Australia, in- habiting mainly the man-modified en- vironments dominated by introduced vegetation. A few species appear still to be actively spreading largely as a result of changing patterns of agriculture and transportation. Lists of introduced molluscs in Australia have been given by Musson (1890), Gabriel (1930), Cotton (1954) and Smith and Kershaw (1979), Thirty- five species are here recognised (see Ap- pendix) as having been introduced into Australia by European man. Several others may be well established here but remain unrecognised while others are about to be introduced and distributed. This is particularly likely with respect to tropical species. Most introduced species of non- marine molluse can be considered nox- ious animals being either pests of +Senior Curator (Zoology), National Museum of Victoria 24 y SMITH Tf gardens, crops or pasture, or vectors for stock disease. Thus far no snail-borne human diseases have been found being infective in Australia, except reports of schistosomiasis in northern Australia during World War II, but the possibility remains with each fresh introduction. Many of the species have proved to be highly successful world travellers having colonized most temperate regions of the world in the last two or three centuries. Fresh Water Snails Four species of freshwater snails belonging to three families are con- sidered established introductions. These were probably brought in on aquatic plants with importations of live fish. Several other species, mainly tropical, are confined to aquaria with no reports of ‘‘wild’’ populations. Only one species, Physa acuta, appears to be at all widespread. The species has only recent- ly been recognized as a common freshwater faunal element in southern Australia, it being confused in the past with native species of Physastra and Isidorella, \t appears to prefer still to slow flowing freshwater with plenty of aquatic vegetation and is tolerant of tur- bid and moderately eutrophic condi- tions. An important recently recorded in- troduction (Ponder, 1975), is the lym- naeid Pseudosuccinea columella. This is reported to be a more potent vector of Vic. Nat. Vol. 98 the economically important sheep liver fluke, Fasciola hepatica, than the native lymnaeid Austropeplea tomentosa. It has been recorded from aquaria in Perth, Sydney, Melbourne and some regional centres and seems to be established in the wild in isolated pockets in these centres. Orginally a native of North America, it may have been introduced into Australia from New Zealand. Land Snails Twenty-one species of land snails belonging to eight families are listed as introductions into Australia. Several re- main very localized and insignificant in the environment of long established suburban gardens. Two or three species of the genus Oxychilus, the glass snails, can even be described as beneficial as they feed on non-green vegetable matter or on small animals such as insect larvae or pest species of molluscs. However one family, the Helicidae, contains several species which are common, widespread pests of gardens and crops, often occurring in very large population densities. Helix (Cryptomphalus) aspersa, the common Garden Snail, and Cochlicella ventrosa, the Small Conical Snail, have a very widespread distribution throughout the moister areas of southern Australia. Helix is mainly a garden and orchard pest feeding on leaves and fruit of ornamental and crop species. Cochlicella is found in these areas and is also important as a pest of pasture grasses in certain areas. The Sand-Dune Snail, Theba pisana occurs in very high population densities along many sections of the coastal areas with some centres being established inland, such as along the River Murray. This is also spreading to become a garden pest in some areas. A snail similar in ap- pearance, the White Snail, Cernuella (Cernuella) virgata occurs in large populations in South Australia and Western and Central Victoria where it has become an important wheat con- taminant pest. Most of the helicids appear to be adversely affected by higher mean yearly temperature conditions, the effect pro- bably being most marked on the January/February reproductive biology. Untested observa- tions suggest that these snails require cool wet conditions for breeding and subsequent survival of the juvenile snails. If the main wet season occurs in conditions of high temperatures, this combination may not be as favourable for successful breeding. Garden helicids appear to be being replaced in Northern New South Wales by a bradybaenid, Bradybaena similaris from Asia. A potentially very important pest in- troduction, Achatina fulica the Giant African Snail, has been threatening to establish a firm foot-hold in Australia for some time. Isolated populations were reported in the Cairns area of North Queensland a few years ago (Colman, 1977) and many live specimens are intercepted by quarantine officers at ports of entry every year. There seems no valid reason why Achatina should not eventually become established in the wetter tropical and subtropical areas of Australia in the future. Slugs The most widespread and most severe pest species of introduced non-marine molluscs are to be found in the slug family Limacidae. Three of the five species in this family, Deroceras reticulatum, D. caruanae and Lehmannia (Lehmannia) nyctelia are the most common and widespread living- plant feeders in the Australian terrestrial mollusc fauna. The other two limacid species, though not nearly as common, are conspicuous members of the fauna because of their large size (Altena and Smith 1975). The pest species Milax gagates and the marginal to non-pest species Arion intermedia are also very widespread in southern Australia with Arion intermedia probably penetrating farther into unmodified native bush areas than any other species of introduc- ed mollusc, The beneficial carnivorous slug Testacella is very rare with only a few specimens having been recorded. Slugs, because of their lack of shell and ability to enter and lie hidden in very small spaces, are particularly dif- ficult to exclude from machinery and packaging, thus facilitating their rapid infestation of remote areas. 25 Discussion Over the two hundred years or so of European settlement of Australia non- marine molluscs must have been ac- cidentally introduced into various areas many thousands of times. These in- troductions occurred from widely geographically separated gene pools resulting in complex character recom- binations within one species. This has made the identification of introduced species in Australia an almost impossi- ble process in many cases as the ‘‘parent’’? species to which these in- troductions should be referred are themselves incompletely known tax- onomically. Many of the characters used to separate closely related species in Europe are linked in identification keys to geographical features. These keying characters are of little value when con- sidering an introduced species. Of the many species that have un- doubtedly been brought into the country only certain ones have survived to breed and become established. The large com- mon garden slug of Britain, Arion ater, has been recorded as an introduction many times. However no established populations are known to the writer anywhere in Australia. Other species possess in their genetic make-up, the flexibility to make of themselves suc- cessful world travellers capable of establishing vigorous populations in most temperate regions of the world. Very few tropical or subtropical species are included on the list of in- troductions, This is mainly due to the lack of knowledge of the native tropical non-marine molluse fauna of Australia, making it almost impossible to decide which species are here as part of their natural widespread geographical distributon and which are here as a result of the activities of man within the region. The only documented introduc- ed tropical snail is Achatina fulica, whose progress across the world has been comprehensively reported (Mead, 1961). Most introduced species have a distribution across native faunal region boundaries (Smith and Kershaw, 1979). In highly man-modified regions, such as many parts of south eastern Australia, 26 they are the dominant group of non- marine molluscs. In most cases there is strong evidence that their distribution is continuing to increase with species being currently recorded as pest species in localities where only a few years ago they were entirely absent. This trend is being accelerated by the increased land clearing for crop monoculture coupled with the rapid transport of products of that process across great distances. This same facility of rapid transport is also increasing the risk of new introductions into Australia. Some of these introduc- tions are accidental such as the inadver- tent introduction of aquatic snails such as Pseudosuccinea columella on plants imported with live fish for aquarists. Others are deliberate, such as the smug- gling of live edible Roman snails Helix pomatia to set up illicit culture projects for sale to fashionable restaurants. Acknowledgements I would like to thank Ms. Rhyllis Plant, technical assistant at the National Museum for her assistance in the preparation of material for this paper and Mrs Lyn Anderson for typing the manuscript. REFERENCES Altena, C.O. van R. and B, J, Smith, 1975. Notes on introduced slugs of the families Limacidae and Milacidae in Australia, with two new records. J, malac. Soc. Aust. 3(2): 63-80. Colman, P. H., 1977. Full alert for the giant African land sail. N. Qd. Nat. 44(170):8. Cotton, B, C., 1954. A catalogue of introduced snails and slugs in Australia, Rec. S. Aust. Mus, 11(2): 177-187, Gabriel, C. J., 1930. Catalogue of the land shells of Victoria. Proc. R. Soc. Vict. 43(1):62-88. Mead, A. R., 1961. The Giant African Snail. Chicago, Musson, C. T., 1890. On the naturalised forms of land and fresh-water Mollusca in Australia. Proc. Linn. Soc. N.S. W. (2)5:883-896. Ponder, W, F., 1975. The occurrence of Lymnaea (Pseudosuccinea) columella, an intermediate host of Fasciola hepatica, in Australia. Aust. ver, J, 51:494-495. Smith, B, J. and R. C. Kershaw, 1979. Field guide to the non-marine molluscs of south eastern Australia, Canberra. Appendix _ List of species of non-marine molluses introduced into Australia by man during the last two hundred Vic. Nat. Vol. 98 years. Species of actual or potential major economic importance are marked with an asterisk (*), Family Lymnaeidae Lymnaea stagnalis (Linnaeus, 1758) *Pseudosuccinea columella (Say, 1817) Family Planorbidae Planorbarius corneus (Linnaeus, 1758) Family Physidae Physa acuta Draparnaud, 1805 Family Cionellidae Cionella lubrica (Muller, 1774) Family Valloniidae Vallonia pulchella (Muller, 1774) Family Ferussactidae Ferussacia folliculus (Gmelin, 1790) Family Achatinidae * Achatina fulica (Ferussac, 1821) Family Arionidae Arion intermedius Normand, 1852 Arion hortensis Ferussac, 1819 Arion ater Linnaeus, 1758 Family Zonitidae Oxychilus cellarius (Muller, 1774) Oxychilus draparnaldi (Beck, 1837) Oxychilus alliarius (Miller, 1822) Vitrea contracta (Westerlund, 1873) Vitrea crystallina (Muller, 1774) Zonitoides arboreus (Say, 1816) Family Limacidae *Deroceras reticulatum (Muller, 1774) *Deroceras caruanae (Pollonera, 1891) *Lehmannia (Lehmannia) nyctelia {Bourguignat, 1861) *Lehmannia (Limacus) flava (Linnaeus, 1758) Limax maximus Linnaeus, 1758 Family Milacidae *Milax gagaies (Draparnaud, 1801) Family Euconulidae Euconulus fulva (Muller, 1774) Family Testacellidae Testacella haliotidea Draparnaud, 1801 Family Bradybaenidae Bradybaena similaris (Ferussac, 1831) Family Helicidae Cochlicella acuta (Muller, 1774) *Cochlicella ventrosa (Ferrussac, 1821) * Helix (Cryptomphalus) aspersa (Muller, 1774) * Theba pisana (Muller, 1774) Eobania vermiculata (Muller, 1774) *Cernuella (Cernuella) virgata (da Costa, 1778) Cernuella (Xerocincta) neglecta (Draparnaud, 1805) Cernuella (Microxeromagna) vestita (Rambur, 1868) Candidula intersecta (Pioret, 1801) The Effects of Introduced Aquatic Plants in Australia By HELEN I. ASTONT Of approximately 200 aquatic fern and flowering plant species growing in the wild in Australia about 20, i.e., about 10% are naturalized introduc- tions. Although the number of introduc- ed aquatics is small their impact on the Australian scene is considerable. They have no beneficial qualities which are not supplied equally as well by native species, yet several have proved ex- cessively detrimental, becoming major weeds with severe environmental, social and economic effects. Weed species have displaced native aquatics, become aesthetically displeasing, reduced water purity by deoxygenation and eutrophication, altered evapotranspira- tion rates, reduced water flow in irriga- tion channels and rivers by up to 70%, reduced the carrying and storage capaci- ty of water bodies, blocked engineering works such as locks and floodgates, revented swimming and _ boating, ouled pasture after floods, caused loss + Senior Botanist, oan National Herbarium of Victoria January/February of agricultural production particularly in irrigation areas with crops such as rice, harbored the vectors of disease or nuisance insects such as mosquitoes, forced authorities into the extensive use of herbicides, and absorbed large quan- tities of public finance in control pro- grammes. In 1978 the estimated cost of aquatic weed control in Australia was 2% - 3 million dollars. In view of the proven detrimental ef- fects of a number of naturalized in- troductions (particularly Fichornia crassipes, Water Hyacinth; Salvinia molesta Salvinia; Elodea canadensis Canadian Pondweed, Elodea; Sagittaria graminea Sagittaria; Alternanthera philoxeroides Alligator Weed and Myriophyllum aquaticum, Parrot’s Feather) it is advisable to prevent the in- troduction of any further aquatic species into this country without due forethought as to their weed potential. It is also advisable to prevent any further extension of those introduced aquatics which are already in Australia into areas outside of aquaria and backyard ponds. Control and/or eradication of aquatic 27 weeds requires the development of uniform laws on noxious weeds and trade, education of field officers and the public to encourage discovery and reporting of new infestations, monitor- ing and assessment of control measures, and research into the total ecology of aquatic ecosystems including biological control of particular species. Suggested Reading Aston, H. 1., (1973 or reprint 1977), Aquatic Plants of Australia, (Melbourne University Press, Melbourne). . Gopal, B., and Sharma, K. P., (1979). Aquatic weed control versus utilisation. Economic Botany, 33; 340-346. Mitchell, D. S, (1978), Aquatic Weeds in Australian Inland Waters. (Australian Government Publishing Service, Canberra), Boneseed in the Bushland of Victoria By D. LANE+ Boneseed (Chrysanthemoides monilifera) was introduced into Australia from South Africa and was cultivated in most states as a garden shrub and on occasions, used to stabilise sand dunes. An ability to grow in bushland soon became evident and ex- amples of occurrences of escapes from cultivation are listed in Grey (1976). In Victoria, extensive infestations of boneseed occur in coastal areas on the Mornington Peninsula and between Geelong and Apollo Bay. In dry woodland extensive infestations occur at Arthurs Seat, the You Yang Mountains and on the eastern outskirts of Melbourne (Fig. 1), Scattered infesta- tions, usually in the vicinity of towns, occur throughout the state (Parsons, 1973). Boneseed has not been alone in in- vading areas of Australian bushland. Many species e.g. blackberry (Rubus fruticosus agg.), Pines (Pinus spp.) Polygala (Polygala myrtifolia) Tutsan (Hypericum androsaemum), flat weeds (Hypochoeris spp.) and numerous grasses have been similarly invasive. Nor has the establishment of exotic species been all one way. Australian Acacia spp. and Hakea spp. have spread in South Africa and Eucalyptus species are becoming widespread in California. *Keith Turnbull Research Institute, Vermin and Noxious Weeds Destruction Board, Frankston, Victoria, 3199, 28 In this article, boneseed will be discussed as an example of an exotic which can invade native plant com- munities and an approach to the control of this species will be outlined. A suc- cessful invader, either a native or an ex- otic species, must produce seeds (or other reproductive parts) which can be readily disseminated and able to establish in new habitats. Boneseed, selected because of prolific flower pro- duction, sets a large number of seeds each year. These have a hard seed coat and a fleshy outer covering. When ripe, the fruits are eaten by some animals, e.g. foxes or birds, and this provides an effective means of spread into bushland. The seeds are large and the seedlings ex- hibit both a rapid initial growth and an ability to withstand shading, infertile soils and moisture stress. In South Africa, boneseed is a vigorous and successful species which has evolved into six sub species (Norlindh, 1943) that occupy habitats throughout the country. Hutchinson, (1946) refers to boneseed as ‘‘an amaz- ing species both as regards variation, choice of habitat and distribution . . . which grows in abundance from sea- level on the Cape Peninsula right around the cast coast to as far north as Usam- bara in Tanganyika Territory; it climbs to the top of the Khamiesberg and the Karee Bergen in the west, and well up the slopes of the Mont aux Sources on Vic. Nat. Vol. 98 the Drakensberg. . . The Species attains its fullest development on shale near the coast’’. This inherent vigour, combined possibly with an absence of natural pathogens in Australia, is doubtless the basis of the success of establishment of boneseed. While it is popular to believe that the Australian native species are best adapted to their environment and would therefore have a competitive ad- vantage Over exotic species, it appears that this may not be completely true. Evolution of native species has occurred in isolation, with low grazing pressures from native animals under climates which differed from today’s. As well, variability in the environment occurs from year to year and long lived species have had to adapt to survive the ex- tremes. Any community, also, is not composed of adult individuals fully ex- ploiting all available resources but is a balance between ageing plants and establishing replacements. In combina- tion, these three factors suggest that the native communities will have spaces in space and time that can be occupied by exotic species. In the case of boneseed, the available niche is a layer beneath the tree and tall shrub canopy and above the grasses and herbs. The Growth of Boneseed in Bushland Boneseed does not appear to have any specific requirements for germination once the seed coat has cracked. Seed- lings establish at any time of the year but particularly in autumn and spring or following clearing or fires. Seedling sur- vival is reduced in moist, shady situa- tions, etiolated plants being more susceptible to fungal attack. Seedlings do survive beneath mature boneseed plants so an established infestation is maintained and does not represent a temporary phase in community develop- ment. Mature boneseed forms a very dense canopy which excludes smaller plants, e.g. grasses and herbs, and the seedlings of trees and shrubs. This alters the composition and character of bushland and can threaten the existence of some native species. This density can be achieved because boneseed is free from competition from similarly sized January/February native species and has few parasites or pathogens. The Spread of Boneseed While areas such as Arthurs Seat and the You Yangs carry extensive infesta- tions, most boneseed is restricted to bushland in the vicinity of settled areas, This indicates that natural spread is slow since many areas of Victoria have similar soils, climate and vegetation to the affected sites. A major barrier to the spread of boneseed is agricultural land since seedlings do not survive grazing or cultivation. Control of Boneseed The control of a plant, such as boneseed, in bushland poses difficult and unique problems. Most weed con- trol is based on altering the environment in which the weed is growing to suppress re-establishment once the existing plants have been removed. In agriculture, cultivation or grazing programmes can be changed or competitive species established, with the use of fertilizers. Where the weed growth cannot be sup- pressed, repetitive control measures have to be resorted to. In bushland, the op- tions of changing the environment or in- troducing competitive species are not available and repetitive treatment is often beyond the scope of resources or damages the native species. Biological control can reduce dense infestations to scattered plants. However, effective pathogens which are specific to the weed species have to be available and such organisms have not been found for boneseed. For boneseed, a characteristic of the seed germination has been used to develop an effective method of control of dense infestations. Exposure to heat (100°C for 30 seconds) has been found to stimulate virtually complete germina- tion of all seed, provided the seed coat is cracked (Lane & Shaw, 1978). The seed coats develop three cracks while lying in the soil and all fruits which fall to the ground in January to February have cracked by September-October. Seeds within the cracked coats can germinate, however the rate is slow and only about 4% will germinate within one month in 29 Fig. 1 the laboratory. After heating, however, over 90% germination can occur in the same period. In the field, a slow, cool burn pro- vides suitable conditions to stimulate germination. Plots cleared after a bushfire at Arthurs Seat in 1973 and following experimental burns at the You Yangs have remained free of boneseed once seedlings which established im- mediately after the burn were destroyed. The seedlings can be removed by hand or by herbicides. One herbicide, bromoxynail, at a rate of 1:600 will kill boneseed seedlings but not harm grasses or Acacia species which also germinate after a burn. This herbicide has no residual effect in the soil so permits re- establishment of native species on treated areas. In developing control programmes for exotics such as boneseed, treatments must be sympathetic to the native flora. At the same time however, the existing 30 BONESEED DISTRIBUTION 1976 SCATTERED PLANTS \\E PATCHES IN BUSHLAND MAIN INFESTATIONS and potential threat of the exotic species to the survival of the natives must be remembered. The removal of establish- ed exotics invariably requires work that will damage existing native plants. The benefit comes from ensuring that the native community is able to regenerate by reshooting and the establishment of seedlings. REFERENCES Gray, M. (1976) Miscellaneous notes on Australian Plants. 2. Chrysanthemoides (Compositae). Contrib. Herb. Aust. 16:1-2. Hutchinson, J. (1946) A Botanist in Southern Africa. P. R. Gawthorn Ltd., London. Lane D. & K. Shaw (1978) The role of fire in boneseed (Chrysanthemoides monilifera (L.) Norl.) Control in Bushland. Proc. Ist Conf. of C.A.W.S.S. Melb. pp 333-5. Norlindh, T. (1943) Studies in the Calendulae. 1. Monograph of the genera Dimorphotheca, Casalis, Osteospermum, Gibbaria and Chrysanthemoides. Parsons, W. T. (1973) Noxious Weeds of Victoria. Inkata, Press, Melbourne. Vic. Nat. Vol. 98 The Rehabilitation of Weed Dominated Communities BY F. D. PANETTA* Introduction There are numerous instances in Australia where areas modified to a greater or lesser extent by man’s ac- tivities have been invaded and subse- quently dominated by exotic plant species. Two species which have been particularly successful in this regard in Victoria are blackberry (Rubus fruticosus agg.) and boneseed (Chrysanthemoides monilifera). Such species appear to be capable of preven- ting the regeneration of native shrub and tree species and may persist locally for an indefinite period of time. This paper seeks to examine issues related to the rehabilitation of weed dominated communities and attempts to highlight aspects which warrant further investigation. Three broadly interrelated areas will be dealt with, viz. rehabilita- tion aims, rehabilitation strategy and the selection of replacement species. Rehabilitation Objectives The aims of any rehabilitation effort should be clearly defined at the outset. It must be kept in mind, however, that the present understanding of vegetation processes and the degree of development of skills involved in the management of vegetation are sufficiently rudimentary to pose problems concerning the realiza- tion of such aims, A primary objective should be to determine the desired floristic and struc- tural attributes of the rehabilitated com- munity. The establishment of a monoculture of Pinus radiata is one method of displacing blackberry and other troublesome weeds, but may not find much support among the general public. The establishment of plantations of Eucalyptus spp. may be marginally *Department of Environmental Studies, Rusden State College, 662 Blackburn Road, Clayton, Vic. 3168. January/February more acceptable. If the rehabilitated community is to be considered as a habitat for native fauna, an exotic monoculture may be _ undesirable (Barnett ef al., 1976, Disney and Stokes, 1976). Perhaps the rehabilitated community should resemble the aboriginal vegetation as closely as possi- ble. A useful guideline for decision mak- ing at this stage may be provided by pat- terns of present and projected land use. If the area under consideration is marginally productive agricultural land it may be acceptable to establish a Pinus or Eucalyptus monoculture. Alter- natively, if the weed dominated com- munities are presently found in areas which have importance as reserves or recreational facilities, the desired floristic and structural attributes of the rehabilitated community may closely resemble those of the native community prior to the invasion by exotic plant species. If the aim is to establish a native monoculture, one would simply require a species which could be expected to be successful under the prevailing en- vironmental conditions. The selection of such a species could follow from the ex- amination of either local remnant com- munities or historical records. If it is desirable to establish a more complex community, e.g. a mixture of two or more species, possible interac- tions between the species must be con- sidered, both in the initial establishment phase and as they relate to the per- sistence of the community through time. Noble and Slatyer (1977) have recently attempted to explain the vegetation dynamics of Australian plant com- munities on the basis of a few attributes of pairs of dominant species. The first attribute concerns the method of recovery of a species after disturbance. Such methods include 31 recovery by means of vegetative regrowth (V), a local seed pool (S), im- migration of highly dispersable seed (D) or no special mechanism for recovery (N). (It should be noted with regard to the first two methods of recovery, however, that not all species are purely V or S; many species display a mixture of both methods). The second attribute concerns the ability of a species to reproduce in the presence of competition from in- dividuals of either its own or another species. Species can thus be characteriz- ed as being either tolerant (T), partially tolerant (P) or intolerant (1) of such competition. These two vital attributes may be seen to be complementary to a certain extent. If a relatively high frequency of disturbance, e.g. fire, is a controlling factor in the development of a com- munity, then mechanisms of recovery from disturbance are likely to be impor- tant contributors to the persistence of species. Conversely, if the intervals be- tween disturbance events are long relative to the life span of individuals then an ability to reproduce in the face of competition is likely to be favoured. If a species mixture is to be stable, it is essential that one species does not replace the other(s) under disturbance regimes which the rehabilitated com- munity might be expected to experience. There are a number of possible com- binations of vital attributes which may ensure the stability of a species pair, just as there are a few combinations which are unlikely to persist. For example, VT- VT and VP-ST species pairs are likely to produce stable communities, whereas VT-NP and VP-NI species pairs are like- ly to be dominated eventually by the first member of the pair. Where one member of the rehabilitated community is an obligate seed reproducer, suc- cessive fires at intervals shorter than the time to reproductive maturity are likely to eliminate it (Fig. 1). A certain level of protection from fire may be necessary to ensure its persistence. It will be seen shortly that the vital at- tributes of potential weed competitors Figure 1. The effects of fire upon the development of a community comprised of two species. See text for explanation of symbols. Species Replacement VP-SP Sequences 5G) GS 2992“ caeeo ote thoes . . SI-ST So Cofote F900 0.0 ates ° s o7 8 3S fire ——_—> ha OR 2999 5% *,%,0 090 0 Hee hae ODT Cee 6 Ge a ere” ia oo * Vie Sh Sl ST 32 Vic. Nat. Vol. 98 are of great importance in the design of a rehabilitation strategy. Noble and Slatyer (1977) comment that VT and DT weed species may be the most difficult species to displace. Whatever the desired attributes of the rehabilitated community may be, a sub- sidiary aim will be to establish a reasonably uniform vegetative cover as quickly as possible in order that the availability of resources, i.e. light, moisture and nutrients, may be effec- tively lowered. It is essential that resources freed by the local elimination of the vegetative phase of the target species become utilized by desirable species. Otherwise, such resources may simply be usurped by regeneration aris- ing from the seed of either the target species or other weeds which invade subsequently or have been previously present but not abundant. The rate at which resource availability is lowered will be of varying degrees of importance, primarily depending upon the supply of propagules of weed species. For example, where there is a small or negligible soil store of pro- pagules and the nearest source of col- onizers is some distance away, the availability of resources may remain fairly high for some time without adversely affecting the success of the rehabilitation effort. Conversely, if weed propagules are readily available (S or D recovery mechanisms), the rate at which resource availability is lowered becomes critical. It must be kept in mind that in any rehabilitation effort we are dealing in the realm of probabilities; any condition which serves to reduce the probability of establishment of weed species relative to that of desirable species will benefit the programme. If seedlings of the target species are not capable of establishing in the presence of larger plants (I or P) the lowering of resource availability brought about by the growth of the replacement species will be more effec- tive in preventing weed regeneration than if the weed species can reproduce in the presence of competition (T). Rehabilitation Strategy Whilst rehabilitation strategy must be largely determined by the objectives of January/February the undertaking, it may vary con- siderably according to the scale of the operation. For example, over small areas it may be possible to establish cover rapidly by hand planting seedlings of selected species. This approach quick- ly becomes unrealistic as the size of the area to be rehabilitated increases. Over large areas, introduction of the seed of a species mixture may be the only feasible alternative. Where weed species have not attained complete dominance and individuals of native species are relatively abundant, a practicable strategy may be to remove the weeds over a period of time, doing so sufficiently slowly that regeneration from native species can keep pace with the increased availability of resources. Bradley (1971) has provided an excellent set of guidelines for clearing weeds, by which the rate of clearing is adjusted to the relative abundance of exotic and native species. The essence of this ap- proach is that it is ultimately beneficial to err on the side of under-clearing as opposed to over-clearing of undesirable species. Weed species, being particularly well-adapted to disturbance, are generally favoured by this phenomenon (Lewis, 1973, Harper, 1977). In- discriminate removal of individuals may simply represent a wastage of effort. Where weed dominance occurs over large areas and the potential propagule input from native species is minimal, e.g. agricultural land which has fallen into disuse, it becomes necessary to take a more active role. In order to establish native species it will generally be necessary to remove the vegetative phase of the weed population. This removal may be effected by a variety of means, e.g. mechanical, chemical, burning. If rehabilitation is to proceed by the in- troduction of seed, the removal of the vegetative phase must be virtually com- plete; establishing seedlings of native species will generally be unable to com- pete with regrowth. Should herbicides be employed, they should preferably be selective and of limited persistence. Assuming that the elimination of the vegetative phase is effective, the soil seed bank of the weed species becomes the next immediate factor with which 33 the rehabilitation strategy must deal. Thompson and Grime (1979), for the herbaceous flora of temperate regions, have recently grouped seed banks into four categories (Fig. 2). The first two categories both possess seed banks which are present for less than twelve months, differing only in whether max- imum numbers of seed are present dur- ing summer and complete germination is brought about by environmental condi- tions in autumn (Type I), or the com- plementary pattern exists, with full ger- mination taking place in spring (Type II). The remaining categories comprise species with persistent seed banks, dif- fering in whether the seed bank is small (Type III) or large (Type IV) relative to the annual production of seed. If a transient seed bank is present, it should suffice to prevent seed produc- tion prior to undertaking rehabilitation, or, this failing, to delay introducing the seed of replacement species until ger- mination is complete and the weed seed- lings are removed. An apparent difficul- ty with the latter approach, however, is that seasonal conditions suitable for the germination of weed seeds may coincide with the most suitable conditions for the germination and establishment of the replacement species. Where interactions between high densities of weed seedlings and the seedlings of replacement species are unavoidable, seedling growth characteristics may decide the outcome. Seedling growth may be viewed as being dependent upon both seed size and potential growth rate, and species vary markedly with respect to these attributes (Grime, 1979). A relatively large-seeded resident weed species whose seedlings Figure 2. Idealized representation of four types of seed bank. Shaded areas: dormant seed. Unshaded areas: non-dormant seed. See text for description of types. Seed Bank Types Spring Type Type Type Type IV 34 Summer Autumn Winter VU ee Vic. Nat. Vol. 98 are characterized by high growth rates could hinder rehabilitation efforts to a larger extent than a small-seeded, slow- growing species such as groundsel bush (Baccharis halimifolia) (Panetta, 1977). Amor and Piggin (1977) note that the outcome of competition between exotic and native species is often difficult to predict. Should the target species possess a persistent seed bank, the possible dif- ficulties encountered in establishing replacement species increase in magnitude. The germination characteristics of the seed of the target species now become critical. If dor- mancy is largely of the induced and/or enforced type (Harper, 1977), altered light quality in conjunction with increas- ed temperature fluctuations at the soil surface following the removal of vegeta- tion (Thompson et a/. 1977, Panetta, 1979) should stimulate germination, and seedlings may be removed prior to in- troducing seed of the replacement species. Soil disturbance should be minimized in order to ensure that seeds remaining dormant due to deep burial are not brought to the surface. If seed dormancy is predominantly of the in- nate type, subsequent germination becomes unpredictable and is likely to occur intermittently over a long period (Salisbury, 1964, Harper, 1977). The best strategy in this case could be to in- troduce the seed of replacement species at fairly high densities, in order to en- sure that the ‘ecological vacuum’ created by clearing is filled by desirable species as quickly as possible. Examination of the seed banks under thickets of Rubus polyanthemos in- dicates that for at least one member of the blackberry species aggregate, viable seeds are present in low numbers (F. D. Panetta, unpublished data). This would appear to indicate that seedlings arising from the soil seed banks of the species should pose little threat to rehabilitation efforts. Selection of Replacement Species . The selection of replacement species will be dictated, with certain qualifica- tions, by the rehabilitation aims and strategy. Given the declared aims and January/February strategy, the ‘‘ideal’? replacement species should follow. (It has been remarked with regard to my current research regarding the rehabilitation of blackberry-infested sites at Lysterfield Lake Park, Victoria, that the criteria of high growth rate, production of a uniform cover and long term stability might be most readily fulfilled by blackberry itself!) The availability and ease of collection of seed are prime considerations in the selection of replacement species, as are their dormancy and germination characteristics. The degree of dormancy possessed by the seed should be suffi- ciently low that germination is rapid and uniform under field conditions. It may be possible to reduce dormancy levels by pretreatment, e.g. through stratification or scarification. If, as in many Australian communities, seed harvesting by ants is likely to reduce seed density substantially (Ashton, 1979), it may be necessary to treat seeds with feeding deterrents. Replacement species should possess sufficient ecological amplitude to grow successfully under a wide range of resource availability. Although a high potential growth rate would be ad- vantageous where resources are readily available, moderate to low potential growth rates are favoured under condi- tions of light, moisture and nutrient stress (Grime, 1979). Seedlings of replacement species arising from relatively large seeds may gain an ad- vantage over weed seedlings arising in situ from smaller seeds. A low degree of palatability should minimize growth reduction or mortality of seedlings due to grazing by rabbits and marsupials. Whilst it is possible to exclude grazing by fencing off rehabilitated areas, this represents addi- tional expenditure and may limit the size of area which can be rehabilitated. Conclusions It has been established for some time that the success of a weed control effort is dependent upon subsequent modifica- tion of the environment such that once a weed individual is eliminated it cannot be replaced by an individual of either the same or another weed species. The latter 35 FLOW DIAGRAM FOR REHABILITATION PROCEDURE Natural Community Seed Bank Dispersed Seed Seed Dormancy Germination Characteristics Seed Availability Fire Protection Grazing Protection 36 OBJECTIVES VITAL ATTRIBUTES OF WEED SPECIES t REHABILITATION STRATEGY SELECTION OF REPLACEMENT SPECIES Era ESTABLISHMENT OF REHABILITATION COMMUNITY MANAGEMENT Monoculture Vegetative Regeneration Tolerance of Competition Vital Attributes Ecological Amplitude Weed Control Replanting Vic. Nat. Vol. 98 Figure 3. Rehabilitation procedure. possibility may be of increasing im- portance should biological control research lead to the reduced abundance of currently troublesome species. With a knowledge of the regeneration characteristics of particular weed species it should be possible to design a rehabilitation programme which will facilitate the establishment of a stable community comprised of desirable species (Fig. 3). If replacement species are chosen according to appropriate criteria it may be possible to minimize management, e.g. maintenance, effort following their establishment. Acknowledgments I am grateful to A. Thatcher, A. Hopkins, E. McClellan and D. Doley for comments on the manuscript. REFERENCES Amor, R, L. and Piggin, C. M. (1977), Factors influencing the establishment and success of exotic plants in Australia, Proc. Ecol. Soc. Aust. 10: 15-26. Ashton, D. H. (1979), Seed harvesting by ants in forests of Eucalyptus regnans F. Muell, in central Victoria., Aust. J. Ecol. 4: 265-77. Barnett, J. L., How, R. A. and Humphreys, W. F, (1976), Mammals of Clouds Creek, north- eastern New South Wales, and their distribu- tion in pine and native forests, Aust. Zool. 19: 23-34, Bradley, J. (1971), Bush regeneration. Mosman Parklands and Ashton Park Association, Sydney. Disney, H. J.de S. and Stokes, A. (1976), Birds in pine and native forests, Emu 76: 133-8. Grime, J. P. (1979), Plant Strategies and Vegeta- tion Processes (Wiley: Chichester). Harper, J. L. (1977), Population Biology of Plants (Academic Press: London). Lewis, A. J, (1973), Ragweed control techniques: effect on old-field plant populations, Bull. Torrey Bot. Club 100: 333-8. Noble I. R. and Slatyer, R. O. (1977), The effect of disturbance on plant succession, Proc, Ecol. Soc. Aust, 10; 133-45, Panetta, F. D. (1977), The effects of shade upon seedling growth in groundsel bush (Baccharis halimifolia L.), Aust. J. Agric. Res. 28: 681- 90 Panetta, F. D. (1979). Germination and seed sur- vival in the woody weed, groundsel bush (Baccharis halimifolia 1.) Aust. J. Agric. Res. 30; 1067-77. Salisbury, E. J. (1964), Intermittent germination in Capsella, Nature (Lond.) 199: 1303-4. Thompson, K, and Grime, J. P. (1979), Seasonal variation in the seed banks of herbaceous species in ten contrasting habitats, J. Ecol. 67: 893-921. Thompson, K., Grime, J. P. and Mason, G. (1977), Seed germination in response to diurnal fluc- tuations in temperature, Nature (Lond.) 267: 147-9. Some Notes on Feral Pigs and Their Distribution in Victoria By SIMON E. TOWNSEND.* The feral pig is a large, conspicuous, generally abundant animal and today an economically important component of Australia’s vertebrate fauna. The main occurrence of the feral pig is across the better watered parts of the tropical north and eastern half of the continent. Large populations are spread across Queensland, New South Wales and the Northern Territory, wherever suitable cover, feed and water are to be found. Small and local populations exist * 5/4 Lambert Rd., Toorak, 3142. January/February in South Australia, Tasmania and Western Australia as well as in Victoria (Alison, 1969; Frith, 1973). As its name suggests, the feral pig is a domestic animal which has established free breeding populations. Without human management, natural selection has resulted in a phenotype with a super- ficial resemblance to the Eurasian wild pig Sus scrofa. This is the ‘‘wild boar’’ of the venery, or classical hunting, and the progenitor of the varieties of domestic pigs. However, this phenotype is variable owing to a continuing flow, 37 by accident or design, of domestic genes into the feral population. Some authorities claim that recognizable strains of domestic breeds are often found in the wild (Frith, 1973; Rolls, 1969). In New Guinea the remains of pigs with an age of more than six thousand years have been reported, indicating an introduction at or before that date (Chowning, 1973; Hope, 1977). Since the Australian seas probably did not reach their present level till approx- imately five thousand years before the present (Loffler, 1977), New Guinea and Australia may not have been separated by any significant water barrier six thou- sand years ago. Theoretically, it is possi- ble that pigs might have entered Australia unaided at a date much earlier than is as yet substantiated. Existing Australian populations are presumed to have descended from escapes or deliberate releases of Euro- pean stock. It is possible that some could be of Asian origin. Their ancestors may have been brought to the north of the continent by Asian travellers or fishermen within historical times. Archaeological evidence is lack- ing to support this or the previous theory, therefore the feral pig cannot authoritatively be said to have a history in Australia any longer than that of European settlement. The feral pig has received scant atten- tion in the literature as an element of the Victorian mammal fauna. This is pro- bably because Victorian populations are small and local, though widespread. Perhaps more importantly, bodies con- cerned with recording faunal distribu- tion in the past have overlooked or ignored the species presence. The most recent, though still in- complete, references to feral pig distribution in Victoria are to be found inthe Study Reports of the Land Conser- vation Council of Victoria. All Study Reports available at the time of writing were consulted and the relevent references to feral pig distribution are included in Table 2. 38 One earlier but important reference to the distribution of the feral pig is to be found in Allison (1969). ‘There are very few pigs to be found in Victoria, most of these being spillover animals on the border of New South Wales, in the swamps and scrubs adja- cent to the Murray River. One small col- ony exists around Benalla in the heavy forests, where they may be located the first day out — or the fifty-first.”’ The Australian distribution map in Frith (1973) indicates feral pig popula- tions stretching south to the Murray River, also in an area approximately north of Melbourne and in the most eastern extremity of the state. Un- fortunately he gives no references direct- ly related to the distribution of the feral pig in Victoria. Table 1 consists of a list of locations of feral pig populations in Victoria sup- plied by the Vermin and Noxious Weeds Destruction Board of the Crown Lands Department of Victoria. This can be considered the ‘‘official’’ distribution of Victorian feral pig populations. Table | Feral Pig Population Locations in Victoria. Supplied by the Vermin and Noxious Weeds Destruction Board at 28 December 1978, Bairnsdale Ballarat Benalla Boort Cohuna Corryong Gisborne Inglewood Kerang Kyabram Mansfield Meringur Morn- ington Moyhu Nathalia _Piangil Red Cliffs Robinvale Sale Seymour Werrimul Yea Table 2 is a series of locations of feral pig populations and their sources based on reports other than that of the Vermin and Noxious Weeds Destruction Board including first hand accounts of sightings by private individuals. The specific geographical features used to in- dicate the populations of Victorian feral pigs, such as towns, rivers or national parks are those closest to or encompass- ing them. Abbreviations used for some sources are, Forests Commission, Victoria, F.C.V. and National Park Services, N.P.S. Vic. Nat. Vol. 98 Table 2 Feral Pig Population Locations in Victoria and Thier Sources Collected by S.E. Townsend. Location Source Barmah F. Borelli, 1972; BC VS 979 A, Meakes, August 1977; author, March 1978. Boole Poole Peninsula M. Vague, April 1979, Brisbane Ranges National Park Broadford Carrum (M.M.B.W. Sewerage Farm) Anonymous, 1979, F.C.V., 1979. M. Carter, 1977/78. Corryong F,C.V,, 1979. Delatite Valley E.V.C. Adamson, 1978. Gippsland Lakes Coastal Park N.P.S., 1978. Granite Hills (near Yea) R. Dato, 1979. Gunbower Island FG24,,1979, Hattah Lakes National Park N.P.S., 1978; National Parks Ser- vice, Hattah, 1977; author, December 1977. Healesville P.R. Brown, 1979; K. Pearce, 1979, Holey Plains State Park N:P-S.,° 1978: « D: Smith, 1978. Hogua Valley E.¥.C. Adamson, 1978. Inglewood R. Fletcher, 1978; J. Malone, 1977; C. Neads, 1979; C.R. Townsend, 1978; author, December 1979, Kinglake R. Dato, 1979; R. Zann, 1978. Kulkyne National Parks Ser- vice, Hattah, 1977; Land Conservation Council, (June 1974, p. 184); author, December 1977. Lindsay Island J, Seebeck, 1967. R. Dato, 1979; C. Tomisich, 1979. Mt. Marianne Mudgeegonga L. Cooper, 1976. Murmunjee L. Cooper, 1976. Nepean State Park N.P.S., 1978. Patterson River M. Carter, 1977/78. Pearcedale G.M. Pizzey (no date). Quail Island State Faunal Reserve E. Drake-Clark, 1977; author, 1977. Robinvale F.C.V., 1979; author, September 1977. Rochester D. Clark, 1979. January/February Sale Common State Game Refuge Mt. Samaria National Park R. Johnson, 1979. NEPS., SISK TD: Smith, 1978. (near R. Dunn, 1972/73. G. McNeil, 1979. C.R. Townsend, January 1980; author, April 1980. F.C.V., 1979; Land Conservation Coun- cil, (October 1974, p.73); A. Fleming, 1871; K. Holmes, 1976; R. Stoner, 1978. R. Dato, 1979. D. Marriot, 1979; K. Pearce, 1979. W.B. Emison et al (1978, p.357); F.C.V., 1979. W.B, Emison et al (1978, p.357). Silver Band Falls Halls Gap) Stockmans Reward Mt. Tallarook Tolmie Toobarac Toolangi Wannon River Wartook Valley Whitefield F.C.V., 19799. Wimmera River E.V.C. Adamson, 1978. Wombat State Forest D. Clark, 1979; K. Pearce, 1979. Doubtless many of the populations in- dicated overlap or are in reality one in the same, especially those in the head- waters of the Broken and Goulbourn Rivers. However, they represent in- dependent sightings and illustrate how widespread is the species. The exact origin of most Victorian feral pig populations will never be precisely known. The author would ven- ture to suggest that at least some Murray River populations are directly descend- ed from those that were already well established in the Riverina by the 1880s (Rolls, 1969). While the likelihood of escape of a few domestic pigs occasionally con- tinues, the diverse and _ generally unrelated locations of most Victorian populations suggests that they are the result of deliberate liberations. Such liberations, of trapped feral phenotype pigs, have been and continue to be primarily perpetrated by irresponsible hunters wanting to increase the variety of available game in the areas they hunt 39 over (K. Pearce, C.R. Townsend and M. Vague pers. comm.). The feral pig is credited with killing stock, spoiling crops, damaging fencing and fouling watering points (Frith, 1973). For these reasons it was added to the list of declared vermin in Victoria in 1973. Naturally enough the feral pig is less popular with agriculturalists than hunters. The latter find it a challenge at times. While the danger involved in hun- ting feral pigs is often overrated it does exist and a large pig bailed up or wound- ed can be a formidable opponent (Allison, 1969; Frith, 1973; Rolls, 1969). Like any uncontrolled stock, the feral pig is a real and potential harbour of disease transferable to stock and in some cases to humans. Already a danger to agricultural production, the threat pos- ed by the presence of the feral pig would reach disastrous proportions should foot and mouth disease enter Australia (Snowdon, no date). The feral pig population, well entrenched over much of the continent including Victoria, could become a significant vector for the spread of this contagious and virulent disease. The continued unsettled state of much of south east Asia, with resultant large and random movements of displaced peoples has particular and pointed relevance when one considers the vast and only sporadically guarded northern coastline of Australia. If diseased stock was landed, feral pigs along the north coast could quickly become infected and transfer foot and mouth disease through the continent via the medium of the widespread feral pig population and un- managed ungulates of all kinds. Once foot and mouth disease was endemic to this population it could become impossi- ble to eradicate. The effect on Australia’s meat industry and dairying could be disastrous, especially in respect of exports. Similarly, non agricultural ungulates in captivity, in particular the Zoological 40 collections in each State, would be en- dangered. These collections have been assiduously built up and preserved. Pre- sent quarantine requirements make fur- ther acquisitions of wild ungulates from overseas impossible. Not the least to suffer in such an even- tuality would be Victoria’s four species of wild deer. Unlike most introduced wildlife, the sambar, red, fallow and hog deer are protected under the Wildlife Act 1975 and are proclaimed game. The pressure on native wildlife by predation and competition from feral pigs is poorly understood but is presum- ed to be serious (Frith, 1973; Serventy, 1966). Direct predation on reptiles, am- phibians and invertebrates is probably more extensive than of other animals due to their relative lack of mobility and the feral pig’s omnivorous diet. Habitat degradation is potentially a more devastating threat to native wildlife than direct predation. Areas particularly sensitive to damage by feral pigs are those which are favoured for feeding and wallowing — swamps and watercourses. These are very limited in extent in this driest of continents. The effect of feral pigs on forest en- vironments in Australia is largely unknown. The New Zealand experience has not shown exceptionally severe damage (Harris, 1970), at least not when compared to the devastating results of acclimatization of other species in that country. In central Victoria, the effects of rooting by feral pigs has been reported as “‘keeping the country open’’ in relation to regrowth of the understory in wet and dry eucalyptus forest (K. Pearce, pers. comm.). The wide range of habitats inhabited by feral pigs in Victoria include coastal tea-tree and paperbark scrubs, wet and dry eucalyptus forests, mallee scrubs and the more open types of forest such as river redgum forest. As this species can be found in areas with restricted waterpoints such as mallee country, then Vic. Nat. Vol. 98 it seems reasonable to suspect they will travel many miles when necessary, presumably under cover of darkness, to find them. The current, and the threatened, hazards to agriculture and the Australian environment presented by the continued existence of feral pig populations, far outweigh any possible benefits they might create. In Victoria, the most densely settled State with the most intensive agriculture, the situation is aggravated by further releases of cap- tured feral pigs in unpopulated areas by unthinking and selfish people, to im- prove the opportunities for hunting. The demand for hunting as recreation is high and opportunities relatively low so these releases are understandable to a degree but cannot be condoned (Allison, 1969; Frith, 1973; Rolls, 1969). The deliberate release of feral pigs is irresponsible, antisocial and illegal. If focus could be taken from the feral pig and redirected towards native species at present not utilized as game, the feral pig could possibly be contained and eradicated. This might be possible in Victoria where the feral pig is still only local in distribution and where a brief chance may still exist for grappling with the problem. Frith (1973) and Wharton (no date) have discussed at length the possibility of further native species being utilized as game. Mr J. Wharton, Director of the Fisheries and Wildlife Division of the Ministry for Conservation of Victoria (pers. comm.), feels that some wallabies and native pigeons in Victoria, show potential as additional game species. An attempt to wean attention away from feral pigs as desirable game and redirect it towards further native species might ensure that both receive needed conservation attention. It could lead to the eradication or containment of the former and the much needed and long overdue detailed study of the latter. Acknowledgements Help in this project was received from January/February the Australian Deer Association, the Victorian Field and Game Association, the Vermin and Noxious Weeds Destruction Board of the Victorian Crown Lands Department, the Forests Commission, Victoria, the National Parks Service, the Bird Observers Club and the Natural Resources Conservation League of Victoria. Private persons who provided information or gave assistance at other times include E.V.C. Adamson, F. Borelli, P.R. Brown, P.G. Brown, M. Carter, D. Clark, L. Cooper, R. Dato, E. Drake-Clark, R. Dunn, A. Fleming, R. Fletcher, M. Harrison, K. Holmes, R. Johnson, J. Malone, D. Marriot, G. McNeill, A. Meakes, C. Neades, K. Pearce, G.M. Pizzey, J. Seebeck, D. Smith, ‘*Zooey’’le Soeuf, P.L. Stevens, R. Stoner, C. Tomisich, C.R. Townsend, M. Vague and R. Zann. The friendly and helpful criticisms of the manuscript by Roy Dunn, Peter Rawlinson, John Seebeck, Frank Town- send and Graham Pizzey were much ap- preciated as was the latters newspaper appeal for information on the authors behalf. REFERENCES Allison, C, (1969). The Australian Hunter. Cassell, Australia. Chowning, A. (1977). An Introduction to the Peoples and Cultures of Melanesia. Cummings Pub. Co. Inc., Menlo Park, Calif. Emison, W.B,, Porter, J.W., Norris, K.C. and App, G.J. (1978). Survey of the Vertebrate Fauna in the Grampians-Edenhope Area of South Western Victoria, Mem. Nat. Mus. Vic. 39; 281- 363. Frith, H.J. (1973). Wildlife Conservation, Angus and Robertson, Sydney. Harris, L.H. (1970), Wild Pigs in Wild Animals in New Zealand. Eds. A.L. Poole and J.-H. Johns, A.H. and A.W. Reed, Wellington. Hope, J. (1977). The Effects of Prehistoric Man on the Fauna of New Guinea in The Melanesian Environment. Ed, J. Winslow, A.N.U.P., Canberra. pp.21-7. Land Conservation Council (August 1973). Report on the North Eastern Study Area, District 2. Melbourne: Government Printer. (June 1974). Report on the Mallee Study Area. Melbourne: Government Printer. (October 1974), Report on the North Eastern Study Area, Districts 3, 4, and 5. Melbourne: Government Printer. 44 Loffler, E. (1977). The Effects of Traditional Man on Landforms in Papua New Guinea in The Melanesian Environment, Ed. J. Winslow, A.N.U.P., Canberra, pp.3-10. Rolls, E.C. (1969). They All Ran Wild, Angus and Robertson, Sydney, Serventy, V. (1966). A Continent in Danger. Reynal and Co,, London. Snowdon, W.A. (no date). Foot-and-Mouth Disease in Wildlife Management Australia (a series of undated seminar papers presented at La Trobe University, Melbourne). pp.231-36. Wharton, J.C. (no date). Hunting in Wildlife Management Australia (a series of undated seminar papers presented at La Trobe University, Melbourne). pp. 198-203. Bush-peas of Victoria — Genus Pultenaea — 15 By M.G. Corrickt Pultenaea fasciculata Benth. in Ann. Wien. Mus. Naturg. 2:82 (1840). Pultenaea fasciculata is a subalpine to alpine species of the Eastern Highlands of Victoria and is also found in New South Wales and Tasmania. It is a small erect, somewhat procum- bent shrub 15-30 cm _ high, but sometimes trailing if growing in thick vegetation. The stems are terete with a silvery pubescence on young growth. The alternate, terete leaves are 3- 10 mm long, grooved on the upper sur- face and with a slender, fragile, mucronate tip. The upper leaf surface is not visible, but the lower surface is slightly scabrid with silvery appressed hairs mainly on the young growth. The slender, dark brown stipules are 1-2 mm long with recurved tips. The orange flowers are solitary in the leaf axils towards the ends of the bran- ches, but the tips grow on before the flowers die. The standard is 8-9 mm long and 8-9 mm wide and is tinged with purple brown, as also are the keel petals. The calyx is silky pubescent, 4-5 mm long with a pedicel 1-2 mm long. The upper calyx lobes are broader and less deeply divided than the lower. The dark brown bracteoles have ciliate margins and a few pale scattered hairs on the back. They are attached at the base of +7 Glenluss Street, Balwyn, Victoria. the calyx tube but vary considerably in shape and length, from 1.5 mm long and | mm wide on Lake Mt. collections to 3-4mm long and | mm wide on specimens from Mt. Cobberas and vicinity. Each flower is subtended by a single reduced leaf with enlarged stipule. The ovary and base of the style are pubescent with white silky hairs and the plump pod is also silky pubescent and does not extend beyond the tips of the calyx lobes. SPECIMENS EXAMINED included: Bogong High Plains, 28.i. 1966, A.C. Beauglehole 15747 (MEL _ 1517572); Native Cat Plain, 29. i. 1971, A.C. Beauglehole 36616 (MEL 1517575); Nunniong Plateau, 5.i. 1949 NA. Wakefield (MEL 1507294); Lake Mt., 25.1.1948, JH. Willis (MEL 1517580). Pultenaea graveolens R. Tate in Trans. Roy.Soc.S. Aust. 7:68 (1885) This species is scattered in isolated auriferous areas of Western Victoria and is in a few localities in South Australia, but is apparently nowhere common. Pultenaea graveolens is a resinous, highly aromatic and often hairy shrub 1- 1.5 m high with rather drooping bran- ches. The rounded stems are hirsute and light brown when young. Fig. 20. a — h, Pultenaea graveolens. a, habit; b, calyx and bracteoles, one bracteole drawn a little larger, from MEL 1517538; c, style and ovary from MEL 1517589; d, leaves and stipules; e, stipule from MEL 1517583; f, larger, more hairy leaf form from the Grampians, MEL 1517589; g, pod; h, seed, from MEL 1517575. i—4q, Pultenaea fasciculata. i, habit; j, calyx and bracteoles, one bracteole drawn a little larger, k, style and ovary; |, leaf and stipule; m, stipule; n, enlarged stipule with reduced leaf, all from MEL 1517572: 0, calyx and bracteoles of specimen from Lake Mountain showing very short bracteoles, MEL 1517580; p, pod; q, seed from MEL 1517581. 42 Vic. Nat. Vol. 98 January/February 43 The alternate leaves are ovate-linear 2-15 mm long and 0.5-3 mm wide, with an acute tip and tightly inrolled margins. The lower leaf surface is usually scabrid and hirsute, the upper surface is paler with short curled hairs. The brown, viscid stipules are 1 mm long and stand well out from the stem. The pale orange flowers are solitary in the leaf axils of short lateral branches. The standard is 7-9 mm wide and 7- 9mm high with purple-brown mark- ings; the wings and keel petals are also tinged with purple-brown. The viscid, usually slightly hairy calyx is 5-6 mm long with a pedicel of 3- 4mm. The two upper calyx lobes are broader and less deeply divided than the slender acuminate lower lobes. The bracteoles are 1-3 mm long and 1.5- 2mm broad; they are attached at the base of the calyx tube and extend to the base of the lobes. The ovary is densely villous with white silky hairs which extend along almost the whole length of the style. The pod is plump and villous and well exserted from the calyx. Flowering time is late October. There is considerable variation in plants from the different populations of this species in Victoria. Grampians specimens have the largest leaves and very bright coloured, large flowers and all parts of the plant are hairy. Specimens from Castlemaine area are almost glabrous and have the smallest leaves, while the Stieglitz population is intermediate between the two. The viscid, distinctive, strongly aromatic ex- udation is common to all populations; it is most noticeable at the time the first flowers open and has been variously described as like ‘‘Spirit contaminated with animal matter’, curry or cream cheese. SPECIMENS EXAMINED included: Trooper’s Creek, 30.i.1969, M.G. Cor- rick 1941 (MEL 1517589) Rushworth Forest, 6.iv.1980, M.G. Corrick 6538 (MEL 1517069) Baillieston, x.1929, C.J. Mason (MEL _ 1517583); Porcupine Ridge, x.1963, B. Strange, (MEL 151587); Stieglitz, 30. x. 1943, J.H. Willis (MEL 1517584). Fig. 20b. Known distribution of Pultenaea graveolens and P. fasciculata. G © Poltenaea greveclens © Prltenasa fasciculata H Vic. Nat. Vol. 98 AUSTRALIAN NATURAL HISTORY MEDALLION FUND Amount on hand July 1980 $1493.50 Mr Fred Barton 50.00 Total December 31, 1980 $1543.50 Treasurer: Mr David Dunn, 3 Allfrey St, East Brighton 3187 (578 5753) NEW BOOK **Scientific and Common Names of Insects and Allied Forms Occurring in Australia.’’ 95 pages Index of Scientific Names. Index of Common Names Systematic List of Phylum. Arthropoda. Price $4.00 Postage Paid. Order from CSIRO Editorial & Publications Service, 9 Queens Road, Melbourne, Vic. 3004 Field Naturalists Club of Victoria Reports of recent Club activities General Excursion to Anglesea Sunday 7 December Leaders Mary D.White and Joan Forster had thoroughly covered the area previously and led us to exciting things. There were more than a dozen different orchids including both the Large and the Small Duck-orchid — Caleana major and C.minor. And there was a broad patch of Red-beaks Lyperanthus nigricans, unfortunately now all with dead heads, but Mary White had discovered the red patch in October and we imagined them as they were then. Among many other botanical interests were the two fringe-lilies — Common Fringe-lily Thysanotus tuberosus and Bran- ching Fringe-lily T.dichotomus. Anglesea is one of the few places where the latter can be found. We were surrounded by bird song and those observed included the Dusky Woodswallow, Blue-wing Parrot and Striated Pardalotes. The pardalotes were the highlight of the day. They had burrows in a low bank and several of them were darting in and out — quite regardless of the crowd of field naturalists only a few yards away. Everbody had an excellent view. We had hoped to see Rainbow-birds which had been observed last week but they did not reveal themselves today. Thanks go to our leaders for a superbly organised and enriching trip. January/February General Meeting Monday 8 December President Dr Brian Smith opened with two important announcements. Conservation Award to FNCV. Each year the CCV (Conservation Council of Victoria) honours an organisation that has made a significant contribution to conservation. The 1980 Award went to this Club and was presented to our President by the Premier at government offices earlier this evening. The visible prize is a large oil painting by the en- vironment artist Neil Douglas. New FNCV Treasurer. Mr David Dunn has accepted the position of treasurer to this Club and we wish him well in his arduous under- taking. He follows Mr Dan McInnes who has been treasurer for about twelve years. Actual- ly, the Club has been without a treasurer since the last Annual Meeting but Mr MclIn- nes (being Mr McInnes) has continued to see us through although officially he was merely a ‘‘bookeeper’’, He has done a terrific job for FNCV, nurturing our finances and always planning what is best for the Club. All members will join in thanking Dan McInnes for his great contribution over a very lengthy period. Hawthorn Juniors. The President said that it seems appropriate that the last meeting in our Centenary year should be provided by those who will see the Club through some of its second centenary. He then introduced the 45 President of Hawthorn Junior FNC, Mr Malcolm Turner. Mr Turner spoke briefly of the Hawthorn Club and emphasised that, for some years now, the Club has been run entirely by the juniors themselves — those under 25 years, He introduced each speaker in turn. On the Seashore. Barbara Thompson, aged about 10, spoke of things found on the shore — sponges, crabs, sea stars, shells. Barbara gave some information about each and show- ed specimens. Blue-tongue Lizards. Brian Glassenbury, about 13, talked of five young blue-tongues he owned, how quickly they grew, what he fed them on, the different disposition of in- dividuals. Flies are insects with only two wings not four, as explained by Nick Bastow, age about 15. He said there are 6300 Australian species in a world total of 8000, that the house-fly makes 200 wing beats per second, the mos- quito 600, and the blowfly travels 260 body- lengths in a second. Nick concluded with comments on the effect of DDT on mos- quitoes in India. Cape Barren Geese. Damien Cummins, about 15, stated that only about 5000 of these geese still survive on Bass Strait islands; they breed from June to September with average of 4.7 eggs per clutch, and grow to 22”? tall. he maintained that conservation regulations are not strict enough but reported the recent establishment of the Patriarch sanctuary on Flinders Island where crops are planted so the geese won’t move on to the farms. Glennies Islands. Malcolm Turner showed slides of the Glennies — four islands off the west coast of Wilsons Promontory. They are the same granite formation as the Prom, large areas are bare rock and there is no sur- face water. Bush Rats (darker, more docile and more plentiful than on mainland) and Swamp Antechinus were trapped. There was evidence of White Skinks and Water Skinks, many burrows of Fairy Penguins and Mut- tonbirds (Short-tailed Sheerwater), bones of the Fur Seal, and Dolphins off shore. Ar- cheologists are studying the middens. The President thanked Hawthorn Club for the varied and interesting programme. Exhibits centred on activities of Hawthorn Juniors. The previous day they had been ona water plant excursion led by Helen Aston and there was a large display of such plants. 46 Publications produced by Hawthorn Juniors were for sale. More trees on farms. A letter was read to the meeting asking this Club to support the writer’s plea for tax rebates to farmers who plant more trees. He had written to the Prime Minister and the Treasurer about the matter and asked FNCV members to do the same. South Gippsland. Members listened to the FNCV submission to the LCC (Land Conser- vation Council) concerning extensions to na- tional parks in Gippsland. The meeting en- dorsed the submission. General Meeting Monday 12 January Land Planarians. After an absence of six years, Mr Leigh Winsor was the first speaker in this Members Night. He lives at Townsville where he is working on land planarians. He had expected flatworms in the tropics to be more pentiful, larger and more colourful than in the south, but his expectations were wholly faulty. However, other wildlife around (almost within) Townsville is abun- dant and he had listed 80 bird species in his garden. Referring to a visit to Britain, Mr Winsor said how astonished he was that all cryptosoic life forms are known; here in Australia there is yet much to be discovered and studied. Eucalypts. Mr Alan Morrison showed slides of eucalypt trees — flowers, fruits and trunks of several species. Repitle, bird and mammal slides were shown by Mr Lloyd Thomas. Insects were included in the slides shown by Miss Wendy Clark, Marine egg capsules. Dr Brian Smith show- ed slides of egg capsules of molluscs (shells, squid, etc) in astonishing variety of size and shape. Pond Life. Mr McInnes spoke of Albert Park Lake where water weed, which previously hampered boats, has been com- pletely removed yet there is still as many microscopic creatures as before. Under microscopics he exhibited specimens taken there of water mites, water boatmen, back swimmers, copepods and the only plant life — 1/8” spots of algae growing on a sheet of plastic. Exhibits, as well as the pond life, included a scorpion from Toolangi Forest, nest of a silver-eye, rat-tail maggots from a water bin, and an album of photos of the Nature Show. Vic, Nat, Vol, 98 GROUP MEETINGS All FNVC members are invited to attend any Group meeting; no extra charge. At the National Herbarium, the Domain, South Yarra, at 8.00 p.m. First Tuesday — Mamal Survey Group. Tuesday, 3 February. Members night. Tuesday, 3 March. Outback Australia. Third Wednesday — Microscopy Group. Half hour members exhibits and observations. Wednesday, 11 February. Gadget Night. Leader: Mr D. Wentworth. Note change from third Wednesday for this month only. Wednesday, 18 March. Green Algae. Speaker; Mr D. McInnes. First Wednesday — Geology Group. Wednesday, 4 February. Members night. Wednesday, 4 March. Earthquakes and their prediction. Speaker: Dr M. Etheridge, Monash University. Second Thursday — Botany Group. Thursday, 12 February. North America; the beauty of wild flowers. Speakers: Mr Thiess and Ms Doery. Thursday, 12 March. From here and there; travels round Australia. Speakers: Mr and Mrs O. Brewster. At the Conference Room, the Museum, Melbourne, at 8.00 p.m. Good parking — enter from Latrobe St. First Monday — Marine Biology and Entomology Group. Monday, 2 February. Holiday observations and members exhibits, slides. Monday, 2 March. Molluscs of Port Phillip Bay, Speaker: Dr Brian Smith. Monday, 6 April. Pond life with a movie camera. Speaker: P. Genery. GROUP EXCURSIONS Botany Group — last Saturday. Saturday, 28 February. Mt Donna Buang. Saturday, 28 March. Pt Wilson, Port Phillip Bay. Geology Group — second Sunday. Sunday, 8 March. Mt Robinson and Kinglake. Mammal Survey Group. Saturday, 14 — Sunday, 15 February. Camp at Mt Worth. Saturday, 7 — Monday, 9 March. Camp at Mt Bullfight. Day Group — third Thursday. Thursday, 19 March. Train outing to Fern Tree Gully National Park. Train to Upper Fern Tree Gully from Flinders St. at 10.15 a.m. Leader: I. Gillespie 578 1879, There will be no April outing. January/February 47 Field Naturalists Club of Victoria Established 1880 OBJECTS: To stimulate interest in natural history and to preserve and protect Australian fauna and flora. Members include beginners as well as experienced naturalists. Patron: His Excellency the Honorable SIR HENRY WINNEKE, KCMG, KCVO, OBE, KStJ, QC. Key Office-Bearers 1980-1981 President: Dr. BRIAN SMITH, 8 Hunsford Avenue, North Clayton, 3168 (560 8358) Secretary: Miss WENDY CLARK, 27 Rangeview Grove, North Balwyn, 3104 (859 8091) Correspondence to: FNCV, National Herbarium, The Domain, South Yarra, 3141 Treasurer: Mr. D. DUNN, 3 Allfrey Street, East Brighton, 3187 (578 5753) Subscription Secretary: F.N.C.V. C/- National Herbarium, The Domain, South Yarra, 3141 Editor: Mr. R. WALLIS, C/- State College of Victoria—Rusden, Blackburn Road, North Clayton, 3168, 544 8544. Librarian: Mr. P. KELLY, C/- National Herbarium, The Domain, South Yarra, 3141. Assistant Librarian: Miss M. J. LESTER, 4/210 Domain Road, South Yarra, 3141 (26 1967) Excursion Secretary; Miss M. ALLENDER, 19 Hawthorn Avenue, Caulfield, 3161 (527 2749) Book Sales Officer: Mr. D. E. McINNES, 129 Waverley Road, East Malvern, 3145 (211 2427) Group Secretaries Botany: Mr. MICHAEL McBAIN, 19 Foster St, St Kilda, 3182 (534 2293) Day Group: C/- National Herbarium, The Domain, South Yarra, 3141. Geology: Mr. T. SAULT, C/- National Herbarium, The Domain, South Yarra, 3141 Mammal Survey: Mr. RAY GIBSON, 26 McCulloch Street, Nunawading, 3131 (874 4408) Microscopical: Mr. M. H. MEYER, 36 Milroy Street, East Brighton (596 3268) Entomology and Marine Biology: Mr. D. E. McINNES, 129 Waverley Road, East Malvern, 3145 (211 2427) FNCV Kinglake Nature Reserve: McMahons Road, Kinglake. Bookings and keys: Mr. |. F. MORRISON, 788 Elgar Road, Doncaster (848 1194) MEMBERSHIP _ Membership of the F.N.C.V. is open to any person interested in natural history. The Victorian Naturalist is distributed free to all members, the club’s reference and lending library is available and other activities are indicated in reports set out in the several preceding pages of this magazine. Subscription rates for 1980 PAGICODOMRAN 1. aie Weta = aA ab ret Seo. hole ca cos endo hboce hus che PARE Fa clt ecg laretito-h) athe 4 Joint Metropolitan .............2.00202.0,, y an eB Country Members and Retired Persons POD CCUM Ana MILAetred iam sms sedis sey eimgh totdidil Widen ban cn, phd tee oS Bee Subscription to Victorian Naturalist....... Overseas Subscription to Victorian Naturali = MRL COUIAISER ee NR eu eyelid. All subscriptions should be made payable to the Field Naturalist Club of Victoria and posted to the Subscription Secretary. G3. JENKIN BUXTON PRINTERS PTY. LTD., WEST MELBOURNE Vol. 98, No. 2 March/April 1984 Published by the FIELD NATURALISTS CLUB OF VICTORIA in which is incorporated the Microscopical Society of Victoria $ { 75 Renistered for nosting as a publication — Cateaory ‘'B"’ FNCV DAIRY OF COMING EVENTS GENERAL MEETINGS At the National Herbarium, the Domain, South Yarra. Monday, 13 April, 8.00 p.m. Otway study night. Keynote speakers will be arranged and all Groups are asked to prepare a short address. Monday, 11 May. Annual General Meeting. Presidential address by Dr Brian Smith — zoological research at the Museum, Monday, 15 June. Film night — South-west Tasmania. New Members — March/April General Meetings. Ordinary Ray Carter, Clematis Rd, Clematis. Mavis Condon, 6 Evandale Rd, Malvern. Beverley Cross, 14 Simpson’s Rd, The Basin. L. Gerke, 12/546 Toorak Rd, Toorak. Andrew Isles, 103 Noone St, Clifton Hill. Fiona Johnson, 51 Mason St, Hawthorn. Joan Locke, 139 Mary St, Richmond. Ulla Pedersen, 1/8 Duff St, Sandringham. Julie Raines, 13 Fortune Ave, Lilydale. Libby Sandiford, 241 Royal Pde, Parkville. Bruce Straw, 26 Panorama Ave, Lower Plenty. Mary Todd, | Glenroy Rd, Hawthorn. Country Grant Baverstock, 13 Helena St, Highton. Fred de Munk, Wesley Camp, Old Chum Creek Rd, Healesville. Peter Dostine, 371 Princes Highway, Sylvania Heights, New South Wales. A. Piesse, 17 Warwillah Ave, Wangaratta. B. Wiecek, 2 Milburn St, St. Mary’s. Joint Adrian and Philip Daniell, 24 Ruskin Ave, Croydon. Christine Drum and Lindsay Delzoppo, C/O 5 Emo Rd, East Malvern. Keith and Dorothy Every, 16 Valley Rd, Mt. Waverley. Martin and Wendy Mebalds, 5 Mitchell St, St. Kilda. G.W. and L.L. Quick, 17 Penguin St, Melton. B. and H. Sterkenberg, 21 Watsons Rd, Moe. FNCV EXCURSIONS Sunday, 3 May. Pirianda Gardens. These Gardens are managed by the National Parks Service and only open at certain times of the year. Visits must be booked in advance and numbers are limited. The coach will leave Batman Ave at 9.30 a.m. Fare $6.00. Bring a picnic lunch. Sunday, 7 June. Zoological Gardens. Meet at the main extrance at 11.00 a.m. Bring a picnic lunch. Preliminary notices: Saturday, 17 October — Friday, 6 November. New Zealand, North Island. A number of members have indicated in this excursion so arrangements will be proceeded with; however more bookings are required and all bookings should be confirmed with a $50.00 deposit. This excursion covers an area not usually included in tours. Cape Kidnappers is the only mainland gannet rookery in the world ac- cording to the brochures. The tentative programme is: Oct. 17 Auckland; Oct. 18 Auckland/ Coromandel/Whitianga; Oct. 19 Whitianga/ Tauranga; Oct. 20 Tauranga/Rotorua; Oct. 21 Rotorua/Whakatane; Oct. 22 Whakatane/Hicks Bay; Oct. 23 Hicks Bay/Gisborne; Oct. 24 Gisborne/ Wairoa; Oct. 25 Wairoa/Napier, visiting Urewera National Park; Oct. 26 Cape Kidnap- pers/Napier; Oct. 27 Napier/New Plymouth; Oct. 28 New Plymouth; Oct. 29 New Ply- mouth/Tongariro National Park; Oct. 30 National Park; Oct. 31 National Park/Auckland; Nov. 1 Auckland/Kaitaia; Nov. 2 Reinga/Kaitaia; Nov. 3 Kaitaia/Bay of Islands; Nov. 4 Bay of Islands; Nov. 5 Bay of Islands/Auckland; Nov. 6 Auck- land/Melbourne. The cost is expected to be approx- imately $1250. Special study strips: re ag Wendy Clark for details (A.H. 859 1). Saturday, 16 — Sunday 17 May. Snails of Otways Forest. Leader: Dr Brian Smith. The Victorian Naturalist Volume 98, Number 2 March/April, 1981 ISSN 0042-5184 Editor: Robert L. Wallis Assistant editor: F. Dane Panetta Editorial Committee: H. Cohn, R. Kent, B. Smith A Blue Whale Baelonoptera musculus Stranded near Warrnam- DOOt ICON a DY AA os NSIES Foi 5 eon songs 46 toa,

281 Z. March/April *Moraea aristata (Houtt.) Aschers. & Graebn.; see 11; 343 4. Myriophyllum sp. (A): E, A. Orchard pers. comm. BM. Myriophyllum sp. (B); E. A. Orchard pers. comm. JK. *Najas marina L.: see Aston, Vict. Nat. 96: 67-69 (1979) Z. Notelaea longifolia Vent.; see 1:415 Z. *Paspalum dasypleurum Kunze ex Desvaux; see Simon, Bot. Branch Tech. Bull 3: 42 (1978) N. *Paspalum urvillei Steud; see /// 199; the present author recently witnessed spreading colonies near Walwa in Grid USO (Collection ACB 68461, 16 May 1980 — MEL and author’s private her- barium) U. *Petrorhagia nanteuillii (Burnat) Ball et Heywood: see 1: 170 R. Phyllanthus trachyspermus F, Muell.; see: 3; 510. A. *Plantago australis Lamk.; in Flora of N.S. W. 181: 11 (1977) Briggs et al records this species as naturalized for Victoria KN. *Pontederia cordata L.; see Aston, Vict. Nat. 96: 67-69 (1979) D. Prostanthera incana A. Cunn.; see: /: 515 W. Prostanthera sp. aff. decussata; J. Carrick pers. comm, N, *Salix alba L.; see 12: 24 DEJIKNPRVWZ. Sclerolaena intricata (R. H. Anderson) A. J, Scott; Syn. Bassia intricata R. H. Anderson; see Scott, Dept. of Plant Biology, Univ. of Birmingham, Birmingham, Great Britain: 101-119 (1978) A. Solanum adenophorum F. Muell. in Fragm. Phytogr. Austr. 2:162 (1860-61) H, Solanum coactiliferum J. M. Black in Trans. R. Soc, S, Aust. 33: 224 (1909) F. Solanum petrophilum F. Muell.; see 12: 554 H. Solenogyne dominii L. G. Adams in Brunonia 2:43-65 (1979) CDEJKMNPS. Solenogyne gunnii (Hook.f.) Cabrera; see Adams ibid, EVWZ. *Soliva anthemifolia (Juss.) R.Br. ex DC.; MEL pers. comm. 3 July 1980, has supplied the follow- ing: ‘one of your recent collections, ACB 63962 from near Murray River, Grid Q37, 4 June 1979, has been identified as Soliva anthemifolia (Juss.) R.Br. ex DC. This is yet another new record for Victoria’ U. *Sorghum bicolor (L.) Moench; A collection, ACB 63772, 24 Jan. 1979, from Stony Rises near Colac in Grid K14 was determined by B. K. Simon and now housed at MEL. BRI and the author’s private herbarium K. Stipa sp. (A); J. W. Vickery pers. comm. C. Stipa densiflora Hughes; see /; 53 MRSVWZ. Stipa falcata Hughes; see /: 53 ABCFGHMRYVW. Stipa sp. (B); J. W. Vickery pers. comm. C Stipa mundula J. M. Black; see 2: 108 C. Stipa nodosa S. T. Blake; see 2; 108 C. Stipa oligostachya Hughes; see Hughes, Kew Bull. Misc. Inf. 12 (1921) CD. Stipa scabra Lindl.; J. W. Vickery pers. comm. 57 determined several collections as this species BYWYZ. Stipa stuposa Hughes, see Townrow, Proc. R. Soc. Tasmania 112: 227-287 (1978) CDW. Stipa tenuighumis Hughes; see 2: 111 EK. Stuartina hamata W_R. Philipson; see 1; F. Stylidium ecorne (F. Muell. ex. Erickson & Willis) Farrell & James; see Farrell and James, Aust. J. Bot, 27: 39-45 (1979) CDIRS. Utricularia monanthos Hook.f.; see 7: 339; The present author has collected this dwarf species north of Mt. Cope in the Bogong High Plains in Grid V47 — ACB 15489, 26 Jan. 1966 (MEL and the author’s private herbarium) V. Zostera capriconi Aschers; see Jacobs & Williams, Telopea | (6): 451-455 (1980) Z. REFERENCES 1, Beadle, N. C. W., Evans, O. D. and Carolin, R. C. (1972). Flora of the Sydney Region. (A. H. and A. W. Reed Pty. Ltd.: Sydney). 2. Black, J. M. (1978). Flora of South Australia. 3rd Edn. Part 1; Revised and Edit: J. P. Jessop (S.A. Government Printer: Adelaide). 3. Black, J. M. (1948) Flora of South Australia 2nd. Edn. Part 2. (S.A. Government Printer: Adelaide). 4, Brown, Robert (1810) Prodromus florae Novae Hollandiae. (J. Johnson; London). 5, Burbidge, N. T. & Gray, M., (1976). FI. of the Australian Capital Territory (Australian National Univ. Press: Canberra). 6. Churchill, D. M. and Corona, A. de (1972). The Distribution of Victorian Plants. (The Dominion Press: North Blackburn). 7. Galbraith, Jean (1977). Wild Flowers of South- East Australia (Collins: Sydney). 8. Orchard, A. E. (1975). Auckland Institute and Museum Bulletin No. 10 (Auckland Institute and Museum: Auckland). 9. Tutin, T. G., Heywood, V. H., Burgess, N. A., Moore, D. M., Valentine, D. H., Walters, S. M., Webb, D. A., (1972). Flora Europaea. Vol. 3. (Cambridge Univ. Press: Cambridge). 10. Tutin, T. G., Heywood, V. H., Burgess, N. A., Moore, D. M., Valentine, D. H., Walters, S. M., Webb, D. A. (1976). Flora Europaea. Vol. 4. (Cambridge Univ. Press: Cambridge). 11. Willis, J. H. (1970), A Handbook to Plants in Victoria. Vol. 1, 2nd ed. (Melbourne Univ. Press: Melbourne). 12. Willis, J. H. (1972). A Handbook to Plants in Victoria. Vol. 2 (Melbourne Univ. Press: Melbourne). Acacia notabilis — First Records for Victoria Recent field work in the Mallee region of north-west Victoria (since published as ‘Fire in the National Parks of North-West Victoria’ by P. D, C-Cheal, J. C. Day and C. W. Meredith; National Parks Service, 1979) required the preparation of a vegetation classification based on floristic data collected on a quadrat basis. In two of the 10m x 10m quadrats for which full species lists were prepared a problematic Acacia sp. occurred. Specimens were taken and pressed for later identification. As some difficulty was experienced identifying the specimens, they were sent to the National Herbarium, Victoria (MEL) for identification. They were later returned unnamed, with the note ‘‘. . . doesn’t match anything in the Victorian reference set.”’ After further investigation, including comparison with the type held at MEL, I have concluded that the specimens are Acacia notabilis F, Muell. These are the first records of this species for Victoria. Locality The plants were found in two localities in the far west of the Sunset Country: — (a) 10 minute grid A38, at grid reference 433714 on the 1:250000 map series, Mildura sheet SI 54-11. Collected 25.10.1978. (b) 10 minute grid A39, at grid reference 446713 on the 1:250 000 map series, Mildura sheet Sl 54-11. Collected 13.10.1978. Habitat (a) Open shrubland, dominated by Eucalyptus gracilis/Eucalyptus socilis, to 3.5m tall and 40% canopy cover above an open shrub layer of Acacia notabilis, to 1.6m tall and 25% canopy cover, with a low open (15% canopy cover) shrub layer of predominantly Beyeria opaca. The red loamy clay of this broad interdune flat was stabilised by a more or less continuous crust of mosses and lichens, (b) Open shrubland, dominated by Eucalyptus calycogona, to 3m tall and 30% canopy cover above an open shrub layer of Acacia notabilis, to 2m tall and 15% canopy cover, with a low open (15% cover) field layer of a variety of small ephemeral herbs (notably Calotis hispidula, Crassula spp., and Plantago turrifera) and perennial Stipa spp., Bassia diacantha and Maireana pentagona, The brown clay loam (again a broad inter-dune flat) was stabilised by an almost continuous crust of lichens and mosses. Species common to both sites were Bassia diacantha, Beyeria opaca, Brachyscome Vic. Nat. Vol. 98 Figure 1. Speciment of Acacia notabilis F. Muell. lineariloba, Calotis hispidula, Crassula colorata, Helipterum pygmaeum, Maireana pentagona and Stipa elegantissima. The habitat agrees closely with that described for the species in Whibley (1980), p.122 viz. *‘. . . open scrub vegetation. Soils; mainly brown or shallow calcareous, hard alkaline red duplex.’’ Description A. notabilis is readily distinguished from all other Acacia spp. recorded from north- western Victoria by the very broad (app. lcm) legumes containing transverse seeds, encircled by a very long funicle. In addition, it is readily separable from the only other tall, broad-foliaged Acacia spp. of the region (i.e. Acacia hakeoides and Acacia pycnantha) by the prominent thickened yellow margins to both the phyllodes and the legumes. Acacia notabilis F. Muell. is a tall glabrous shrub to 3m. tall. The branches are terete with a smooth reddish-brown bark. The oblong lanceolate to rhomboid, somewhat glaucous phyllodes are 5 to 15 cm long and 5 to 25mm broad with a prominent mid-vein, numerous fine lateral veins and a prominently thickened yellow margin. The apex is more or less obtuse and there is a gland on the upper margin just above the short, wrinkled peduncle. Inflorescences are axillary racemes shorter than the phyllodes with 45 to 60 flowers per head, followed by narrowly oblong legumes 3 to 7 cm long and about | cm broad. The margins are thickened and the pods are raised over the transverse seeds, which are almost completely encircled by the long funicle. Flowering time of the Victorian plants is unknown but young legumes were present on specimens collected in late October. The species also occurs in New South Wales, South Australia and Western Australia. Acknowledgements: The Staff of the National Herbarium (Victoria) kindly provided access to various specimens kept in the collection there, including the type(s). REFERENCES: Whibley, D.J.E., (1980). Acacias of South Australia Pub. Govt. Printer, Adelaide. P.D. C-Cheal C/- National Parks Service (Victoria), 240 Victoria Parade, East Melbourne, 3002. Preliminary Notice Ideas for Ornithological Research in the Eighties VORG Conference Melbourne, 24 — 26 July 1981 The Victorian Ornithological Research Group will be holding a Conference in Melbourne over the weekend 24 — 26 July 1981, on the theme of Ideas for Or- nithological Research in the Eighties. If the price of petrol continues to rise, the title may be Bird Study Close to Home — which would then be another way of express- ing the theme. All interested persons are invited to attend the Conference. It is hoped that further March/April details will appear in a later issue of this jour- nal; in any case they may be obtained from the address below. VORG Conference Secretariat P.O. Box 203 South Melbourne, 3205 Rosemary Balmford Secretary, VORG. 59 Inside the Burrow of the Common Wombat, Vombatus ursinus (Shaw 1800) By J.C. McILROY*, R. J. COOPER* ANDE. J. GIFFORD* Introduction The common wombat, Vombatus ursinus (Shaw 1800) is a large, her- bivorous marsupial which inhabits the forest-covered, mountainous areas of south and south-eastern Australia. One of its best-known habits is its excavation and use of burrows for diurnal shelter. To date, though, little is known or has been published about the burrows, in- cluding their internal structure. Nicholson (1963) whilst a schoolboy, crawled into several wombat burrows and sketched their layout. Mcllroy (1973) examined 197 wombat burrows and, based on their length, classified them into three types — minor, medium and major burrows. Each type differed considerably in their physical and en- vironmental characteristics, patterns of use and function. Mcllroy also crawled into each burrow but, because of his size, was not able to fully examine many of the burrows over their entire length. During July and August, 1979, we had the opportunity to examine the in- teriors of seven wombat burrows, As part of an extensive research programme on the effects of vertebrate pest control campaigns on non-target animals, we had radio-tracked 12 wombats which we had dosed with 1080 poison (sodium fluoroacetate). Eight of the wombats subsequently died, all within their bur- rows. Consequently, to recover the transmitters, we excavated seven of the burrows; excavation of the eighth bur- row, however, was not a practical pro- position. This paper describes our obser- vations on the internal structure of these seven burrows. *Division of Wildlife Research, CSIRO, P.O. Box 84, Lyneham, A.C.T. 2602 60 Methods The study area was situated in the Bondo State Forest, near Tumut, New South Wales. Five burrows were in 4 and 8 year old plantations of Pinus radiata established after the original native eucalypt forest had been clear- felled and the other two burrows were situated in adjacent retention areas of native forest. Six of the burrows were situated in red earth, the most common soil in the area. The seventh burrow was in astony, granitic soil. Initially we began removing all the soil above the burrow but this soon pro- ved impracticable so we simply dug 1-4 shafts, up to 2.2 m deep, along the route of the burrow until we eventually located the wombat. Because of the physical effort involved no further shafts were dug after this, even though six of the burrows continued onwards. All burrows were examined by torch- light from the entrance and bottom of each shaft and the presence and dimen- sions of resting chambers were recorded, including their distance from the burrow entrance. Other measurements taken were the dimensions of the entrances and the tunnels at shaft sites, the depth of the tunnels below the ground at shaft sites and the length of each tunnel, as far as possible. In most cases the total length of the burrow could not be measured. The length and girth of each wombat was also obtained prior to its ingestion of poison. Results The seven burrows varied in length from over 7.0 m to over 17.9 m (Table 1). Their single, inverted U-shaped en- trances ranged between 31-65 cm in height and 37-49 cm in width. Tunnel Vic. Nat. Vol. 98 Table 1. The internal measurements of seven common wombat burrows. Entrances Tunnels (range) Length Height Width Area** Depth* Height Width Area** (m) (cm) (cm) (m) (m) (cm) (cm) (m’) 7.2 31 47 0.19 0.3-0.4 20-26 39-43 0.10 TD 32 41 0.17 0.3-0.9 27-29 35-36 0.12 7.0 65 a7 0.32 0.3-0.9 25-32 27-28 0.09 16.7 42 46 0.25 0.4-1.8 23-27 28-36 0.08 17.9 40 47 0.25 0.4-1.3 24-28 32-35 0.10 8.3 35 49 0.22 0.2-1.5 18-28 23-39 0.06 10.1 44 47 0.27 0.8-2.2 = — _ Resting chambers .Distance from Depth* Height Width Length Area** entrance (m) (m) (cm) (cm) (cm) (m’) (a) 1.9 0.4 — — _ — (b) 4.0 = oan = — = (a) 4.5 <., 25 57 78 0.19 (b) 6.8 = = - — _ (a) 4.8 0.9 31 49 65 0.20 (a) 5.3 he 35 50 95 0.23 (b) 19.3 1.8 4l 50 106 0.27 (a) 2.6 0.8 34 56 100 0.25 (b) 5.8 _— 35 55 108 0.25 (a) 6.2 _— a - = = (a) 3.1 1.1 35 49 81 0.23 (b) 8.8 2.2 36 59 130 0.28 *Depth of soil above tunnel or resting chamber; (a) = anterior chamber, (b) = second chamber —= No data recorded. ** Areas based on area of a parabolic segment = 2/3 (2a)h where 2a = width and h = height. heights ranged between 17.5-32 cm and widths between 23-43 cm. Two of the burrows divided into separate tunnels 1.5 m and 4 m from the entrances, respectively. In the first burrow one tun- nel continued for more than 4.7 m while the other tunnel ended abruptly after a further 2.9 m. In the second burrow both tunnels extended on for at least another 5.5 m and 6.1 m, respectively. The slope of the ground the burrows were dug into and the direction they followed varied considerably. Five bur- rows, dug into relatively flat to moderately sloping ground continued directly onwards while another two, dug March/April into moderate slopes, turned shortly after the entrances and extended across the slopes. The slope of the tunnels also varied. Three tunnels were initially level but then either gradually sloped up- wards or downwards. Another three in- itially sloped downwards but then levell- ed off or rose and then descended again. One tunnel steadily rose from the en- trance onwards, parallel with the slope above it. Each burrow contained at least 1-2 resting chambers. These were enlarged, scooped-out oval sections of the tunnels, varying considerably in size (height 25- 41 cm, width 49-59 cm, length 65-130 61 cm). The most anterior chambers were located 1.9-6.2 m from the entrances, either in direct line or just after a gentle bend or fork. The next chambers were situated a further 1.5-5.0 m in (i.e. 4.0- 10.3 m from the entrances), generally in the same stretch of tunnel as the anterior chamber. The one exception occurred just after the burrow abruptly changed direction. The depth of soil above the chambers and the deepest points of ex- cavation varied from 0.4-2.2 m. One anterior resting chamber contained a layer of eucalypt twigs and leaves, a common bedding material (Mcllroy 1973), but the other 11 chambers ex- amined were unlined. Three of the dead wombats were found in the anterior chambers, two in the next chambers, one 11.8 m in, past two chambers and the seventh animal 16.7 m in, at the end of the burrow. Each wombat was found lying on its chest. Rabbits, Oryctolagus cuniculus, also sheltered in the burrows and, in two in- stances, had excavated smaller tunnels into the wall 0.2 m inside the entrance and 16.7 m in, at the end of the burrow. No other vertebrates were found in the burrows, although Mcliroy (1973) listed foxes, Vulpes vulpes, mountain possums, Trichosurus caninus, echidnas, Tachyglossus aculeatus, and bush rats, Rattus fuscipes, as other in- habitants of wombat burrows. Discussion Although there are larger animals in the world that dig or shelter in subterra- nean holes, such as the aardvark, Orycteropus afer, and warthog, Phacochoerus aethiopicus, the common wombat is still a remarkable animal in regard to its burrowing ability. The seven burrows we examined, for in- stance extended for more than 7-17.9 m, involving the excavation of approx- imately 0.6-1.8 m* of soil. Mcllroy (1973) recorded 197 burrows measuring between 0.3-19.5 m in length while Troughton (1957) mentions one burrow 62 29.5 m in length. The cross-sectional area of the entrances to the burrows were also quite large (0.17-0.32 m? for our 7 burrows, 0.12-0.26 m? for the 197 measured by Mcllroy 1973). The actual tunnels, though, were much smaller (0.06-0.12 m?) and just large enough for a wombat to move along. (The cross- sectional area of an adult wombat, bas- ed on the area of a circle, is approx- imately 0.04-0.05 m?, excluding the legs). The resting chambers, in com- parison, were much larger in cross- sectional area (0.19-0.28 m?) than the tunnels. It is clear from the work of Wells (1978) that the resting chambers have an important role in the thermoregulation and activity rhythms of the hairy-nosed wombat, Lasjorhinus latifrons. Wells did not record air temperatures deep within the burrows in his semi-arid study area but soil temperatures, measured ap- proximately 1 m below the ground sur- face and 3 m in from the burrow en- trances, remained relatively constant throughout the year. In contrast, air temperatures within the antechambers and just outside the burrow entrances fluctuated widely throughout the year, with marked daily and seasonal gra- dients present. According to Wells, when a wombat returns to a burrow after a night’s activity, it retreats into the depths of the burrow. Later (e.g. the next afternoon) it moves up the burrow towards the entrance but if it encounters unsuitable (e.g. higher) air temperatures, it retreats again. If the air temperature is not markedly different from that in the depth of the burrow, such as during a dull day, it rests in a chamber within the ‘twilight’ zone, about 3 m in from the entrance. It then emerges when either light intensity (e.g. during winter) or air temperatures (e.g. during summer) are suitable for activity. This generally occurs after sunset but may occur during dull daylight. Less is known about the role of the resting chambers in the ecology of the Vic. Nat. Vol. 98 common wombat. G. Brown (pers. comm. 1980) has found that ambient temperatures just within their burrow entrances vary widely but after about 4 m inside a burrow air temperature and soil temperature are almost equal. In contrast to the hairy-nosed wombat bur- rows, he found that soil temperatures approximately 1 m below the ground surface (and thus probably air temperatures deeper inside the burrow) varied throughout the year. At Bondo, such variation is likely to be from 8- 20°C. Nicholson (1963) believed that the common wombat’s movements within burrows were directly related to light in- tensity. On bright, sunny days he found wombats deep down inside the burrows. On less bright days they were often found closer to the burrow entrance while on very dull days they were usually present in the half-light, just inside the burrows, or sometimes were active above ground. Mcllroy (1973) made similar observations but believed that air temperatures also governed activity rhythms. Possibly, as with the hairy- nosed wombat, both light intensity and air temperature are involved in deter- mining emergence and re-entry times for the common wombat and the ‘nests’ Nicholson (1963) found 1.8-4.9 m inside burrows, the 35 chambers Mcllroy (1973) located within the first 0.9-7.3 m of 33 burrows and the 12 chambers we located 1.9-10.3m from the entrances represent ‘sensing posts’ where a wom- bat can ‘lie-up’ and wait until conditions are suitable for above-ground activity. Some of the chambers, particularly the posterior ones, may also have other functions. Nicholson (1963), for exam- ple, relates how adult female wombats make simple nurseries of bracken fronds and bark at the end of tunnels. He also described how a wombat entering a deserted burrow or one containing a dead wombat would dig a new chamber about 2.7 m from the old chamber and line this with bracken fronds and bark. March/April Chambers used by females were ap- parently always slightly larger and better lined than those used by males. Of the chambers (or tunnels) examined by Nicholson (1963), Mellroy (1973), or those reported here, none appeared to have been used as ‘sanitary chambers’ for deposition of faeces, as occurs with some semi-fossorial mammals (e.g. rodents). Internal division of burrows does not appear to be common. Nicholson (1963) found one burrow that divided 2.1 m in from the entrance into two tunnels 4.4 m and 8.2 m long, respectively, while Mcllroy (1973) found 12 burrows that divided in a similar manner. The reason for such divisions is not clear. Nicholson (1963) remarked that if a wombat found a deserted burrow containing a dead wombat it may dig another tunnel. Young wombats, while learning to dig, also gradually excavate their own small tunnels inside their mothers’ burrow, It appears then that over many years some of these tunnels are excavated further, finally linking up with other tunnels, either within the same burrow or with tunnels from adjacent burrows, to form a complex network of inter-connecting tunnels and entrances. In conclusion, one must be impressed by the simplicity of construction but sophisticated function of a wombat bur- row. In essence it is simply a long tunnel dug into the ground that is sufficiently large enough for a wombat to move along and yet, with its series of resting chambers, it provides not only a secure haven from predators, bushfires and other perils above ground but also a means by which individuals can avoid problems with thermoregulation and emerge when climatic conditions are suitable. REFERENCES Mellroy, J. C. (1973). Aspects of the ecology of the common wombat, Vombatus ursinus (Shaw, 1800). Ph.D, Thesis, Australian National Univer- sity. 63 Nicholson, P. J. (1963). Wombats. Timbertop Mag. 8, 32-38. Troughton, E. Le G. (1957). ‘‘Furred Animals of Australia’’ 6th edit. Angus and Robertson, Sydney. Wells, R. T. (1978). Thermoregulation and activity rhythms in the hairy-nosed wombat, Lasiorhinus latifrons (Owen), (Vombatidae). Aust. J. Zool. 26. 639-51. A Key To Some Gasteromycete Genera Commonly Found In South-eastern Australia Since the publication in 1944 of G. H. Cunningham’s Gasteromycetes of Australia and New Zealand much work has been carried out upon this class of the fungi; new genera have been erected and new combinations made. The Key To Families and Important Genera Of The Lycoperdales by D. M. Dring in The Fungi 1VB, published in 1973, in- corporates many of these modern tax- Lycoperdaceae. onomic concepts. The following key, coupled with the species descriptions in Cunningham’s work, should assist in the identification of the ‘puffballs’ most commonly found in this Botanic region. The key is confined to the Lycoper- daceae and certain monotypic genera not yet recorded for this region have been omitted. Fruit bodies mostly terrestrial, some on wood; exoperidium of one layer, often caducous; spore sac dehiscing by apical pore or by attrition from above; capillitium septate or not, typically branched, hyaline or tinted; spores mostly globose, brown, smooth, spiny or warted, occasionally reticulate. I, Exoperidiumfassands case 2 te. «coke peoeterirertes cocosere peers SHE ae aeretccieet > 1° “Broperiditim: nota sand’ case. 2... > Prieta eek eek GPR bn eth BREA ae 3 2(1) Spores strongly reticulate; exoperidium dehiscing by falling away from GDOVE Hs ee el oa PG dds be ee Py ae ee ee Abstoma 2(1) Spores not reticulate; exoperidium caducous except for a small basal disc; endoperidium tough with definite apical stoma ........ Disciseda 3¢1)Truecapilhitinmeab und antec e: cy. eateries eat clears nat eho aeineeeenttancee 4 3(1) True capillitium absent; paracapillitium abundant .................... 9 4(3) Sterile base absent or virtually so or fibrous ..................... = 4(3) Sterilé- base: cellular, prominent sxe ee cette sons eae eee ee hia ee 7 $(4) Apical storia absent 15. siete en oc0ig oa pecss cre aisle Poth oben he een ote eter eee 6 5(4) Apical-stomeé. present). 17455). «5.0 eee aeean om eds cere eae Bovista 6(5) Exoperidium and endoperidium falling away ......... Langermannia 6(5) Endoperidium thick, tough, splitting stellately; capillitium strongly SPIO Saal, Behe ared ood ela ieg- gt eS ed in ON Ol Mycenastrum 74) Stoma presenter Sins aibe eb tase lade att eta opens Pe enn en Re 7(4) Stoma absent; dehiscence by falling away of upper part of peridium; sometimes a tough zone between gleba and sterile base, not a true PUA PHP ARIE 6c nci oe cuss gun, Sie bse tik etree ee eed ee ae Calvatia 8(7) Capillitium free within peridium with well marked main stem, (bovistoid) much branched; pseudocolumella poorly UevEloped:. Aye sliiger cates doke z 0 1 | aie seneeieald Kilometres Fig.1 Mount William, Grampians are regarded as brown algae (Phaeophyta). Larger log-like bodies were described by Dawson (1859) from Lower Devonian beds on Gaspe Penin- sula, Canada, and called Prototaxites. Prototaxites consists of a system of tubes of two sizes, but numerous thin sections of the Grampians specimens failed to reveal a definite internal anatomy. There can be no question of identifica- tion with either present or past trees which might have yielded similar ‘‘logs’’, as the Grampians sediments are of Late Silurian or earliest Devonian age, (Spencer-Jones 1976), and were laid down before the development of large land plants. In fact, the well-known Baragwanathia flora of central Victoria, 66 Fig. 2. Log-like structure, Mount William, Gram- pians. Photo: P.R. Kenley Vic. Nat. Vol. 98 containing some of the earliest land Medwell, G.J., 1977: Palaeocurrent directions in plants, was probably contemporaneous. Otway Group sediments, Otway Ranges, southwestern Australia. Proc. Roy.Soc. Vict, 89: pp 27-50. Spencer-Jones, D., 1976; Grampians Group of REFERENCES Dawson, J.W., 1859: Introductory geological notes. in Penhallow, D.P., On Nematophyton and allied forms. Trans. Roy.Soc. Canada 6: (4) pp 27-36. Western Victoria, in Geology of Victoria, J.G. Douglas & J.A. Ferguson, Eds, Geol. Soc, Aust.Spec. Pub. 5, A New Macropod Species of the Grampians By P.R. Five species of macropods have been listed by Wakefield (1974), Seebeck (1976) and Emison er a/. (1978) for the Grampians ranges. These are: Macropus giganteus (Eastern Grey kangaroo) M. fuliginosus (Western Grey or Mallee kangaroo) M. rufogriseus (Red-necked wallaby) Petrogale penicillata (Brush-tailed Rock Wallaby) Potorous tridactylus (Potoroo). The Western Grey is usually seen in open woodland or grassland flats, par- ticularly in the Black Range and Victoria Valley area. The dark brown fur usually serves to differentiate it from the Eastern Grey kangaroo, which may be seen with it in these locations. The Eastern Grey occurs more widely throughout the ranges and foothills, together with the Red-necked wallaby. The Brush-tailed Rock Wallaby colony in the Victoria Range was described by Wakefield (1971). The population of this wallaby is small and disturbance of its environment by visitors and an army cadet corps which used a nearby area for training, may have endangered it. The Potoroo too has a limited distribution — Pomonal area — and its status may also be uncertain since part of its known range is on free-hold land subject to alienation. *P.O. Box 180 Hamilton, Vic. March/April BIRD* Sub-fossil evidence reveals that the following species were also once present in western Victoria (Wakefield 1974; LCC (1978) report): Bettongia gaimardi (Southern bet- tong) B. penicillata (Woylie) B. lesueur (Boodie) Macropus greyi* (Toolache wallaby) Lagorchestes leporoides* (Brown hare wallaby) Thylogale billardierii (Red-bellied wallaby) Aepyprymnus rufescens (Rufous rat kangaroo) Onychogalea unguifera (Northern nail-tailed wallaby) O. fraenata (Bridle nail-tailed wallaby) Megaleia rufa (Red kangaroo) Wallabia bicolor (Swamp or Black wallaby) (* believed to be extinct). The Southern bettong once occurred in the Grampians (Wakefield 1974) whilst the sub-fossils of this species and the others variously occurred in the Lower Glenelg, Tower Hill, Byaduk Caves and Mt. Hamilton deposits and at Koroit beach. Wakefield (1974) ac- counts for the presence of these species by association with changes in the climate. Wet-forest species such as the Swamp wallaby were prominent in Lower Glenelg deposits in Pleistocene sediments c. 15,000 years BP and again in the late Holocene epoch. Semi-desert 67 forms such as the Red Kangaroo, Boodie and Bridled wallaby appear in the early Holocene epoch c. 8,000 years BP, and more recently (2000 — 3000 years BP) in Koroit beach aboriginal middens (LCC report). Did some or all of these species also occur in the Gram- pians? The Swamp Wallaby was present in the Lower Glenelg area at least into the early 1900’s, according to recollections of an early Portland farming family (A.C. Beauglehole, pers. comm.). The present most western occurrence given by Wakefield (1974) is the Otways, ex- tending to the Port Campbell National Park. There is no evidence that it still occurs in the Lower Glenelg National Park (A. Arnold, National Parks Ser- vice, pers. comm.). The presence of the Swamp Wallaby in the Grampians was established in March 1979. Mr Don Macarthur, a farmer whose property at Mirranatwa adjoins State Forest in the Serra Range, captured a small wallaby amidst tussocks. The distinctive grey, black and reddish brown pelage signified to Mr Macarthur that this was not the com- mon red-necked wallaby. He gave the animal to Mrs Susan McInnes of Vic- toria Valley but, despite treatment, it soon died. Subsequently the wallaby came into my possession and I lodged the specimen with the National Museum of Victoria. Confirmation of identity was obtained from the curator of mam- mals, Miss Joan Dixon. Other in- dividuals of the species have subsequent- ly been seen in the Mirranatwa Gap area on both east and west slopes of the Serra range. The extent of distribution of the species in the Grampians is unknown although there appear to be similar habitat areas (thickets of tea-tree, melaleuca and heath) elsewhere on lower slopes of the ranges. Wakefield (1974) considered that of the sub-fossil species, only the Bettong was present in western Victoria at the time of European settlement. The Rufous rat kangaroo was regarded in the LCC report as having been present. Perhaps, in the light of the discovery of the Swamp Wallaby in the Grampians, one should not rule out the possibility of the survival of one of these smaller species too. REFERENCES Emison, W.B., Porter, J.W., Norris, K.C, and Apps, G.S. (1978). ‘‘Survey of the vertebrate fauna in the Grampians-Edenhope area of south western Victoria.’’. Mem. Nat. Mus. Vic. 39, 281-363. Land Conservation Council of Victoria (1978). Report on south western area District 2, pp. 123- 126. Seebeck, J.H. (1976). ‘‘Mammals of the Pomonal area, the Grampians’’. Victorian Nat. 93, 138-147. Wakefield, N.A. (1971). ‘‘The Brush-tailed Rock Wallaby (Petrogale penicillata) in western Vic- toria’’. Victorian Nat. 88, 92-102. Wakefield, N.A. (1974). ‘‘Mammals of western Vic- toria’’. p.35 in: Proc. Symp. the Natural History of Western Victoria (eds. M.H. Douglas and L. O’Brien — Aust. Inst. Agric. Sci.). Australian Natural History Medallion Fund Amount on hand Mr Graeme Love Total December 1980 (Third Donation) February 1981 $1543.50 10.00 $1553.50 Vic. Nat. Vol. 98 A Short History of the Discovery and Naming of Banksias in Eastern Australia Part I Banks & Solander By A.I. SALKIN* It is now nearly 300 years since Euro- peans first collected plants in Australia. During that long period, collectors from practically all European countries col- lected and named material and stored it in public and private herbariums. One of the problems created for Australian taxonomists was the diversity of the botanists who named plants and the location of material used as type specimens. This series of articles at- tempts to give some sort of perspective to this problem. It does this by looking at one genus Banksia and traces the slow collection of species in eastern Australia and tries to make some sense of what is still a confused picture. The landing of Captain James Cook on the eastern seaboard of New Holland marks what most observers regard as the beginning of scientific botany in Australia. It also marks the beginning of study into an unusual and attractive genus in the family Proteaceae, the genus Banksia. Cook and in particular the ‘‘scientific gentlemen’’ Banks and Solander were, however, not the first men to make scientific collections in Australia; seventy-one years earlier in 1699 William Dampier had made two small but important collections in the vicinity of Shark Bay (Mueller, 1883; Osborne & Gardner, 1939; George, 1971) and a Dutch navigator possibly Willem de Vlaming (Brown, 1814) had collected in the region of the Swan River in 1697, two years before Dampier. Whilst no Banksia species are known to have been collected on these early *Science Departinent, Brentwood High School, Heath St. Glen Waverley, 3150. March/April visits, the occasions are worth recalling because they epitomise aspects of early botanical collections that create pro- blems for later botanists. In the case of Dampier the collection as far as we know was not described even though it was the first known authentic collection, and as the localities and dates of collec- tion are not given it is difficult even to speculate at which of his landing points the collections were made. The second known collection has even more problems associated with it than the first. In the herbarium of the Geneva Botanic Gardens are two specimens that could only have come from Western Australia. They bear the locality Java and were described by the Dutch botanist Burmann in 1768 as ferns but are the leaves and stems of Acacia trun- cata (Burm.f.) Hort. ex Hoffmsg, and Synaphea petiolaris (Burm.f.) Merrill. Robert Brown in his report on the botany of New Holland, (Brown, 1814) was aware of this discrepancy and com- mented: “The genus Synaphea seems to be confined to the south west coast of New Holland for it is more likely that Polypodium spinulosum of Burmannus (flor. ind. 233 t 67.f.1.) which I have formerly referred to this genus as well as Adiantum truncatum of the same author long since determined to be a species of Acacia by Mr Dryander were brought from that coast to Batavia by one of the Dutch navigators, perhaps Vlaming, than that they are really natives of Java, from which Burmannus received them.”’ The scientific collections of Banks and Solander were of an entirely dif- ferent order than the two known earlier collections; they are not only much more extensive but they also established the 69 methodology for collecting, drying and labelling specimens. Whilst fault may be found with the zoological specimens (Whitehead, 1969) the meticulous order of the botanical specimens enables later work to be done with confidence. Whilst only locations are given on specimen slips, these in conjunction with the jour- nals kept by Cook, Banks and Solander (Beauglehole, 1955, 1963; Solander, 1770), as well as the ship’s log enable us to give fairly accurate locations and dates for any of the 600 species collected in Australia, and more important, it allows us to correct species determina- tion if a species is known not to grow at a particular locality. On April the 30th, 1770, Cook landed on the Australian continent for the first time at a place he first called Stingray Harbour (then Botanists Bay, and final- ly Botany Bay) (Wharton, 1893, Beauglehole, 1955). The scientific gentlemen collected one hundred and sixty one species of plants and there is evidence from manuscripts that they may also have collected a further eleven species. A recent vegetation survey (McKern, 1965) of the landing area lists only twelve species not collected or men- tioned by Banks and Solander. Many duplicates of each species were col- lected. In the case of Banksia in- tegrifolia for instance there are fifty five known duplicates (McGillivray personal communication). It is little wonder then that Cook remarked in his log: “The great quantity of plants Mr Banks and Dr Solander found in this place occasioned my giving it the name of Botany Bay." At this site, four Banksia species were collected. These were what we now know as B. serrata, (the lectotype for the genus), B. integrifolia, B. ericifolia, and B. robur, A further species was collected when the ship was careened in the Endeavour River after being holed on the Great Barrier Reef; this was the only tropical species, B. dentata. Solander in his manuscript (Solander, 1770) regard- 70 ed this as the same broad leaved species collected at Botany Bay which we now know could only have been B. robur. The National Herbarium of Victoria has many of the duplicates of the Banks and Solander collection and among these is one labelled B. dentata, the collection site is given as Stingray Bay, the previous name for Botany Bay. If the collection site label is correct, the specimen cannot be B. dentata and can only be B, robur. It is somewhat dif- ficult from the material and from its condition to distinguish it from B. den- tata and as the phytoglyphs xx of the two species are similar, this is also no help even if material could be obtained for analysis. There is, however, the suspicion that this is the species collected at Botany Bay that Solander assumed was the same as the species collected at the Endeavour River. The ship reached England in July 1771 and the ambitious plans for what at that time was one of the greatest scien- tific collections did not come to fruition, There are many reasons for this. There is the involvement of Banks in other ac- tivities but the most plausible reason is that most botanists were daunted by the magnitude of even giving names to the vast quantity of material brought back. Sir Edward James Smith in his “A Specimen of the Botany of New Holland”’ (1793) gives some insight of the task facing botanists of his day. “When a botanist enters on the in- vestigation of so remote a country as New Holland, he finds himself as it were in a new world. He can scarcely meet with any certain fixed points from whence to draw his analogies; and even those that appear most promising, are frequently in danger of misleading, in- stead of informing him. Whole tribes of plants, which at first sight seem familiar to his acquaintance as occupying links in Nature’s chain, on which he has been ac- customed to depend prove on nearer ex- amination, total stranger, with other configurations, economy, and qualities. Vic, Nat. Vol. 98 Not only are all the species that present themselves new, but most of the genera, and even natural orders.’’ The collection came to be known as Banks cabinet, (Stafleau, 1966) and was added to by collectors whom Banks employed. It was on Cook’s third and fatal voyage of exploration that a fur- ther Banksia species was added to the collection. This was collected by David Nelson at Adventure Bay, South Bruny Island, Tasmania in 1776 and is the species we now know as B, marginata. It was not until 1781 that any of the six Banksia spp. so far collected were described and then only four of the six in Banks’ herbarium were described. The description was published in a sup- plement to Linnaeus’s ‘‘Genera Plan- tarum’’ in 1781, not by Linnaeus who had died in 1778, but by his son Carl von Linne. The Spanish botanist Antonia Jose Cavanilles in the ‘‘Anales de Historia Natural’’, (Cavanilles, 1800) relates how initially the German botanist Forster, who was Banks’ collector on Cook’s second voyage, named a number of species from New Zealand, Banksia, after Banks. Carl von Linne thought these were not a new genera but members of the genus Passerina. He therefore used the name Banksia for the four species from Australia. The species from New Zealand were however members of a new genus and their re- discoverer, Gaertner, in order to avoid confusion, named them Pimelia. xx phytoglyphs are preparations made from leaf cuticle and are often specific for a Linnean species and sometimes even show variation at the sub species level. REFERENCES Beauglehole, J.C. (ed.) 1955-69. The Journals of Captain James Cook on his Voyages of Discovery. Hakluyt Society, Cambridge. Beauglehole, J.C. (ed.) 1963, The Endeavour Jour- nal of Joseph Banks. Vol.2. Angus and Robert- son. Cambridge Brown, R. 1814. Botany of Terra Australis. In M. Flinders. Voyage to Terra Australis Vol, 2 Nicol. London, Cavanilles, A.J. 1800, Observations on the Soil, natives and plants of Port Jackson and Botany Bay. Anales De Hist. Nat. 3. 181-245. Trans. R.J. Dorr. George, A.S. 1971. The plants seen and collected in North-Western Australia by William Dampier W.Aust. Nat, 11,8. 173-8 Linne, Carl von (Linnaeus Filius) 1781. Supplemen- tum Plantarum McKearn, J.G. 1965 Vegetation survey prepared for Royal Botanic Gardens, Sydney. Distributed by N.S.W. Nat. Parks and Wildlife Service. Mueller, F. 1883. The Plants Indigenous Around Shark Bay and its Vicinity. Parlt. Paper No. 26 Government Printer: Perth. Osborne, T. G. B,, and Gardner, C. A. 1939 Dam- pier’s Australian Plants. Proc, Linn. Soc. Lon- don session 151, Pr 2: 44-50 Smith, J. E. 1793-5 A specimen of The Botany New Holland. Sowerby: London. Solander, D. C. 1770. Unpublished notes and descriptions, now in The Department of Botany British Museum (Natural History), London, Stafleau, F.A. 1966, Introduction to the facsimile edition of Novae Hollandiae plantarum specimen (la Billardiere 1804 Historia Naturalis Classica, Weinberg. Wharton, W. J. L. (ed.) 1893 Captain Cook’s Jour- nal During his First Voyable Round the World Made in H.M. Bark Endeavour 1768-71. Elliot Stock: London. Whitehead, P.W.P. 1969. Zoological Specimens from Captain Cook’s Voyages. J. Soc. Biblphy. Nat. Hist. 5:3, 161-201. New Book **Flowers and Plants of Victoria and Tasmania’’ G. R. Cochrane, B, A. Fehrer, E. R. Rotherham John and Marion Simmons, J. H. Willis 176 pages, 653 Color Plates, Index for Victoria. Index for Tasmania Price $23.95 (Discount to members) Postage $1.00 50km, $1.40 Vic. Order from Sales Officer F.N.C.V. March/April 71 Mammals and Birds in Part of the Cobaw State Forest, Victoria By M.W. Boyce*, K.A. BOUNDY* and D.D. HANSON* Study area The Cobaw State Forest (See Figure 1) is 2,440 ha of open forest II (sensu Specht 1970) situated in the Cobaw Range which forms part of the huge granitic outcrop known as the Cobaw batholith extending from Kyneton to Pyalong. Soil is friable red gradational. The study area, approximately 13 km from Lancefield and at an altitude of 675 m, comprises 2.5 ha in the northern section of the Forest. The area was last burned by the Forests Commission in 1970. Much of the area is littered with fallen trees, a legacy of logging and storm damage. Granite boulders and outcrops are scattered throughout the area and these, together with the fallen trees, provide potential cover for small ground dwelling mammals. Average an- nual rainfall is 750 mm. The area was chosen as it represents the vegetation type of the Forest. The canopy is comprised of Messmate (Eucalyptus obliqua) and Manna Gum (£. viminalis). Selective felling of mature trees occurred up to 1972. The burned out remains of some large Messmates exist, two of which have a circumference of 8 m at breast height in- dicating that the area once had some very large trees, although now the oldest trees are mainly 15 m high. The understorey is sparse consisting almost entirely of Silver Wattle (Acacia dealbata), the majority of which are thin and straggly with only a small number reaching a height of 2.5 m. The ground layer ranges from sparse to areas where there is a dense mixture of grasses and sedges or dense patches of * Toorak State College, P.O. Box 224, Malvern Vic, 3144 72 COBAW STATE PYALON Pee A “ : ‘ \ KYNETON a) \ \ [LANCERIELD i \ | ] \ ] | | \ © \@MELBOURNE a ny \ a aN j me f / w 3 N —ee 5 Sy. =. ete r ae one i. ~ — - Wwe Fig. 1. Location of Cobaw State Forest Austral Bracken (Pteridium esculentum). Common species among the ground layer include Greenhood or- chids (Pterostylis spp), Pink fingers (Calendenia carnea), Common. bird- orchid (Chiloglottis gunni), Clematis (Clematis aristata), Bidgee-widgee (Acaena_ anserinifolia), Ivy flat-pea (Platylobium triangulare), Cut-leaf cranesbill (Geranium solanderi), Ivy- leaf violet (Viola hederacea), Purple violet (V. betonicifolia), Prickly woodruff (Asperula scoparia), and Austral bears-ear (Cymbanotus preissianus). Methods Field work took place during a six week period of October and November 1980. Vic. Nat. Vol. 98 Trapping, spotlighting, observation by day and interpretation of skeletal materials, tracks, scratchings and faeces were the methods by which animal presence was noted. However, only species actually captured or positively sighted are included in the results sec- tion. One hundred trap sites were establish- ed on a 500 x 500 m grid using a 50 m grid interval. Trapping took place on three consecutive nights for each of three consecutive weeks (900 trap nights). Wire cage traps (36cm x 20cm x 16cm), baited with a mixture of honey, rolled oats and peanut butter, were set out each afternoon and checked early the next morning. Spotlighting was undertaken between dusk and 2230 hours using a 12 volt seal- ed beam spotlight and battery. Mam- mals sighted were recorded together with location and, in the case of ar- boreal animals, the species of tree in which they were observed. Although it was not possible to cover the whole area by spotlighting, enough residual timber tracks and animal pads existed to allow a significant proportion of the area to be surveyed. Rain and heavy winds limited spotlighting to five hours. Whilst working in the study area birds were observed with the aid of Pentax 8 x 40 binoculars. Calls were used to deter- mine presence of some species but only those actually sighted in, or flying above, the study area were recorded. Results Ten species of mammals were record- ed and are listed in Table 1. Table 2 lists the birds observed with those most com- monly recorded asterisked. Bats were seen by spotlight but none were captured or positively identified. Discussion The diversity of the mammal com- munity found was low but might have been higher if the area had been sampled over a longer period of time. Other March/April species that have been recorded in the Forest are the Feathertail Glider (Acrobates pygmaeus) and the Tuan (Phascogale tapoatafa), (Mammal Survey Group of Victoria, pers. comm.). Scratchings and faecal evidence strongly suggest the presence of Echidna (Tachyglossus aculeatus) or Bandicoots. There was little blossom available for birds during the period of the survey. However, there was an abundance of in- sect life which probably explains why most birds observed were insectivorous. TABLE 1 Mammals recorded in the study area Species Number Recorded Rate per * 100 trap nights 100 spotlight hours A. Trapped Trichosurus vulpecula 4 Pseudocheirus perigrinus i Antechinus stuartii 48 Rattus rattus 9 Felis catus I CS -Hourk B. Spotlighted Macropus giganteus Pseudocheirus perigrinus Petaurus breviceps Phascolarctos cinereus s C. Sighted Macropus giganteus Wallabia bicolor Phascolarctos cinereus Oryctolagus cuniculus —-NwWS * 900 Trap Nights 5 Spotlight Hours TABLE 2 List of birds seen in the study area Brown goshawk Accipiter fasciatus (Vig. and Horsf.) Wedge-tailed eagle Aquila audax (Latham) Sulpher-crested cockatoo Cacatua galerita (Latham) Crimson rosella Platycereus elegans (Gmelin) Golden bronze cuckoo Chrysococcyx lucidus (Gmelin) Boobook owl Nivox novae-seelandiae (Gmelin) Kookaburra Dacelo gigas (Boddaert) Sacred kingfisher Halcyon sancta (Vig. and Horsf.) Superb blue wren Malurus cyaneus (Latham) 73 White-browed scrub wren Sericornis frontalis (Vig. and Horsf.) Brown thornbill* Acanthiza pusilla (White) Yellow-tailed thornbill Acanthiza chrysorrhoa (Quoy and Gaim) Grey fantail* Rhipidura fuliginosa (Sparrman) Eastern yellow robin* Eopsaltria australis (White) Scarlet robin* Petroica multicolor (Gmelin) Rufous whistler Pachycephala rufiventris (Latham) Golden whistler* Pachycephala pectoralis (Latham) Grey shrike-thrush * Colluricincla harmonica (Latham) White-throated treecreeper* Climacteris leucophaea (Latham) Red-browed treecreeper Climacteris erythrops (Gould) Spotted pardalote* Pardalotus punctatus (Shaw and Nodder) Yellow-faced honeyeater Meliphaga chrysops (Latham) White-eared honeyeater Meliphaga leucotis (Latham) White-throated honeyeater Melithreptus albogularis (Gould) White-naped honeyeater* Melithreptus lunatus (Vieillot) Australian magpie Gymnorhina tibicen hypoleuca (Latham) Grey currawong Strepera versicolor (Latham) Australian raven Corous coronoides (Vig. and Horsf.) Little raven Corous mellori (Mathews) Acknowledgements This report is based on part of a study carried out with support from a research grant from Toorak State College. The assistance of Mr Ivan Franklin from the Forests Commission of Vic- toria, Macedon Office is gratefully acknowledged. Protected species of mammals were handled under the provision of a permit issued by the Fisheries and Wildlife Division, Ministry for Conservation. REFERENCE Specht, R. L. (1970) Vegetation. In Leeper, G. W. (ed.), The Australian Environment. C.S.1.R.O., Melbourne. A Note to Prospective Authors Contributions to The Victorian Naturalist are sought which deal with any aspect of natural history, field biology or earth science, but which preferably have a Victorian em- phasis. Intending authors are requested to forward two copies of their manuscript, if possible typed and double spaced, to the editor. Acceptance is subject to approval by the referees and editor. Authors will receive galley proofs for checking; these should be returned promptly to ensure there are no delays in publication. Diagrams (in black ink on white card) and photographs (black and white) may also be included and the details should be of sufficient size and clarity to enable suitable reduction. Authors will receive 25 reprints gratis. If more are re- quired, then orders should be made directly with the printer when proofs are forwarded for correction. 74 Authors are also requested to forward nature notes describing interesting observa- tions, experiences or results of experiments which might not warrant inclusion in the journal as a full scientific paper because of their nature or size. Notes are usually refereed, but free reprints are not supplied. Reviews of books may also be sent to the editor, Another form of contribution sought from authors is that of the general or review natural history article. Unlike scientific ar- ticles, these need not present data from “new’’ observations or experiments; rather, such general articles could review current knowledge, discuss the historical bases or highlight some significant aspects of our natural history. Style of all contributions should follow that in current issues. Vic. Nat. Vol. 98 N.T. Burbidge Memorial Lecture The Burbidge Memorial Lecture was instituted by the Australian Systematic Botany Association in honour of Nancy Tyson Burbidge, for many years curator Herbarium Australiense and at the time of her death Director Flora of Australia project. Throughout her long and distinguished career she promoted an interest in Natural History and published non-technical books on eucalypts, wattles and grasses. Amongst her technical writings was a note on Ixodia published in the Victorian Naturalist (75: 95-6, 1958). The following address was the second to be delivered and was presented at a meeting of the Australian Systematic Botany Association held in conjunction with ANZAAS in May 1980. Seedlings and the Australian Flora By H.T. CLIFFORD* It is a high honour to be invited to dicotyledons largely because they deliver this memorial address and it is with a sense of humility that I do so for we have met to honour the memory of a distinguished and versatile colleague. Nancy Burbidge was a botanist in the widest sense and published important papers in plant ecology, geography and taxonomy. In addition, she produced several basic bibliographic treatises and wrote or contributed to a number of ex- pository floras and handbooks. This evening’s address is concerned with seedlings. For those of you who may think them dull I can only say that I share the opinion of Topp (1890) who claimed in his Presidential address to the Victorian Naturalists, they were ‘‘a most interesting and suggestive subject’’. In discussing the seedlings of Australian plants I believe I am touching upon a relatively neglected area of study, though one with a long history. However, since seedlings can usually be studied with relatively little equipment or funds they may well prove to be more popular in the immediate future than in the past. The discussion will be restricted to the seedlings of *Department of Botany University of Queensland St Lucia, Qld. 4067 March/April display a bewildering array of diversity as compared with those of the mono- cotyledons. The raising of seedlings can be a pleasurable occupation but is at times frustrating for so many species require somewhat specialized conditions to ger- minate successfully. In addition there are innumerable hazards to which the seeds and seedlings may fall victim. These have been admirably summarized as follows, with reference to seedling Eucalypts. *‘One reason why these records are in- complete is that during a generation seedlings have disappeared at various stages through accident, climatic changes, attacks by insects and animals, and the various happenings of a nursery’ (Maiden, 1933). A problem I failed to anticipate was that of seedlings being crushed by cane- toads squatting in pots! Of the many aspects of plant science to which a knowledge of seedlings may contribute, only five will be considered. The choice is quite idiosyncratic and reflects my own interests in the subject over the past 30 or so years. Where references are cited they are generally the oldest of which I am aware 75 in order to stress the works of earlier botanists in this, a Memorial Lecture. (a) Taxonomy One of the earliest applications of seedling data to the classification of Australian plants was apparently due to De Candolle (1828) who divided the genus Eucalyptus into two sections on the basis of their possession or otherwise of alternate leaves. In reaching this deci- sion he was probably influenced by the descriptions of new species which at that time were often based upon immature specimens grown in pots (Maiden, 1902). Though in this instance the role of seedling characters may have been misinterpreted their value in con- tributing to the taxonomy of Eucalyptus was later re-affirmed by Mueller who in his account of E&. cornuta in the Eucalyptographica wrote, ‘‘The study of Eucalypts in their earliest stages of growth for aiding in their specific discrimination is important, as shown in the text and lithograms of several species in the present work’’, (Mueller, 1883). In a like vein Bailey supported the raising of seedlings for the elucidation of relationships amongst taxonomically difficult groups. Thus in discussing Smilax australis R.Br. he said, ‘‘There are doubtless several forms or species amongst the specimens generally regard- ed as S. australis R.Br., but these cannot be described until they are brought under cultivation and the plants studied at all stages of their development’’, (Bailey, 1902). Yet another plea for the incorporation of seedling data into taxonomic studies is found in a revision of some Angophora species where it is stated, “‘An investigation of the seedlings, not merely increases our knowledge of plants, but it puts in our hands frequent- ly a means of differentiating species and varieties that is likely to be of very great value. This is affected both by the in- formation gained from the form of 76 cotyledon leaves, and also that of the primary or juvenile leaves, which so fre- quently differ from those of the mature plant”’ (Hall, 1913), Notwithstanding the usefulness of their advice these earlier writers have been largely ignored and relatively few modern taxonomic revisions make any reference to seedlings. The taxonomic significance of the seedling derives principally from its morphology and all its parts contribute information. Readily observable characters are the numbers, size and shape of the cotyledons as well as the form of the earliest leaves. With respect to the cotyledon number it was early reported that the seedlings of Nuytsia possessed several cotyledons (Drum- mond, 1839) and it is probable that Brown (1810) even earlier observed a plurality of cotyledons in Persoonia seedlings. Later records of genera with mainly polycotyledonous seedlings in- clude Pittosporum (Galbraith, 1947) and /diospermum (Blake, 1972). Whilst tricotyledonous individuals oc- cur infrequently amongst the seedlings of most species of dicotyledons they oc- cur with relatively high frequencies amongst the progeny of Melaleuca quin- quenervia (3-4%) and Aegiceras cor- niculatus (5-10%). Amongst the dicotyledons cotyledon shape and size is quite diverse. In some families such as the Bignoniaceae the cotyledons of the different species are remarkably similar, in other families in- cluding the Proteaceae the cotyledons of the different species assume a wide range of shapes and sizes. The tax- onomic significance of the cotyledons varies from group to group but clearly cannot be ignored. (b) Genetics Segregation amongst the seedlings raised from individual plants is often ac- cepted as an indication that they are of hybrid origin. The segregation may be extensive as has often been shown for Vic. Nat. Vol. 98 suspected Eucalyptus hybrids (McAulay, 1938; Brett, 1938), or it may involve the production of only two seedling types. An example of the latter situation was reported by Hall (1910) for the genus Acacia. Here seed was collected from a cultivated tree of A. baileyana which was growing near to A. decurrens. Both trees had been in flower at the same season. On raising seedlings it was found that about 20% were hybrids, as judged from their morphology, the re- mainder resembling those of the seed parent. In a like manner the progeny of wild plants of Banksia oblongifolia growing in south-east Queensland are often of two kinds. In some years, up to 6% of the seedlings raised differ from those typical of the species and grow into plants intermediate in morphology be- tween B. oblongifolia and B. robur. Such intermediate morphology suggests the aberrant plants are Fi hybrids and their frequencies provide an estimate of the amount of pollen transfer between the parent species. In contrast to segregation amongst sibl- ings extreme uniformity of seedlings from a single plant is suggestive of apomictic reproduction. Another in- dication of apomixis is the occurrence of polyembryony, a phenomenon which is readily detected when the number of seedlings to emerge is in excess of the number of seeds sown. Apomixis is widespread in the Australian flora and polyembryony has been reported to oc- cur in several genera including Cassia (Symon, 1956) and Casuarina (Barlow, 1958). (c) Morphology The evolutionary and hence tax- onomic significance of the morphology of juvenile foliage as a reflector of phylogenetic relationships is widely ac- cepted. In support of this viewpoint the seedlings of phyllode bearing Acacia spp. are generally, cited for their initial March/April leaves are pinnate or bipinnate. Similar- ly the entire-leaved species of Dodonaea have seedlings with deeply dissected leaves such as are commonly en- countered amongst members of the Sapindaceae. As both Acacia and Dodonaea are widely distributed genera with many species growing in dry to semi-arid en- vironments their joint possession of a seedling type whose first leaves are dissected and later leaves are entire is an interesting example of evolutionary con- vergence. The widespread occurrence of heteroblasty in the Australian flora sug- gests the subject is of ecological and tax- onomic significance. This viewpoint was appreciated by Diels (1906) who drew heavily on Australian examples to il- lustrate his book on juvenility and floral maturity in the plant kingdom. Furthermore, the experimental mor- phologists have long used phyllodineous Acacia spp. to investigate the influence of the environment on the transition from normal leaves to phyllodes. Thus Goebel (1905) wrote ‘‘It is easy to see the formation of phyllodes is no longer under the direct influence of outer con- ditions for the seedling plants of Acacia which I examined formed phyllodes even though they were cultivated in a very moist chamber.’’ As this quote is from an English edition of an earlier published German text the experiments must have taken place before the turn of the century. (d) Germination Amongst the dicotyledons there are two basic types of seedling development. With one, the cotyledons remain within (cryptocotylar) and with the other the cotyledons are withdrawn (phanerocotylar) from the testa. As a rule cryptocotylous seedlings exhibit hypogeal germination and phanerocotylous seedlings epigeal but there are exceptions in that some species e.g. Alyxia ruscifolia have seedlings in 7 which the cotyledons are raised above the ground and are hence epigeal but none-the-less remain enclosed in the testa and so are cryptocotylar. It is generally agreed that epigeal (mostly phanerocotylar) germination is primitive in dicotyledons (Eames, 1961) and that the hypogeal (mostly cryp- tocotylar) condition is advanced. The basis of this opinion is rarely argued and presumably rests on the widespread oc- currence of phanerocotyly amongst dicotyledons. Examination of a sample of several hundred species belonging about two hundred Australian genera has shown that germination behaviour is far from randomly distributed within the docotyledons. If the genera are grouped into the superorders of Dahlgren (1975) only 12 of the 22 for which data are available have cryptocotylar seedlings. Amongst these the condition is relatively common only in the Magnolianae, Nym- phaeanae, Theanae and Hamamelidanae taxa. And so, on the basis of its taxonomic distribution cryp- tocotyly would appear to be a primitive rather than an advanced trait in dicotyledons. In addition to its phylogenetic significance the mode of germination may also be of taxonomic importance. For example, in the genus Drosera both phanerocotylar and cryptocotylar species occur. From the few Australian species studied it would appear the two sections of the genus are characterized by different germination patterns. Members of the sect. Rorella (D. binata) have phanerocotylar and members of the sect. Ergaleium (D. peltata and D. auriculata) have cryptocotylar germina- tion (Vickery, 1933). (e) Ecology For the ecologist, seedlings are often a source of embarrassment in that though they are often present in study areas their identities are usually unknown. With current ecological interests turning 78 more and more to vegetation dynamics it is probable that special keys to seedl- ings will be required. Fortunately, there are a multitude of characters available and such keys are not difficult to con- struct. The ecological significance of the cotyledons was appreciated long ago for Acacia seedlings by Cambage (1915) who noted, ‘‘The cotyledons of A. stenophylla, Bidwilli and Farnesiana are fairly fleshy while those of A. pendula and A. aneura are slightly less so. The significance of the geographical distribution of the fleshy cotyledons will be discussed in a later paper after more evidence becomes available, but this form appears to be one which is able to exist in areas where the climate is subarid, or where the rainfall is confined mainly to one season of the year.’’ Un- fortunately, the promised paper was ap- parently never published. As distinct from its morphological im- portance, germination pattern is also of ecological significance as has been shown by Jackson (1974) in his study of regeneration in African savannahs. He postulated that cryptogeal (plumule car- ried below ground by elongating petioles of cotyledons) germination was an adap- tation to fire. About Brisbane no cryp- togeal species have been encountered but dicotyledonous species with cryp- tocotylar germination occur in much greater proportion in rainforest than in Eucalyptus-forest communities so pro- tection of the plumule is in this instance not against fire. The selection force favouring cryp- tocotylar germination in rainforests is apparently grazing and for all species tested with cryptocotylar germination the experimental removal of the primary axis has lead to the production of new shoots from the axillary buds of the cotyledons. In view of the correlation between the taxonomic position of species and their germination patterns it is probable that species with cryptocotylar or cryptogeal Vic. Nat. Vol. 98 germination are pre-adapted to the savannah environment in that they were derived from taxa already possessing that character. As yet no example of species with cryptogeal germination ap- pears to have been recorded for Australia. It is appropriate in concluding these remarks on the ecological importance of seedlings to draw attention to two papers by Nancy on the germination of Australian Chenopodiaceae (Burbidge 1945, 1946). In these works she made it clear that a knowledge of seedling behaviour in the field is a prerequisite to an understanding of the regeneration of plant communities. From the foregoing it is clear that the seedlings of Australian Magnoliatae have contributed much to our knowledge of several aspects of botany and that they are indeed, ‘‘an interesting and suggestive subject’. The long record of publications on Australian seedlings and their diversity bring them I believe within the range of interests of Nancy Tyson Burbidge who not only had a deep appreciation of plants but also of history. REFERENCES Bailey, F.M. 1902. Flora of Queensland. Vol. 5. Brisbane Govt. Printer. Barlow, B.A. 1958. Heteroploid twins and apomixis in Casuarina nana Sieb, Aust, J. Bot., 6, 204-219. Blake, S.T. 1972. Idiospermum (Idiospermaceae), a new genus and family for Ca/ycanthus australien- sis. Cont. Qld Herb, 12, 1-37. Brett, R.G. 1938. A Survey of Eucalyptus species in Tasmania. Pap. and Proc. Roy. Soc. Tas. 1937, 75-109, 2 plates. Brouwer, Y.M. 1979, Domatia in Seedlings. Flora Malesiana Bull. 32, 3239-46. Brown, R. 1810. Prodromus florae Novae Hollan- diae et Insulae van-Diemen. London. Burbidge, N.T. 1945, Germination studies of Australian Chenopodiaceae with special reference to the conditions necessary for regeneration. I. Atriplex vesicarium Heward. Trans. Roy. Soc. S. Aust, 69, 73-85. March/April , 1946. Germination studies of Australian Chenopodiaceae with special reference to the con- ditions necessary for regeneration, II. (a) Kochia sedifolia F, vy M., K. pyramidata Benth., (c) K. georgei Diels. Trans. Roy. Soc. S. Aust. 70, 110-120, Cambage, R.H. 1915, Acacia seedlings, Pt, 1. Jour, and Proc. Roy Soc. N.S.W. 49, 81-121, 12 plates. Candolle, A.P. de Prodromus systematis naturalis regni vegetabilis. Vol. 3 pp. 216-222 (Eucalyptus) Paris. Treuttel & Wurtz. Dahlgren, R. 1975, A system of classification of the Angiosperms to be used to demonstrate the Distribution of Characters, Bot. Notiser 128, 119-147. Diels, L. 1906. Jugendformen and Blutenreife im Pflanzenreich, Berlin. Borntraeger. Drummond, J. 1839 cited in Fletcher, J.J. 1909. Il- lustrations of Polycotyledony in Persoonia, with some reference to Nuytsia (N.OO. Proteaceae and Loranthaceae). Proc. Linn. Soc. N.S.W. 33, 867-882, plates 34 and 35, Eames, A.J. 1961. Morphology of the Angiosperms. New York, McGraw-Hill, Galbraith, J. 1947 Seedling habit of Pittosporum bicolor. Vic. Nat, 63, 228. Goebel, K. 1905 Organography of Plants, Pt II. (trans. 1.A. Balfour), Oxford. Clarendon Press. Hall, C. 1910 Notes and Exhibits. Proc. Linn. Soc. N.S.W. 35, 310. 1913 The Seedlings of Angophoras with descrip- tion of a new species. J. and Proc. Roy. Soc. N.S.W. 47, 98-105, 3 plates. Jackson, G, 1974 Cryptogeal germination and other seedling adaptions to the burning of vegetation in savanna regions: The origin of the pyrophytic habit. New Phytol. 73, 771-780. McAuley, A.L. 1938 Evidence for the Existence of a Natural Hybrid between Eucalyptus globulus and Eucalyptus ornata. Pap. and Proc. Roy. Soc. Tas. 1938, 45-46, | plate. Maiden, J.H. 1902 Is Eucalyptus variable? Jour. and Proc. Roy. Soc. N.S.W. 36, 315-40, 1935 A Critical Revision of the Genus Eucalyptus 8, 123, Sydney. Govt. Printer. Mueller, F.M, 1883 Eucalyptographia, A Descrip- tive Atlas of the Eucalypts of Australia, Decade 9. Melbourne Govt. Printer, Sporne, K.R. 1969 The Ovule as an Indicator of Evolutionary Status in Angiosperms. New Phytol. 68, 555-566. Smith, J. 1841 Cited in Heslop-Harrison, J. 1955, New Concepts in Flowering-Plant Taxonomy. London, William Heinemann. Symon, D.E. 1956 Polyembryony Nature, Lond. 177, 190. Topp, C.A. 1890 Presidential Address. Vic. Nat. 7, 1-8, Vickery, J.W. 1933 Vegetative reproduction in Drosera peltata and D. auriculata. Proc. Linn. Soc, N.S.W. 58, 245-269. in Cassia. 79 An Extra Plant Record for Tasmania By JOHNS. WHINRAY* Some plants that occur on the Australian mainland are found in Tasmania only on Bass Strait islands (Curtis, 1956; 1963; 1967). On some eastern Tasmanian Bass Strait islands I have found previously thirteen more plants which, in the Australian region, were not known to occur south of Vic- toria (Whinray, 1973). This note records the extension of the range of the bogrush Schoenus carsei Cheesem. to Cape Barren and Clarkes Islands in south-eastern Bass Strait. The species was thought to be confined to South Australia, Victoria and New Zealand (Black, 1960; Eichler, 1965; Willis, 1973), until my specimens were determined. Cape Barren, of about 44 000 hec- tacres in area, is the second largest island of the Furneaux Group and Clarkes, of about 9 000 hectares, is its third largest island. Cape Barren Island Records. My first record of Schoenus carsei was made at Prickly Bottom Flat in the north-west of the island on 9 January 1970 (MEL, HO).** Next I collected it by the north coast on Chimney Hill Flat near Victualling Office Bay on 8 June 1970 (MEL). Since then I have obtained specimens from one more Prickly Bottom Flat locality (MEL, AD, CANB), and from two localities at Kents Bay in the south- eastern part of the island (MEL, AD, CANB). I have also recorded it at five other Prickly Bottom Flat sites and in six more places in the south-eastern part of the island. Two of the latter records were made at Kents Bay. Schoenus carsei occurs in permanent- *Flinders Island, Tasmania, 7255, **Specimens lodged in Australian herbaria are in- dicated by the standard abbreviations for those in- stitutions, 80 ly damp or wet places such as springs, bogs, stream margins, bottoms and peaty flats. The associated plant species vary from place to place. Two very different sites will now be described briefly. One very wet Prickly Bottom Flat site was the edge of Bull Scrub Creek, about one kilometre south-east of its mouth. At this spot the shrubs were short, hay- ing regrown since a fire of about four years before (c. 1972). They were Manuka Leptospermum _ scoparium, Bushpea Pultenaea dentata, Slender Honey-myrtle Melaleuca gibbosa, Swamp paperbark Melaleuca ericifolia, Scented Paperbark M. squarrosa, and Bluntleaf Heath Epacris obtusifolia. The six rushes growing in this associa- tion included Sea Rush Juncus krausii, Schoenus carsei, and Slender Twigrush Baumea gunnil. The other herbs includ- ed Angled Lobelia Lobelia alata, Mossy Pennywort Hydrocotyle muscosa, and Tufted Centrolepis Centrolepis fascicularis. The driest site on Prickly Bottom Flat was a small bottom on its western side, about one kilometre south-south-west of the mouth of Hammonds Creek. The dominant species there was Pithy Swordsedge Lepidosperma longitudinale growing to one metre high. Associated with it were a few clumps of Coast Sawsedge Gahnia trifida to 1.2 metres high. As the area had been fired about three years previously (c. 1973), all the shrubs were lower than the swordsedge. They were Manuka Leptospermum scoparium, Slender Honey-myrtle Melaleuca gibbosa, Heath Honey- myrtle M. squamea, Bushpea Pultenaea dentata, Dagger Hakea Hakea teretifolia and a Guineaflower Hibbertia sp. Some of the herbs of this site were Everlasting Helichrysum dealbatum, the Vic. Nat. Vol. 98 exotic White Cudweed Gnaphalium candidissimum, Spreading Roperush Calorophus laterifolius, and Schoenus carsel. Clarkes Island Record. The one occurrence of Schoenus carsei on this island was found on 25 September 1976 in a small depression about 300 metres south-west of the southernmost part of Sandy Lagoon. The site is at the southern edge of the many old consolidated dunes of the San- dy Lagoon area and receives seepage from them. The vegetation was fired in about December 1974. The lowest part of the depression con- tained shallow water and had a domi- nant layer of much Pithy Swordsedge Lepidosperma longitudinale and occa- sional clumps of Coast Sawsedge Gahnia trifida. Lower herbs grew between the nor- thern edge of the tall sedges and the bank. The species included Schoenus carsei, Longleaf Wallabygrass Danthonia longifolia, which is rare in Tasmania (CANB), and Centella Centella cordifolia. Schoenus carsei was collected just above the water level on the damp nor- thern bank of the depression (MEL, CANB). The low shrubs with it were Pink Swampheath Sprengelia incarnata, Slender Honey-myrtle Melaleuca gibbosa, Scented Paperbark Melaleuca squarrosa and Swamp Boronia Boronia parviflora. The herbs there were Pale Twigrush Baumea acuta, Everlasting Helichrysm dealbatum and Grassy Rush Juncus caespiticius. Comment Most of the central and eastern Cape Barren Island has been recommended as a potential Wilderness Reserve (Whinray, 1977; Russell, et al/., 1979). This extra record for Tasmania increases the number of unusual plants known to occur in the potential reserve and adds to its interest. Acknowledgements Miss M.H. Christie provided con- siderable assistance with many Cape Barren Island trips. Mr G.W.G. Goode generously lent his boat on several occa- sions. Dr J.P. Jessop, of the State Her- barium, Adelaide, first determined one of my collections as Schoenus carsei. Dr J.H. Willis soon afterwards determined further material. Mr R.B. Filson made helpful comments on two late drafts of this note. REFERENCES Black, J.M., 1960 Flora of South Australia, 1. Government Printer, Adelaide. Curtis, W.M., 1956. The Student’s Flora of Tasmania, 1. Government Printer, Hobart. A Aston , 1963. The Student's Flora of Tasmania, 2. Government Printer, Hobart. dit OF ,1967. The Student's Flora of Tasmania, 3. Government Printer, Hobart. Eichler, H., 1965. Supplement to J.M. Black’s Flora of South Australia, Government Printer, Adelaide. Russell, J.A., Matthews, J.H., & Jones, R. 1979. Wilderness in Tasmania. University of Tasmania, Hobart. Whinray, J.S., 1973. Some New Plant Records for Tasmania. Launceston Naturalist, 6(3): 5-6, a ea , 1977. Some Plant Records for the Cape Barren Island Wilderness Area. Tasmanian Naturalist, 51: 9-13. Willis, J.H., 1973. A Handbook to Plants in Vic- toria, I. Second edition. Melbourne University Press, Melbourne. New Book ‘*Life on the Rocky Shores of S.E. Australia’. G. Wescott, R. Synnot, H. Powell Pocket Guide 88 pages. Covers 70 species found along the sea-shore. Photographs and Line Drawings. Price $2.00, postage 50 cents. Order from Sales Officer F.N.C.V. March/April 81 Book Review Life on the Rocky Shores of S.E. Australia — an illustrated field guide. By G.C. Wescott, R.N. Synnot and H.K. Powell Available from ‘‘Rocky Shores’’, P.O. Box 154, Yarraville, Victoria, 3013. Price. $2.00 (plus 50¢ postage). This small book is intended as an inexpen- sive introduction to the life of the rocky shore for the untrained person. Its 84 pages cover over 70 species of the commonest plants and animals found on Victorian rock platforms, giving a brief description and notes on range, habitat and ecological relationships. Each species is illustrated either by a drawing or a photograph and the authors have confined themselves to the commonest, most readily encountered organisms. It is a pity that this book apparently had to be produced on a shoe-string. A reduction technique for this type, some professional help with design and more time and care taken with the illustrations could have resulted in a far deeper coverage for the same sized publication and a much more profes- sional looking production. Yet despite these considerable shortcomings the contents are basically sound and as a first introduction for the beginner in sea shore observation the book is well worth the very low purchase price. Brian J. Smith ‘Tasmanian Echinoderms’ By Alan Dartnall (‘Fauna of Tasmania’ handbook no.3, University of Tasmania, June 1980. 21 x 14.5 cm., 84 pp., stapled, soft cover. Available from ‘Fauna of Tasmania’ Office, University of Tasmania, Box 252C, G.P.O., Hobart, Tasmania, Australia. 7001. Price $3.75 (including postage and packing). Cheques and money orders to be made payable to the ‘University of Tasmania’.) In the absence of any book devoted to the echinoderm fauna of south-eastern Australia this hand- book is a welcome arrival. The University of Tasmania has com- menced the production of a series of handbooks and posters on the ‘Fauna of Tasmania’ with a view to collating the information now available and to stimulate interest in the Tasmanian fauna and flora. The intention of the Committee is to devote each handbook to a defined taxon, and to include a checklist, il- lustrated keys for identification, 82 distribution maps, a description of basic morphology, and an explana- tion of methods of collecting and preserving and examining specimens. Thanks to Alan Dartnall this has now been accomplished for the echinoderm fauna. Alan has worked on the taxonomy and biology of these animals for ten years, and wrote this handbook while he was working in the Zoology Department of the University of Tasmania. Half of the handbook is devoted to keys, which are not intended to have phylogenetic or extra- Tasmanian value. However, all but very few of the Victorian shallow water echinoderms are in_ the Tasmanian checklist and keys. Un- fortunately, there are too few of the very good line diagrams in the keys, and there is no glossary for the Vic. Nat. Vol. 98 handbook. I suspect that the keys will pose problems for the uninitiated. The only photographs which are reproduced in the booklet are the few which are included to illustrate ‘body form’. They give no indica- tion of the size of the respective animals, and they lack important taxonomic detail. However, they are useful for confirming identity in association with the keys and it is disappointing that so few are includ- ed. A quarter of the handbook is made up of a series of distribution maps for all of the species. Coded information on depth range and substrate is included with the maps. This is a most useful presentation of current knowledge about Tasma- nian echinoderms, and is an obvious stimulus and guide for field- workers. This aspect of the booklet is naturally of limited value for those interested only in Victorian marine fauna. The section of the handbook on collection, preservation, and ex- amination of specimens is disap- pointing. There is no indication of suitable concentrations for the nar- cotising agents. There is no indica- tion of how the neutral for- maldehyde solution for fixing can be made up. The suggestion that a low power dissecting microscope is suitable for examining the spicules of holothurians is quite misleading. A bibliography is included with the intention of complementing the major work on Australian echinoderms by H. L. Clark and in- troducing the reader to recent work. This handbook does _ bring together for the first time a great amount of information on the echinoderms of south-eastern Australia. Much of the information is relevant to the Victorian fauna, and the booklet is recommended for those who are professionally in- terested in the Victorian marine fauna. Mark O’Loughlin The Origin of Generic Names of the Victorian Flora Part 3 — Latin, Greek and Miscellaneous (Continued from page 225, Vol. 97, No. 5.) By James A. BAINES *Verbascum. The Lat. name for mullein, used by Pliny. Gaius Plinius Secundus, known in English as Pliny the Elder (born 23 A.D., died in the erup- tion of Vesuvius that destroyed Pompeii and Herculaneum in 79 A.D.), wrote ‘Historia Naturalis’ in 37 books, reprinted in Latin with English transla- tion in 10 volumes in Loeb Classical Library — a fascinating mixture of science and superstition. The word March/April mullein comes from Fr moulaine (probably from mol, soft), though Skeat suggests an Anglo-Saxon origin. Our species include *V. thapsus, Great Mullein, Blanket Weed, Flannel Leaf or Aaron’s Rod, and the other 2 species are also known as kinds of mullein. The genus is in family Scrophulariaceae. Thapsus is a superseded generic synonym of Aaron’s Rod (from Isle of Thapsos, thapsinos, yellow). 83 Verbena. Lat. verbenaca, name of the plant Vervain (which is an English form of verbena), from verbenae, boughs of olive, laurel, myrtle, cypress and tamarisk, carried in sacred ceremonies by the Fetiales (in Livy), and by certain Europe, but it is also native here. Our other 3 species are introduced, known as different kinds of verbena, although *V. bonariensis (— ‘from Buenos Aires’), Purple-top or Cluster-flower Verbena, is often called Squareweed, from its 4- priests (in Cicero). V. officinalis, Ver- sided stems, square in section. The vain, was given the specific epithet genus gives its name to family because it was used in herbal remedies in Verbenaceae. Omission Vol. 98 (1) The following text was mistakenly omitted from the article ‘Introduced Mam- mals in Victoria’ by H. Brunner, P. L. Stevens and J. R. Backholer which appeared in the last issue of The Victorian Naturalist. It is to be inserted on page 12, after line 33 (‘some $300,000 on dog control’’), Environmental aspects The disappearance of the Tasmanian tiger has left dingoes and feral dogs as the only large mammalian predators in Australia. Presumably their numbers are mainly determined by the availabili- ty of food and space. More factual in- formation is needed on the effect these predators may have had in the past on our wildlife and what effect they are having at the present time. Results of recent studies carried out in many parts of Australia suggest that well established native prey species are not endangered because of these predators. This is particularly true for the large areas of forest and desert not inhabited by man. In the cases of rare species, there is obviously reason for concern that dingoes, dogs and other predators may speed up the disap- pearance of these animals. Privately owned dogs which are often allowed to roam in packs through wildlife reserves, isolated bush blocks, forest parks and fringe areas of forests are undoubtedly a great menace to wildlife species in those areas. Wallabies, kangaroos and lyrebirds are often harassed and killed in some con- servation areas close to urban develop- ment. Attention, however, is mainly drawn to the bitter complaints of farmers who suffer frequent losses of livestock because of these killer dogs (M.M.B.W., Aberdeen et a/. 1977). 84 Another important aspect is the con- cern expressed by the dingo conserva- tionists who fear for the future of the pure dingo. They feel that this breed may eventually disappear because of continuing cross-breeding with domestic dogs. However, data for this contention are lacking. Control Few advances have been made in feral dog control and we are still using the traditional means of steel jaw traps and poison. Because of the elusive nature of dogs, other methods such as shooting or organized drives have generally proved unsuccessful. In Victoria approximately twenty dogmen are employed by the Depart- ment of Crown Lands and Survey in dingo and feral dog control. Most of these operators rely heavily on steel jaw traps, but some poisoning is used. Traps are set along forest tracks near places where dogs might defaecate or urinate. These traps are usually left in the one area for many weeks and visited at regular intervals. In many cases, dog faeces are used to lure the dogs into the traps. Unfortunately, trapping is a relatively non-specific technique and numbers of other animals (wallabies, wombats etc.) are often caught. For this reason, we are currently investigating more selective and also more humane types of traps and snares. Vic. Nat. Vol. 98 FIELD NATURALISTS CLUB OF VICTORIA Report by Executive Council The members of the Executive Council submit herewith balance sheet as at 31 December 1980 and income and expenditure account for the year ended on that date, and report as follows:- The Net Surplus of the Club for the year ended 31 December 1980 was $60 which, added to the Surplus brought forward at | January 1980 of $10,240, together with a transfer of $833 from Club Improvement Account, resulted in an Ac- cumulated Surplus to be carried forward to next year of $11,133. . The members of the Executive Council took reasonable steps to ascertain, before the income and expenditure account and balance sheet were made out, that all known bad debts were written off and adequate provision was made for doubtful debts. . The members of the Executive Council took reasonable steps, before the income and expen- diture account and balance sheet were made out, to ascertain that the current assets, other than debtors, were shown in the accounting records of the company at a value equal to or below the value that would be expected to be realised in the ordinary course of business. . At the date of this report, the members of the Executive Council are not aware of any cir- cumstances which would render the values at- tributable to the current assets in the accounts misleading. . No charge on the assets has arisen, since the end of the financial year to the date of this report, to secure the liabilities of another person. No con- tingent liability has arisen since the end of the financial year to the date of this report. . No contingent or other liability has become en- forceable or is likely to become enforceable within the period of twelve months after the end of the financial year which in the opinion of the members of the Executive Council will or may affect the ability of the Club to meet its obliga- tions as and when they fall due. . At the date of this report the members of the Executive Council are not aware of any cir- cumstances not otherwise dealt with in the March/April report or accounts which would render any amount stated in the accounts misleading. 8. The results of the Club’s operations during the financial year, in the opinion of the members of the Executive Council, were not affected by any item transaction or event of a material and unusual nature. 9. Since 31 December 1980, and to the date of this report, in the opinion of the members of the Ex- ecutive Council, no item transaction or event of a material and unusual nature has occurred, which would affect substantially the results of the Club’s operations for the next succeeding financial year. 10. No member of the Executive Council, since the end of the previous financial year, has received or become entitled to receive a benefit by reason of acontract made by the Club with the member or with a firm of which he is a member or with a company in which he has a substantial financial interest. 11. The principal activities and objects of the Club are to stimulate interest in natural history and to preserve and protect Australian Fauna and Flora. No significant change in the nature of those activities occurred during that period. 12. The names of the members of the Executive Council in office at the date of this report are as follows:- Dr B. Smith Miss M. Allender Miss W. Clark Mr D. Dunn Mr M. Howes Mr D. Jinks Miss L. Lumsden Miss M. Lester Mr J, Martindale Mr A. Thies Mrs H. Weatherhead This report is made in accordance with a resolution of the Executive Council dated 31st day of March 1981. B. Smith President D. 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Nat. Vol. 98 FIELD NATURALISTS CLUB OF VICTORIA BUILDING FUND Amount OF Pune at sh DeCeMOEr ISTO he ol dav pal La edas tA pase hs been tWrasderenas ed $5,486 [viterest on Investments. and Bank Account. ........cccccecesacsuctmaspenpaenaavacegens 514 NOU OF INEL AC Aad LOCO SSO sar sau FU cb be ise LCS LUE rtp ecereannsretnesreses $6,000 PUBLICATIONS FUND AEM aet MG thet SRE IOCENALOET LO Lae rcce stats ahi a c'nld c 64rd Kia abe g'a.c -4co10ey elela Cato doond.owdL ae yiy $27,479 Interest Gn Investments and Bank Account. 4... 40. ii dese ee eet acbyesuecevaneees 2,337 Surplus (Loss) for the year from — Pemnsof VictOria QnG A asinaniden: speeds teens 54s esuerde bes chabbactiara $1,960 Wild Flowers of Wilson’s Promontory National Park ............0. 50000005 25 SIPC COTUTM EE PRTABTIOLEES tiara rotate w Ess ly ceiera nat y Asda bee ow Ueto 6-4 ALK Ba te § (1) 1,984 PROT TIE Cte SL EMIAEE PW VE CRETE OEP ASO. cura co .clsPosata-s vicjs carne nulg-eeepaciea clea ale'gce's sin ou pus ric 7 : $31,800 CLUB IMPROVEMENT ACCOUNT PICKIN COL A COOUNBAL Sa LIGCOMDCL URI. ss Nits wend Ud entreanin bas bee hashes ne Ones $5,281 aN SERN ROAM EEN MY, Mi en Yo Cees dc pclivsis ria yin doy oc Niaitd welts welds wipaiie a up's legit enced 956 6,237 Less — Purchase Library Books & Equipment RTISPErPOU LC SUrt MIS -PRCGO IN Le zh 1 ciise.ad Biareihe + od Uvbhves S/CbI-# A)y, WOES Atty Pa bls Ftp 449-4 833 Amount of Account at 31 December 1980. 0... ccc crea e vec tesccensvacnenneevases $5,404 EXCURSION FUND Amount.ofiFund at 31 December 1979 .. cc cecces cence rss tuesserecserrgorertenteeeane $4,323 Add — Interest received on Investment «1... sess enc c cess eee sen de nde cde e es ege een esenenene 861 $5,184 Less — OSES ERMTS Ty Sta educa cilas bcs eccsoay been v ENTE Heese beet a teen +44 27 PEC ISS RATE pina tect a] Wibecrels eM ns ke 3 at UA bing Sin a'v ies one cis CHS AMS PS 556 5 32 Amount of Fund at31 December 1980... .. cei sce cac eee nsec tener eereeererenense $5,152 Field Naturalists Club of Victoria Statement by the Members of the Executive Council In the opinion of the members of the Executive Council of the FIELD NATURALISTS CLUB OF VICTORIA, the accompanying Balance Sheet is drawn up so as to give a true and fair view of the state of affairs of the Club as at 31 December 1980, and the accompanying Statement of Income and Expenditure is drawn up so as to give a true and fair view of the financial results of the Club for the year ended 31 December 1980. Signed in accordance with a resolution of the Executive Council on 31st March 1981. B. Smith President D. Dunn Treasurer Statement by the Principal Accounting Officer 1, Daniel E. McInnes, being the officer in charge of the preparation of the accompanying accounts of the FIELD NATURALISTS CLUB OF VICTORIA for the year ended 31 December 1980 state that, to the best of my knowledge and belief, such accounts give a true and fair view of the matters required by Section 162 of the Companies Act 1961, to be dealt with in the accounts. Signed at Melbourne on the 31st day of March 1981. D. E. MelInnes Auditors’ Report to the Members of Field Naturalists Club of Victoria In our opinion — (a) The attached balance sheet and income and expenditure account are properly drawn up in accordance with the provisions of the Companies Act, 1961 of Victoria as amended and so as to give a true and fair view of:- (i) the state of affairs of the Club at 31 December 1980 and of the results of the Club for the year ended on that date; and (ii) the other matters required by Section 162 of that Act to be dealt with in the accounts. (b) The accounting records and other records, and the registers required by that Act to be kept by the Club have been properly kept in accordance with the provisions of that Act. DANBY BLAND PROVAN & CO, Chartered Accountants Richmond R. M, Bland 31 March 1981 Partner Field Naturalists Club of Victoria Reports of recent activities General Excursion to Flinders Sunday 1 February A full coach and several car-loads ar- rived at Flinders to visit the intertidal zone to study marine life. Led by Presi- dent Brian Smith, we were told about zonation and the effects of wave action and exposure on plant and animal life in the intertidal zone. And after an early lunch we followed the tide out on the rock platform. The variety and profusion of life in rock pools is amazing; every rock turned over (and turned back again before leav- ing) reveals different creatures. There were gastropods like the large black elephant shell Scutus antipodes, the two commercial abalone shells — the Black- lip Haliotis ruber and the Green-lip H. laevigata, numbers of chitons, sea stars, sea urchins, to tube worms and a bewildering variety of encrustung sponges and bryozoa. Specimens were put into buckets, examined and explain- ed, then returned to the sea. Particularly interesting finds were a live Southern Brown Cowrie Cypraea (Notocypraea) comptoni and two specimens and of an unusual pyc- nogonid (sea-spider) with eggs. Dr Smith pointed out some predatoc- prey relationships including the carn- varous gastropod Lepsiella_ vinosa feeding on the encrusting tube-worm Galeolaria. The February excursion for intertidal marine life is becoming an annual event, and we thank Dr Brian Smith for another stimulating, informative and very enjoyable day. General Meeting Monday 9 February The speaker was Dr Carroll, President of the Conservation Council of Victoria. Dr Carroll outlined the Council’s work by reading the minutes of the last meeting showing positive planning and action on major issues. Such topics as Harold Holt Marine Park, pine planta- tions in north-east Victoria, Australian Newsprint Mills policy, Combined Energy Network and World Environ- ment Day were among those dealt with. Questions showed much interest in conservation but accurate information is necessary. Dr Carroll mentioned the heavy work-load of a limited staff, and intimated that the knowledge which ex- ists among FNCV members would great- ly help in the preparation of submis- sions. (Perhaps some FNCV members may not know what the CCV is. It is nota government body but an association of various conservation organisations and individuals which aims to co-ordinate and to act as their mouth piece in presenting a common viewpoint to government public authorities, etc. The CCV examines proposed legislation con- cerning the Victorian environment and has representatives on the Land Conser- vation Council.) Swifts. Flocks of some 200 swifts were observed flying low over the eastern suburbs. Large numbers were also sighted at Inverloch. March/April GROUP MEETINGS All FNCV members are invited to attend any Group meetings, no extra charge. At the National Herbarium, the Domain, South Yarra, at 8.00 p.m. First Tuesday — Mammal Suryey Group Tuesday, 7 April. Planigales. Speaker: Debbie Andrews. Tuesday, 5 May. Marine mammals. Speaker; Martin Schulz. Tuesday, 2 June. Identification of rodents. Third Wednesday — Microscopy Group. Wednesday, 15 April. History of the microscope. Speaker: J. Dawes. Wednesday, 20 May. General illumination for the microscope. Speaker: Dr Hammond. Wednesday, 17 June. Rotifers. Speaker: P. Genery. Second Thursday — Botany Group. Thursday, 9 April. Common seaweeds. Speaker: M. T. Sault. Thursday, 14 May. Lichens. Speaker: Mr Rex Filson. Thursday, 11 June. Philippines fungi. Speaker: Mr M. McBain. At the Conference Room, the Museum, Melbourne, at 8.00 p.m. Good parking — enter from Latrobe St. First Monday — Marine biology and Ento- mology Group. Monday, 4 May. Sea urchins. Speaker: Mr H. Bishop. Monday, I June. Insects: some interesting life histories. Speaker: Mr P. Kelly. GROUP EXCURSIONS All FNCV members are invited to attend Group excursions. Botany Group — last Saturday. Saturday, 25 April. Mornington Peninsula — seaweeds. Saturday, 30 May. Lichens. Mammal Survey Group Friday, 17 — Monday, 20 April. Easter camp. Children State Forest. Saturday, 9 — Sunday, 10 May. Toponga River, Eildon area. Saturday, 6 — Monday, 8 June. Queen’s Birthday weekend. Mt. Worth. Day Group — third Thursday. Thursday, 21 May. Albert Park. Meet at 11.30 a.m. at Main Gate, South Melbourne Cricket Ground. Train to Albert Park Station, or St. Kilda Beach tram (No. 10 or 12 in Collins St) to corner Clarendon St and Albert Rd. Leader: K. Gill (836 8016). Thursday, 18 June. National Art Gallery, St. Kilda Rd. Meet near floral clock, Queen Vic- toria Gardens at 11.30 a.m. (if weather suitable) or OUTSIDE Gallery at 1.30 p.m. (special group rates). Leader: B. Gillespie (578 1879). FIELD NATURALISTS CLUB OF VICTORIA CALENDAR OF EVENTS Wed I. Geology Group: Kimberlite and the origin of Diamonds in N.W. Australia. lan Hawkins Melb. APRIL State College. 5. General Excursion to Organ Pipes National Park. 7 ; Ron 6. Marine Biology & Entomology Group — Pond Life with a movie camera. Mr P. Genery. Tue 7. Mammal Survey Group, Planigales by Debbie Andrews. 4 Botany Group. Common Seaweeds. Mr T. Sault. “tng ss General Meeting. Otway Study Night. Keynote speakers to be arranged. Groups asked to prepare short addresses. Wed 15. Microscopical Group. History of the microscope. Mr J. Dawes. EASTER 17-20. Mammal Survey Group — Chiltern State Forest. Sat 25. Botany Group Excursion. Mornington Peninsula — Seaweeds. FOR FURTHER INFORMATION PLEASE PHONE THE RELEVANT NUMBER FNCV Secretary 859 8091 Geology (Bus.) 697 6596 Gen Excursions 527 2749 Mammal Survey 874 4408 Spec Sty Trips 859 8091 Marine Bio & Ento 211 2427 Botany Groups 557 6045 Micro Group 211 2427 Day Group 578 1879 Field Naturalists Club of Victoria Established 1880 OBJECTS: To stimulate interest in natural history and to preserve and protect Australian fauna and flora. Members include beginners as well as experienced naturalists. Patron: His Excellency the Honorable SIR HENRY WINNEKE, KCMG, KCVO, OBE, KStJ, QC. Key Office-Bearers 1980-1981 President: Dr. BRIAN SMITH, 8 Hunsford Avenue, North Clayton, 3168 (560 8358) Secretary: Miss WENDY CLARK, 27 Rangeview Grove, North Balwyn, 3104 (859 8091) Correspondence to: FNCV, National Herbarium, The Domain, South Yarra, 3141 Treasurer: Mr. D. DUNN, 3 Allfrey Street, East Brighton, 3187 (578 5753) Subscription Secretary: F.N.C.V. C/- National Herbarium, The Domain, South Yarra, 3141 Editor: Mr. R. WALLIS, C/- State College of Victoria—Rusden, Blackburn Road, North Clayton, 3168, 544 8544. Librarian: Mr. P. KELLY, C/- National Herbarium, The Domain, South Yarra, 3141. Assistant Librarian: Miss M. J. LESTER, 4/210 Domain Road, South Yarra, 3141 (26 1967) Excursion Secretary: Miss M. ALLENDER, 19 Hawthorn Avenue, Caulfield, 3161 (527 2749) Book Sales Officer: Mr. D. E. McINNES, 129 Waverley Road, East Malvern, 3145 (211 2427) Group Secretaries Botany: Mr. MICHAEL McBAIN, 19 Foster St, St Kilda, 3182 (534 2293) Day Group: C/- National Herbarium, The Domain, South Yarra, 3141. Geology: Mr. T. SAULT, C/- National Herbarium, The Domain, South Yarra, 3141 Mammal Survey: Mr. RAY GIBSON, 26 McCulloch Street, Nunawading, 3131 (874 4408) Microscopical: Mr. M. H. MEYER, 36 Milroy Street, East Brighton (596 3268) Entomology and Marine Biology: Mr. D. E. McINNES, 129 Waverley Road, East Malvern, 3145 (211 2427) FNCV Kinglake Nature Reserve: McMahons Road, Kinglake. Bookings and keys: Mr. 1. F. MORRISON, 788 Elgar Road, Doncaster (848 1194) MEMBERSHIP Membership of the F.N.C.V. is open to any person interested in natural history. The Victorian Naturalist is distributed free to all members, the club’s reference and lending library is available and other activities are indicated in reports set out in the several preceding pages of this magazine. Subscription rates for 1981 (bce S Ti 9 lft 3 Pa SA Se ee en ee sy ea) eee SUE ins CPST Chee 8 a8 9r.s 23 coh Fis! 9.8 Feil airs ale CR Ap tdci tis a's bhepid lel fil elsipe: clkbtrta Country Members and Retired Persons.....,......,.... Joint Country and Joint Retired .............. cas eel ees £44 CUM uhay A ews Ole ee eae SEW EU boost ic ie tlele sabe cule PIDCTIONION LO WICLOLIAUE SATUTAIISE, ome p24 cos 00 aya be bine sie on ciehien beads vaults Kai Overseas Subscription to Victorian Naturalist... Individual Journals All subscriptions should be made payable to the Field Naturalist Club of Victoria and posted to the Subscription Secretary. @) JENKIN BUXTON PRINTERS PTY. LTD., WEST MELBOURNE lan t IS The Victor Natural FNCV DIARY OF COMING EVENTS GENERAL MEETINGS At the National Herbarium, the Domain, South Yarra. Monday, 15 June, 8.00 p.m. Film night — a film on the Terrania Creek rain forest made by the Native Forests Action Council will be shown. Monday, 13 July, 8.00 p.m. Mr J. Ros Garnet will be presented with his Honorary Membership and will speak on “Reminiscences of the FNCV’’. Monday, 10 August, 8.00 p.m. Life history of squids. Speaker: Dr C. C, Lu. New Members — May/June General Meetings. Ordinary Jane Calder, 146 Waiora Rd, Rosanna. Neale Carr, 129 North Rd, Reservoir, David Clark, 4 St Edmunds Gve, Glen Iris. John Eichler, 3/217 Beach Rd, Black Rock. Alda Heap, 8 Nathan Gve, Caulfield South. Eve Mitchell, 7/146 Rupert St, West Footscray. Harold Revell, Zoology Department, University of Melbourne. Christine Shankley, 50 Glyndon Rd, Camberwell. Joint Mr and Mrs N, Bacon, 22 Rae Ave, Edithvale. Philip and Trisha Maher, 94 Hunter St, Deniliquin. Mr and Mrs W. Rocke, 55 Rowen St, Burwood. Country Trevor Hawkeswood, Botany Department, James Cook University. Gwenda Newman, Health Care Centre, Warburton. D. Wilbraham, 15 Kenwood St, Boolarra. FNCV EXCURSIONS Sunday, 7 June. Zoological Gardens. Meet at the main entrance at 11.00 a.m. Bring a picnic lunch. Sunday, 5 July, Toorourrong Reservoir. A coach will leave Batman Ave at 9.30 a.m. Fare $5.50. Br- ing a picnic lunch, Sunday, 2 August. Coolart. A coach will leave Batman Ave at 9.30 a.m, Fare $6.00. Bring a picnic lunch, Sunday, 9 August. Studley Park. This year the Gardens Club is again organising a boneseed eradication day. We will join this united effort in- stead of having a day of our own and trust as many members as possible will attend. We have removed many 1000's of plants in the past and the improve- ment is quite noticeable, So keep up the good work, Meet at Kanes Bridge at 10.00 a.m. Bring gloves and a picnic lunch. Make a list of native plants seen while working as the Botany Group is updating the old plant list. Preliminary notices: Saturday, 19 — Sunday, 20 September, Alexandra, The VFNCA is holding a springtime get- together hosted by the Alexandra/Yea FNC. Satur- day afternoon excursion to Cathedral State Park. Depart from the Alexandra High School at 1.00 p.m. There will be an evening meeting at the High School at 8.00 p.m. and Sunday excursion to the McKenzie Flora Reserve. Meet at the same place at 9.00 a.m. A coach will be chartered and motel ac- commodation on DDB basis, at a cost of $45.00 per person. Riversdale Caravan Park is next to the school with on-site vans. Members camping or hir- ing vans should make their own arrangements. Friday, 16 October — Friday, 6 November. New Zealand. Please note change in day of departure; the party will now leave on Friday, 16 October. The extra day will be spent at Hicks Bay, and other slight changes have been made to the itinerary. More bookings are desired for this excursion and should be made with the Excursion Secretary ac- companied by a $50.00 deposit. Special study trips: The next special study trip will be in September. The Victorian Naturalist Volume 98, Number 3 May/June, 1981 ISSN 0042-5184 Editor: Robert L. Wallis Assistant Editor: F. Dane Panetta Editorial Committee: H. Cohn, R. Kent, B. Smith Early Introductions of Birds to Victoria by R. Balmford......... 96 A Short History of the Discovery and Naming of Banksias in Bastemn Australia Part lbby-Acl. Salkin c.5 0s oes cad eens coi 106 Mammals of the Wallaby Creek Catchment by B. A. Callanan.... 109 Insect Pollination of Angophora woodsiana F. M. Bail. (Myr- taceae) at Burbank, South-east Queensland by T. J. Hawkeswood 120 Selection of a Neotype for the Southern Short-nosed (Brown) Ban- dicoot, Isoodon obesulus (Shaw & Nodder, 1797) by J. M. Dixon . 130 F.N.C.V. — Reports of recent Club activities...........--.+0-- 138 Cover illustration: Southern Short-nosed (Brown) bandicoot, Jsoodon obesulus (Shaw and Nodder, 1797). Photo: Dr. J. Owen. Early Introductions of Birds to Victoria* t By ROSEMARY BALMFORD, t Two streams of thought can be seen to have led to the introduction of animals and plants from other countries to the young colony of Victoria in the 1850’s and 60’s. The better documented stream joined Victoria, even then, to an international movement for the acclimatisation of animals and plants, formally initiated by the establishment in Paris in 1854 of La Société Impeériale d’Acclimatation (Buckland, 1861). The other stream, with the still waters which run deeper, stemmed from the desire of the homesick settler to recreate in a new and unfamiliar landscape some of the familiar sights and sounds of home, a powerful incentive to in- dividuals to take great trouble to bring about the introduction of birds, and especially of singing birds. Beauty was associated with the familiar, and its familiarity enhanced its beauty. Men and women struggling to establish themselves in a harsh environ- ment are not to be blamed for failing to respond to its beauties as their descen- dants could; it was in 1870 that Adam Lindsay Gordon, who had arrived in this country in 1853 at the age of twenty, wrote of ‘‘songless bright birds’’. Brian Elliott (1976) suggests that the absence of the birds traditionally referred to in literature was resented — the nightingales, thrushes, skylarks and ‘‘usual poetical birds of the European repertoire’ were missing and the local birds did not replace them. A Committee of the Legislative Assembly was appointed in 1857, during * Common names are those used in sources. + This article first appeared in The Australian Bird Watcher in 1978. Permission to reprint it was kindly granted by the Bird Observers Club. + 459 The Boulevard, East Ivanhoe, 3079 Victoria. the first session of the Victorian Parlia- ment, to consider the importation of live stock. After giving due consideration to the means of improving the breed of sheep in the colony, it found itself repor- ting that ‘‘your committee think that the bush solitudes of Victoria should be in- vaded by some of the myriads of feathered fowl which gather in clouds in other, but not fairer, lands, and that the vast nations of indigenous quadrupeds which throng over distant and less civilised scenes, should add their quota to give voice and life, activity and food, to where now, scarcely disturbed but by the cry of the laughing jackass, the almost unbroken repose of ages holds its sway over the lovely inland districts of Australia Felix’’. This appreciation of the beauty of the new country was unusual; and was com- bined with a feeling that it was in- complete without the familiar birds and animals of the old. The Old Bushman, H.W. Wheelwright, a sensitive observer of the native birds and animals, speaks for all in the colony when he says ‘‘ . . . larks have been imported from England and turned out wild. It will be a cheering sound in the ear of that man who has but lately left his English home, the clear shrill note of the Skylark in this land, where no single bird has any one long- continued song. Nowhere are British cagebirds more prized than in Australia, and the simple carol of one of our com- monest home songsters, when heard ina foreign land, cannot fail to raise pleasurable emotions even in the rudest and most untutored mind, for it speaks a language of youth and home familiar to all’’ (Wheelwright, 1861). The generally acknowledged founder and consistent inspirer of the formal ac- Vic. Nat: Vol. 98 climatisation movement in Victoria was Edward Wilson of The Argus newspaper. Both streams can be seen ex- erting their influence through Wilson. In a paper read before the Philosophical Institute of Victoria in July 1857 (Wilson, 1858) he argued for the in- troduction of song birds into Victoria, and suggested that first efforts should be concentrated on the skylark and the nightingale. “It may appear to some”’ he said, ‘‘a trivial thing to be devoting our efforts in such a direction, while so much has to be done for the colony in matters of essen- tial importance. But I confess that I am inclined to attach great consequence to the diffusion of these minor delights, and to estimate very highly their beneficial effects upon a people. There is a peculiar charm about the song of the skylark on a fine spring morning or that of the nightingale during one of its own calm summer nights. . . There may bea great deal doubtless, in the associations by which they are surrounded. But it is the peculiar characteristic of these in- teresting creatures to so surround themselves.”’ The other stream, however, appears when Wilson, on a visit to England in 1860 wrote a letter to The Times draw- ing the attention of the public to the im- portance of acclimatisation, and the need for governments to give financial support to the cause as the Victorian Government had done. It had been sug- gested to him that a great want in England was ‘‘a domestic animal not too large when killed to be consumed by a middle class family and the flesh of which should be meaty rather than poultry like’, and that this need could be supplied by the wombat. This unexpected suggestion shows the nature of the international acclimatisa- tion movement; concerned to disseminate animals and plants throughout the world, and to establish them in countries other than those in which they were naturally found, but May/June where it was felt they had a useful part to play. Wilson was present at the first meeting, held in London in 1860, of the Society for the Acclimatisation of Animals (Buckland, 1861). When he returned to Victoria the Acclimatisation Society of Victoria (after 1872 the Zoological and Acclimatisation Society) was established at a meeting held on February 25, 1861 and presided over by the Governor, Sir Henry Barkly. Its ob- jects were almost identical with those of the London Society, the only changes being necessary alterations of place. So the Victorian Society was established for:- *‘The introduction, acclimatisation and domestication of all innoxious animals, birds, fishes, insects and vegetables, whether useful or ornamen- tal; the spread of indigenous animals etc. from parts of the colonies where they are already known to other localities where they are known; the pro- curing, whether by purchase, gifts or ex- change of animals etc. from Great Bri- tain, the British colonies, and foreign countries; the transmission of animals etc. from the colony to England and foreign parts, in exchange for others sent thence to the Society. . .”’ (and so on). Despite Wilson’s enthusiasm for song birds, the minutes show an emphasis on the useful; in 1862, for example, on receipt of a letter from a Mr Duffield of- fering to import birds, the reply stressed that ‘‘useful and edible birds would be preferred to those of merely ornamental character’’. To mark the first year of the Society’s operations, a lecture was given by Pro- fessor McCoy, Professor of Natural Science in the University of Melbourne, at the Annual Meeting in November 1862. He led the imaginations of his hearers to dwell upon ‘‘the great task which has been reserved for us — the stocking of our new country with all the more important, useful and ornamental 97 kinds of animals, whether quadrupeds, birds or fishes, which are to be found in other parts of the world in similar climates, but of which the vast continent of Australia has been left by nature most singularly and exceptionally destitute’’. The international character of the ac- climatisation movement is illustrated by a list of ‘‘enquiries’’ (which would today be called a questionnaire) put to the Society by the Governor in 1864 ‘‘at the instance of the Secretary of State for the Colonies’’. It is clear that the enquiries had been sent to all the British colonies and dependencies on the initiative of the Acclimatisation Society of Great Bri- tain. The essential enquiries for present purposes were: ‘‘Is there any bird, in- digenous or introduced to the country in which you reside which merits attention with a view to its acclimatisation in Great Britain or any of its dependen- cies?’’ and: ‘‘Do you know any bird ex- isting elsewhere the introduction of which to the country in which you reside would be likely to be beneficial?” The birds recommended by the Vic- torian Society, in answer to the first question, as appropriate for acclimatisa- tion elsewhere, were the Emu, the Native Turkey or Bustard, the Wonga- Wonga Pigeon, the Mallee Hen, ‘‘quail of several species’’, the ‘‘so-called Magpies’’, Laughing Jackass, Black Swan, Cape Barren Goose and “‘other geese and ducks for instance Anseranas leucogaster, Anas superciliosa, Bernicla jubata, Casarca tadornoides, Malacorynchus membranaceus’’, The second of these mentioned, “‘breeds now readily in company with the European Wild Duck, which it meets in the wild state, as introduced by the Acclimatisa- tion Society of Victoria’’. The society’s pride in the achievement in _ inter- breeding seems strange today; Frith (1967), for this very reason, recom- mends that Mallard be shot on sight. Mallard and Mallard hybrids are classified as ‘‘noxious wildlife’’ and un- protected under the Victorian Wildlife Act 1975. With the aid of a substantial grant from the Victorian Parliament, as well as subscriptions and donations, the Society established at Royal Park what is now the Melbourne Zoo. Initially the establishment was intended as a holding place for birds and animals acquired by the Society in order that they might be put in good condition and where necessary their numbers increased by breeding with a view to liberation for ac- climatisation. Only in later years did Royal Park acquire its character as a general zoological gardens for visiting by the public, with exhibits not intended for ultimate release. The Appendix gives details of birds which had been liberated by the Society in the first twelve years of its existence, taken from the Annual Report for 1873. It should be remembered that con- siderable efforts were also being devoted to other species, notably alpaca and cashmere goats, camels and salmon, and thought was being given to other desirable imports such as silkworms, glow worms, Secretary Birds (which were reputed to eat snakes) crabs, lobsters and oysters. In the list of birds the two approaches are apparent again: the song birds and swans for delight; the game birds for sport and good eating. Had all the introductions succeeded, the character of the avifauna of Victoria would be markedly different today. Wheeler (1967) lists the following in- troduced species as at that date established in Victoria: Feral Pigeon, Spotted Turtle-Dove, Mallard, Blackbird, Song Thrush, Red-whiskered Bulbul, Skylark, House Sparrow, Tree Sparrow, Goldfinch, Greenfinch, Starl- ing and Indian Mynah. The Ring-necked Pheasant, Spice Finch and Mute Swan have subsequently been added to this list (Wheeler, 1977), but these can be presumed to derive from more recent in- troductions. Thus it can be seen that the efforts of the Society largely failed. Vic. Nat. Vol. $6 Difficulties there were in plenty. The game birds were sent to the properties of interested members for breeding up — to Mr Austin of Barwon Park, famous in Australian history for the acclimatisa- tion of the rabbit, to Edward Henty of Portland and to others. But it was hard to protect them from the uncontrolled depredations of shooters: in May 1862, Mr McHaffie of Phillip Island com- plained of the visits of trespassers with dogs and guns, and notices were to be posted on Phillip Island reading ‘‘All persons are hereby cautioned not to shoot or disturb the birds” (note: not ‘the introduced birds’’) on this Island, they being preserved for the Ac- climatisation Society of Victoria.”’ Native hawks wrought havoc among the song birds, and the Society was anx- ious for their destruction; the purchase of a gun and ammunition for this pur- pose, was authorised in June 1862; but Wilson is recorded in the minutes of September of the same year as writing that ‘‘as those vermin did not exter- minate the native birds, there was no reason to suppose they would the im- ported ones when once they were established’’. There were frequent complaints of the activities of small boys with shanghais. In July 1862 the Society sent a circular to all Victorian municipal councils ad- vising them of the coming into operation of the Act for the Preservation of Native Game and asking them to bring in “‘a bylaw for the protection of all (sic) native birds (excepting hawks) within the bounds of the municipality’’ (the protection of the Act being given only to certain listed species classified as ‘game’) and ‘‘giving power to the Police in all cases to prevent the use of the catapult (or shanghai) by the means of which instrument not only are the native birds rapidly disappearing from the vicinity of our towns but the English birds imported at so much care and ex- pense are frequently destroyed. Were such a bylaw vigorously enforced for a May/June few months this fast growing nuisance would be abated and the birds instead of becoming scarcer would quickly increase and multiply around us.”’ The interest of the Society in native birds was in fact manifested chiefly by the collection of live specimens for ex- change with kindred bodies overseas in return for species it was hoped to ac- climatise in Australia. The records show a flourishing active society; enjoying the support of many members; consistently under Vice-regal patronage; encouraging the formation of similar bodies in the other colonies; triumphantly recording in its annual reports the establishment in the wild of still more species; and ever warmly con- scious of the value of the task it had undertaken. Space does not permit a full history of the Society and of its gradual change to a body conducting a zoological gardens instead of a programme of acclimatisa- tion. But the material exists for such a study, and an outline has recently been published (Jenkins, 1977). What is harder, perhaps impossible, to discover, is the extent of private introduction of birds; to which I now turn. Some clues appear from the records of the Society. The Council minutes from time to time record exotic birds as presented to or bought by the Society; these are to be presumed to have been privately imported; they had clearly not been imported by the Society. In September 1862 letters were sent to people in different parts of the colony suggesting the formation of local bran- ches of the Society to assist in the work of acclimatisation. At the Council meeting held on September 30, 1862, replies were produced from Echuca, Portland, Creswick, Heyfield, Maryborough, Lake Hindmarsh, Castlemaine, Warrnambool, Beechworth and Walmer. “Nearly every gentleman asks for English song birds’’ remarked the Coun- cil in its minutes ‘‘and these frequently 99 arrive in ships from England”’ (italics added) ‘‘and are sold into captivity, whereas if they were purchased’’ (by local branches) ‘‘and set free they would speedily become plentiful throughout the colony’’. Again, these birds were private importations. There was sufficient interest in the subject for A.P. Bartlett, Superinten- dent of the Zoological Society’s Gardens at Regent’s Park, London, to publish in the J/bis of 1862 several pages of “Remarks on the Mode of Preparing and Keeping live Thrushes and other Birds intended for Shipment to Australia’’. But introductions were well under way before the formation of the Ac- climatisation Society. In March 1853 The Argus reported that four white swans had arrived in Melbourne on the “Medway”’ and been presented to the Botanical Gardens. The files of that newspaper for 1854 and later years tell the story of a ship- ment of songbirds brought from England by one Robert Morrice ‘‘a set- tler of many years standing’. A number of birds died on the voyage, but seven Skylarks survived to be liberated on the Barrabool Hills, near Geelong. They were reported singing months later by a traveller from the diggings, sixty miles away near Kyneton. The anonymous contributor to The Argus on October 26, 1854 (most likely Edward Wilson, at that time editor) wrote that R.H. Horne (the poet, who had arrived in Melbourne in 1852) had suggested that Australian birds did not lack the ability to sing, but that they needed teaching. Wilson, if it be he, was prepared to agree that with the introduction of song birds ‘‘the powers of our indigenous songsters might be improved. They have voices, but have never been taught to use them’’. Skylarks, according to The Argus, were recorded in Flemington Road in October 1855, near Geelong in October 1857, near Kilmore in 100 December 1857 and on the Barrabool Hills in November 1858. In January 1856, a dealer imported for sale 800 canary birds, bullfinches, larks and other singing birds. In April the same year one Brender, who had brought to Sydney a large number of birds including thrushes, linnets, skylarks, chaffinches and starlings, was proposing to send some of them to Melbourne for sale. In January 1857 The Argus followed these two reports by recording the arrival of ‘ta German gentleman with a large number of canaries, thrushes, blackbirds, robins, goldfinches, linnets, larks and starlings’’ and five nightingales; and called for donations to enable the nightingales to be purchased for liberation. Java spar- rows (presumably, from the context, free-flying) were recorded in the Botanical Gardens in November and December 1856 (The Argus July 14, 1857). And The Argus continued to chroni- cle the arrival of birds. Six dozen blackbirds and thrushes were shipped to Victoria on the ‘Severn’? in August 1857. ‘‘Several pairs of sky and wood larks, goldfinches and linnets’’ arrived in November of that year in the ““Sydenham’’. A dealer called Neymaler landed his third shipment of birds in Victoria in January 1858 — nightingales, canaries, larks, blackbirds, thrushes, starlings and gold and silver pheasants. A Mr Rushall in October 1858 brought in the ‘‘Norfolk’’ seven partridges, ‘‘several pheasants of the silver, pied, white and common kinds’’ and blackbirds, thrushes, linnets, goldfinches and larks. The writer in The Argus of October 21 stated ‘‘pheasants are already breeding in the colony’’. In December Mr Neymaler’s fourth ship- ment arrived — nightingales, canaries, larks, thrushes, blackbirds and several golden pheasants. The ‘‘Goddess’’ landed 11 pheasants in February 1859, and in March, 28 pheasants, two blackbirds and a thrush Vic, Nat. Vol. 98 arrived at Geelong, consigned to Mr Austin. The Times of London, quoting The Australian and New Zealand Gazette, records on October 18, 1859 the arrival in Melbourne of four dozen thrushes, consigned by Wilson; and on August 10, 1860, this time quoting The Argus, tells of the arrival in Melbourne by the “Norfolk’’ of three larks, nine thrushes and thirty-seven blackbirds, all sent by Wilson. On December 27, in the same year, again citing The Argus, it states that many English birds were breeding in the aviaries in the Melbourne Botantic Gardens, and the thrushes were breeding also in the open air; the starling and blackbirds which were brought out by the ‘Lincolnshire’ and the ‘‘Essex’’ were recovering from the voyage; and ‘*a number of the pheasants, blackbirds, thrushes and larks received from England have been set free in the islands of Western Port and no doubt they are fairly established there’. On April 6, 1860 “‘The Times’’ own correspondent in Melbourne wrote: “Honour to Edward Wilson! The charming singing birds which he despat- ched by the ‘Great Britain’ have arrived safely with few casualties. Out of the forty-two thrushes and fifty-five larks shipped, no less than thirty-seven of the former and forty-three of the latter have been successfully established in the Botanical Gardens. Of twelve pairs of pheasants, only seven cocks and four hens remain alive’’. Whatever the intended fate of the birds brought out by dealers and no doubt sold as cage birds, anything im- ported by Wilson was clearly destined for liberation with a view to acclimatisa- tion. The Old Bushman, who returned to England in 1859 (or perhaps in 1856: (Chisolm, 1976) ) and in any event before the establishment of the Ac- climatisation Society, records that skylarks had been liberated; he once saw May/June a white swan flying in the wild and knew of a tame pair kept in the Cremorne Gardens, Melbourne. Pheasants he knew of as having been imported, but so far, he believed, confined to aviaries; although he knew of a cock-pheasant having been shot a few years before ina patch of tea-tree a few miles from Melbourne, no doubt having been deliberately released (Wheelwright, 1861). Thus, independently of the activities of the Society, birds were being in- troduced. Some, no doubt, escaped, and many were being released in the wild with a view to acclimatisation. This be- ing so, various confident statements in the literature as to the date of first in- troduction of sundry species should be read with caution. It is unlikely that the first date of introduction of any species will ever be known; and many unrecord- ed introductions must have taken place. Attempts have been made to ascertain the precise origin of introduced species (Sage, 1956 & 1957; Le Souef, 1958 & 1964; Keve, 1976) in order to determine what subspecies produced the Australian stock. Le Souef worked from the minutes of the Acclimatisation Society. Sage relies on Ryan (1906) who gives particulars of date and place of first liberations and number of individuals liberated for twenty-three species; and similar details for a number of later liberations of the same species. Colonel Ryan was closely involved with the ac- tivities of the Acclimatisation Society, having been President in 1878 and 1899; he was to be President again in 1912-16. Thus it might have been assumed that he is speaking of liberations by the Society and obtained his information, which is detailed and specific, from the Society’s records. However, he mentions the Society only once, as having liberated some pheasants, and it is not possible to infer from the article that the other libera- tions to which he refers were in fact car- 101 ried out by the Society, or by any other specific person or organisation. No names are given. Further, his information is inconsis- tent with the published records of the Society. For example, he gives 1863 as the date of the first liberation of Starl- ings, Thrushes, Californian Quail and Skylarks, and 1864 for the Blackbird, all of which are listed by McCoy in his Jec- ture as having been liberated by the Society before June 1862. The Report of the Provisional Committee to the members of the Society on August 7, 1862 states that ‘‘The Thrush, Skylark, Blackbird and probably the Starling, may now be considered permanently established amongst us, the three former being heard in all directions’’. The Skylark was, as shown above, present in 1854; whether these in- dividuals survived and produced descen- dants cannot now be known; but 1863, the date of first introduction as given by Ryan, is clearly incorrect in this case; and his dates are likely to be incorrect in other cases. Wheeler (1967) also gives dates of first liberation which appear to be derived from the published reports of the Society. It is easy to envisage the settler, retur- ning to England on a visit, acquiring a cage of birds and nursing them through the long voyage back to Australia to relieve what was to him a dreary wilderness; or buying the birds brought out to Melbourne by dealers; and liberating them optimistically in the hope that they would establish themselves. Today we regret his efforts; but we should not judge him too har- shly. It is only in the last ten to fiteen years that most of us have considered native plants to be suitable for our gardens; the botanical importations of our homesick ancestors have seemed to us until lately the only plants worthy of domestication. Our attitude to the introduced birds has for a long time been different. Part- ly this change arose from an early revul- 102 sion against the fruit eating propensities of some of the exotic species. Com- plaints against Sparrows and Mynahs on this ground were voiced at the sixth an- nual meeting of the Society in 1868. And at a Council Meeting of the Society as early as June 3, 1862 ‘‘the Starling was specially objected to, as being reported to destroy the eggs of other birds’’. Private introductions and liberations continued, however, John Ritchie of Blythevale, near Streatham, some 160 km west of Melbourne, had Turtle Doves in his garden in November 1869, and a large cage of canaries, ‘‘but all the blackbirds and thrushes died which he turned out some time ago’’. (Lewis, 1869). Dr George Nicholson is reported as liberating Thrushes, Blackbirds and Skylarks near Ballarat in 1876, and as having imported (and presumably liberated) other birds in 1867 and 1870 or 1871. All his birds came from Ireland, mostly from County Cork (Bar- rett, 1926). Changing attitudes in later years are demonstrated by the treatment of the in- troduced birds in the standard bird books and other lists. Keartland con- tributing to The Handbook of Melbourne for the use of members of the Australasian Association for the Ad- vancement of Science, which met at the University of Melbourne in 1900, pro- duced an otherwise comprehensive list entitled ‘Birds of the Melbourne District’’ which made no mention at all of any introduced species. Robert Hall (1899) and (1900), listing Australian birds and insectivorous birds of Victoria respectively likewise ignored them. In 1907 he at least dealt with the introduced birds, although in a separate chapter, as did Lucas and Le Souef (1911). Leach in his first edition (1911) was ahead of his time in realistically including them in systematic order. The first edition of Cayley (1931) included no illustrations of introduced birds, although some were described, and in the 1958 edition a separate plate depicting introduced Vic. Nat. Vol, 98 species was added. Mack (1935) listed them separately at the end of his account of the birds of Victoria. Whittell (1954) in his entry on Le Souef (1890), felt constrained to add “includes information on introduced birds’’ almost apologetically, as though such a reference was hardly appropriate in a work entitled ‘‘The Literature of Australian Birds.’’ Wheeler (1967) lists the introduced species in systematic order as they come, recognising them as an integral part of the avifauna, as do Slater (1970 and 1974), the Victorian Year Book for 1966 (Anon, 1966), and Macdonald (1973). The 1926 Checklist (RAOU, 1926) ig- nored the introduced species; the 1975 Checklist (Condon, 1975) and Interim List (Shodde, 1975) included them. In 1969 the Gould League produced what must be the first Australian bird book with a starling on the cover; Birds of Victoria: Urban Areas; accepting reality and recognising the place of the exotics in the region with which the book was concerned. Over 70% of the people of Victoria live in Melbourne (Anon, 1977) and for them, the com- mon, obvious birds are the introduced birds. The introductions of exotic birds to Victoria and the other Australian col- onies (Jenkins, 1977) formed part, but only part, of the activities of the official, organised acclimatisation movement and of the private individuals desirous of recreating in a strange land the familiar sights and sounds of home. I am indebted to Allan McEvey for pointing out that both groups were assuming man’s dominion over the animal kingdom; it was for man to ar- range the creatures wherever in the world he wished to do so. The eigh- teenth century neo-classical love of order, seen also in the landscape gardens of the period, imposed itself upon the natural world; and the nineteenth cen- tury acclimatisers moved in that tradi- tion, exemplified by McCoy’s perora- May/June tion quoted above. Among the Victorian colonists it seems that there was as yet no place for the romantics, prepared to accept, to marvel at, and later to study, nature in its primeval state. There is not space here to examine to- day’s ambivalent attitudes to the established introduced species. Let the last word be with C. J. Den- nis’ Starling, chattering in 1935: “Men rave and count us enemies And many strive to work us ill. Yet pray remember, if you please, That we are here not at our will. Some homesick exile brought us hence To be a solace for his grief So, spite of all our grave offence, Can’t you forgive a cheery thief?”’ Acknowledgements For assistance towards the prepara- tion of this article | am indebted to Ellen McCulloch, Tess Kloot, Helen Aston and Peter Balmford; to the latter also for access to his useful working library of Victorian history. For arousing my interest in the history of ornithology and of Victorian ornithology in particular I owe a debt to Allan McEvey, who kindly read and commented on a draft of this paper. To all of them my thanks. APPENDIX BIRDS LIBERATED IN VICTORIA BY THE ACCLIMATISATION SOCIETY OF VICTORIA TO 1873 At the Botanical Gardens 18 Canaries 18 Blackbirds 14 Thrushes 6 California quail 80 English wild ducks 35 Java sparrows 4 English robins 8 Turtle doves 50 Mainas At Phillip Island 4 Chinese partridges 70 Chinese quail 23 Tasmanian quail 6 Starlings 10 Algerine sand grouse 6 Wild ducks 103 5 Pheasants 6 Skylarks 6 California quail 4 Thrushes 4 Blackbirds 1 Pair white swans 5 Cape pheasants 8 English pheasants 4 Indian pheasants 8 Ceylon partridges 5 Indian partridges At Sandstone and Churchill Islands 4 Pheasants 4 Skylarks 4 Thrushes At Yarra Bend 6 Thrushes 4 Skylarks At the Royal Park 2 Thrushes 20 Greenfinches 15 Yellowhammers 200 Java sparrows 6 Blackbirds 20 Siskin finches 6 Powi birds 3 Partridges 6 Pheasants 10 English robins 20 Mainas 6 Starlings 60 English sparrows 40 Chaffinches At St. Kilda 20 Chinese sparrows At Ballarat 5 English sparrows 20 Java sparrows At Cape Liptrap 10 Pigeons 4 Ceylon peafowls 4 Guinea fowl At Plenty Ranges 10 Pheasants 4 Jungle fowls 7 Guinea fowls Liberated in the Bush in 1870 30 Pheasants 25 Skylarks A number of doves 20 Guinea fowl 10 Pea fowl Liberated in the Bush in 1871 150 Guinea fowl 15 Pheasants 104 Liberated in the Bush in 1872 50 Pheasants A number of Californian quail 17 English robins 20 Guinea fowl In addition to the above, 54 pheasants had been sold and distributed to members of the Society. REFERENCES: Anon, 1966. Victorian Year Book 1966, Com- monwealth Bureau of Census and Statistics, Melbourne. Anon. 1977. Victorian Year Book 1977. Australian Bureau of Statistics, Melbourne. The Argus, 1853. 15 March, The Argus, 1854, 18 February, 19 August, 26 and 28 October, 8 and 14 November. The Argus, 1855. 9 July, 7 September, 22 October. The Argus, 1856. 23 January, 26 February, 2 April. The Argus, 1857. 1 January, 14 July, 23 and 31 Oc- tober, 3 November, 7 December. The Argus, 1858. 15 January, 21 October, 9 November, 20 December. The Argus, 1859. 21 January, 17 February, 2 and 30 March. (Barrett, Charles), B.C., 1926. Introduction of British Birds Victorian Naturalist 43, 190. Bartlett, A. D., 1862. Remarks on the mode of preparing and keeping alive Thrushes and other Birds intended for shipment to Australia. [bis 4 (13). January, 13-18. Bennett, George, 1862. Acclimatisation: Its Emi- nent Adaptation to Australia. Republished by the Acclimatisation Society of Victoria, Melbourne. Blainey, Ann, 1968. The Farthing Poet: A Biography of Richard Hengist Horne, 1802-84. London, Longmans. Buckland, F., 1861. The Acclimatisation of Animals. A paper read before the Society of Arts, London. Republished by the Acclimatisation Society of Victoria, Melbourne. (Bound in Vic- torian Pamphlets no, 32, La Trobe Library, State Library of Victoria.) Cayley, Neville W., 1958. What Bird Is That? Se- cond Edition, revised and enlarged by A.H. Chisholm, K.A. Hindwood, and A.R. McGill, Sydney, Angus & Robertson. Chisholm, A.H., 1950. Birds introduced into Australia. Emu 50: 97, Chisholm, A.H., 1976. ‘‘Wheelwright, Horace William” in Australian Dictionary of Biography Vol. 6. ed. Nairn, Melbourne. M.U.P. Condon, H.T., 1975. Checklist of the Birds of Australia Part 1 Non-Passerines. Melbourne, RAOU. Dennis, C.J., 1935. The Singing Garden. Sydney. Angus & Robertson. Elliot, Brian, 1976, ‘‘Emblematic vision: or landscape in a concave mirror’, in Man and Landscape in Australia ed. Seddon and Davis, Canberra. Australian Government Publishing Service. Vic. Nat. Vol. 98 Fendley, G.C., 1974. ‘‘McCoy, Sir Frederick’? in Australian Dictionary of Biography Vol. § ed. Pike, Melbourne. M.U.P. Frith, H.J., 1967. Waterfowl! in Australia, Sydney. Angus & Robertson. Gordon, Adam Lindsary, 1870. Bush Ballads and Galloping Rhymes. Melbourne. Clarson, Massina. Gould League, Victoria, 1969. Birds of Victoria, Urban Areas. Melbourne. Victoria Gould League. Hall, Robert, 1899. A Key to the Birds of Australia. Melbourne, Walker, McKay & Co. Hall, Robert, 1900, The Insectivorous Birds of Victoria. Melbourne. Author. Hall, Robert, 1907. The Useful Birds of Southern Australia. Melbourne. T.C. Lothian. Jenkins, C.F.H., 1977. The Noah's Ark Syndrome. Perth Zoological Gardens Board. Keartland, G.A., 1900. Birds of the Melbourne District. In Handbook of Melbourne, Australa- sian Association for the Advancement of Science, Melbourne. Keve, A., 1976. Some remarks on the taxonomic position of the Tree Sparrow introduced into Australia. Emu 76: 152. Kiddle, Margaret, 1961. Men of Yesterday (pp. 318- 320). Melbourne, M.U.P. Kramer, Leonie, 1972. ‘‘Gordon, Adam Lindsay”’ in Australian Dictionary of Biography Vol. 4 ed. Pike, Melbourne. M,U.P. Leach, J.A., 1911. An Australian Bird Book. Melbourne. Whitcombe and Tombs. Le Souef, J. Cecil, 1958. The Introduction of Spar- rows into Victoria. Emu 58: 264. Le Souef, J. C., 1964. Acclimatisation in Victoria. Victorian Historical Magazine 36: 8-29. Le Souef, W. H. D., 1890. ‘‘Acclimatisation in Vic- toria’. In Report of the second meeting of the Australasian Association for the Advancement of Science held at Melbourne Victoria in January 1890. 476-482. Lewis, William, 1869, ‘Letters to George Russell’’ in VIl Clyde Company Papers ed. P.L. Brown, 1971, London. O.U.P. (pp. 353-4). Lucas, A.H.S. & Le Souef, W. H. Dudley, 1911. The Birds of Australia. Melbourne. Whitcombe and Tombs. Macdonald, J.D., 1973. Birds of Australia, Sydney. A.H. & A.W. Reed. Mack, George, 1935. ‘‘The Birds of Victoria’’ in Victorian Year Book 1933-4. ed. Gawler, Melbourne. Government Printer. McCoy, F.S., 1862. Acclimatisation, its nature and applicability to Victoria. Anniversary address delivered to the first annual meeting of the Ac- climatisation Society of Victoria, Melbourne. McEvey, A.R., 1975. Bibliography to accompany Victorian Ornithology — A Chronology. Melbourne. National Museum of Victoria. Melbourne Zoo (n.d.) The Melbourne Zoological May/June Gardens, Past History and Present Trends. Special edition of Melbourne Zoo Newsletter, for 110th birthday. RAOU, 1926, The Official Checklist Birds of Australia, Melbourne. RAOU., Ryan, C.S., 1906. On European and other Birds Liberated in Victoria, Emu 5; 110. Sage, Bryan, L.., 1956. Remarks on the Racial Status, History and Distribution of the Tree Spar- row introduced into Australia, Emu 56: 137. Sage, B.L., 1957, Remarks on the Taxonomy, History and Distribution of the House Sparrow introduced into Australia. Bmu 57; 349. Schodde, R., 1975. Interim List of Australian Songbirds. Passerines. Melbourne, RAOU, Serle, Geoffrey, 1976. ‘‘Wilson, Edward’ in Australian Dictionary of Biography, Vol. 6, ed. Nairn, Melbourne. M,U.P. Slater, Peter, 1970 & 1974. A Field Guide to Australian Birds. Adelaide. Rigby. Smith, James (ed.), 1903. The Cyclopedia of Victoria Vol. 1, pp. 283-286. Melbourne. The Cyclopedia Company. Tarr, H.E., 1950. The Distribution of Foreign Birds in Australia. Emu 49: 189. Tarr, H.E,, 1963. Early Note on Introduced Birds. Bird Observer. May 1963, 2. The Times, 1859. 18 October, London. The Times, 1860. 6 April, 10 August, 22 September, 27 December, London. Victoria, Legislative Assembly 1857 Report from Select Committee on Live Stock Importation. Ordered to be Printed March 10, 1857. Wheeler, W.R., 1967. A Handlist of the Birds of Victoria, Melbourne. Victorian Ornithological Research Group. Wheeler, W.R., 1977. Additional Species added to “4 Handlist of the Birds of Victoria, 1967’’. (manuscript). (Wheelwright, H.W.) An Old Busman 1861. Bush Wanderings of a Naturalist. London. Routledge, Warne and Routledge. Reprinted, Oxford University Press, Melbourne, 1979. Whittell, H.M., 1954. The Literature of Australian Birds. Perth. Paterson Brokensha, Wilson, Edward, 1858. On the Introduction of the British Song Bird. Transactions of the Philosophical Institute of Victoria 2, 77-88. Wilson, Edward, 1860. Letter to the Times, 22 September, 1860. (Zoological and) Acclimatisation Society of Vic- toria. 1861-1951 Papers (mostly minutes and reports) Vols, I-13 (Xerox copies in library of Monash University, Clayton, Victoria). 1861-7. Annual reports, Answers to enquiries, report of dinner, rules and objects, etc. (Bound in Victorian pamphlets, nos. 32, 36, 49, 60 and 129 in La Trobe Library, State Library of Victoria. 1872-8. Proceedings and reports of Annual Meetings, Vols. 1-5. of the 105 A Short History of the Discovery and Naming of Banksias in Eastern Australia Part II Sir James Edward Smith By A.I. SALKIN* The ‘‘First Fleet’? of convicts and soldiers landed at Botany Bay on January 18th, 1788. By a strange coin- cidence the ships of a French ‘‘scien- tific’? voyage of exploration anchored in the bay eight days later (Scott, 1916). This was the ill-fated expedition under the command of La Perouse which was to meet a tragic end at Vanikoro (Stafleu, 1966) in the Santa Cruz group of islands, in the Solomons. The motives for the settlement in New South Wales are the subject of much debate but one thing that is quite clear is that it provided an opportunity for scientific material to be sent from Australia to England. Thomas Keneally (1967) in his novel ‘‘Bring Larks and Heroes’’ gives something of the flavour of this period and how the convicts were used in this trade in exotics either as col- lectors or illustrators. There was of- ficially a monopoly on all material of scientific interest and this was under the direct control of Sir Joseph Banks. The botanical material was intended for the Royal Botanic Gardens at Kew and only a few rarities were allowed to be distributed to the King’s favourites through the offices of Banks. Banks however did not employ a collector in New South Wales until 1791; he was David Burton, a superintendent of con- victs who applied to Banks directly for the position. Banks’ reply to Burton gives a clear picture of the importance attached to the monopoly. ‘*T mean by offering you 20 pounds a year to engage you (to) collect for me seeds of Plants, Living Plants when you can and specimens of Plants and that you engage not to supply any other per- son directly or indirectly with any vegetable production the other two 106 kingdoms of nature are open to you.” (Banks, 1791 in Gilbert, 1962) In the meanwhile, Banks was supplied by Governor Philip with seeds and plants. The monopoly that Banks sought to establish merely made a clandestine trade in botanical and zoological curiosities more probable, and also more profitable. Not only were naval and military officers engaged in this ‘trade’? but so also was anybody else who had or claimed knowledge pertain- ing to these matters. The trade in botanical curiosities was much older than the settlement of Australia. New plants suitable for both agriculture and horticulture were as im- portant, if not more so then, as they are now. Botanical collectors risked their lives in the jungles of South America and the mountains of India and China collecting for this trade. The King’s garden at Kew merely gave added status to this penchant for acquiring rarities. Magazines were published that describ- ed new species as they were brought into cultivation. The best of these were in many ways scientific works, their titles give some idea of the market to which the information was intended. The Cur- tis Botanical Magazine, one of the most influential of these publications, con- tinues to be published under a bequest from George Bentham and presumably fulfils a similar service to the original ones which were: “The Botanical Magazine: or Flower Garden Displayed; in which the most or- namental Foreign Plants, cultivated in the Open Ground, the Green House, * Science Department, Brentwood High School, Heath St. Glen Waverley, 3150. Vic. Nat. Vol. 98 and the stove are accurately represented in their Natural Colors . . . A work in- tended for the use of such Ladies, Gentlemen, and Gardeners as wish to become scientifically acquainted with the plants they cultivate.’’ The first volume of the ‘‘Curtis Botanical Magazine’’ was published in 1787. A very early volume, Volume 6 Plate 738 deals with ‘‘Banksia ericaefolia’’ (sic). After a latin generic and species description together with synonyms and illustrations this descrip- tion follows — “‘The Banksia is a genus so named in honor of its first discoverer, the Presi- dent of the Royal Society, in a voyage round the world with Captain Cook, is very nearly allied to Protea, and like that appears to contain a great number of species of various forms and size. Our present plant forms a handsome shrub, thrives freely, and has flowered in several collections; our drawing was taken from that of E.J.A. Woodford, Esq. at Vauxhall in April 1802. The beauty of the flower consists very much in the length of the style; which from the stigma being long retained within the anthers, is fancifully bent into a loop: when the efflorescence is com- plete, the petals expand and let the stigma at liberty. The flower is con- sidered by some as monopetalous, but the petals, in Banksia ericaefolia (sic) at least, adhere so slightly at the base only, that they can hardly be kept from separating when removed from the receptacle. The germen (ovary) in this species is surrounded by brown hairs very like many of the Protea. We could not discover any other calyx than the squama (bracts) of the Amentum (spike), in no respect like that described by Gaertner. A native of New-Holland. By no means tender, and may be kept in a greenhouse with Proteas and other Cape shrubs. Propagated by seeds and cuttings.’’ “The Botanist’s Repository’? by Henry Andrews was not a magazine, but May/June was published in parts between 1797 to 1815. The full title describes clearly the aims which were in the best traditions of natural history — “The Botanist’s Repository for New and Rare Plants containing coloured figures of such plants, as have not ap- peared in any similar publications with all their essential characters botanically arranged after the sexual system of the celebrated Linnaeus in English and Latin. To each description is added a short history of the plant as to its time of flowering, culture, native place of growth, when introduced and by whom.”’ In many cases: *“‘The Botanist’s Repository’’ achieved what it set out to do and a number of plant species were first described in the publication. Bauera rubioides is one of a number of descriptions that were published in this way. The most influential of these botanical publications and one that con- centrated entirely on the flora of Australia was ‘“‘A Specimen of the Botany of New Holland’’ (Smith, 1793). The author Sir James Edward Smith, founder of the Linnean Society, acted as the patron of Mr. John White who ac- companied Captain Phillip as Surgeon- General to the colony of New South Wales. White’s medical training made him a suitable observer and collector because medicine was largely concerned with obtaining drugs from plants, botany being part of medical training. Of the plants that White sent back, 27 were described as new species in the ‘‘Specimen”’, a further 37 were describ- ed in ‘‘Exotic Botany’’ (Smith, 1804), of these 64 new plants only one new Banksia species was described. It is im- portant to realise that so far none of the Banksia spp. at that time discovered had been described by the person who col- lected it and none of the material was re- tained in Australia. This poses many problems for anybody doing research in Australia and the reverse is true of 107 researchers in England. Smith never saw plants growing in the field in Australia. He no doubt saw plants growing in greenhouses but because of phenotypic plasticity this is a poor substitute for field work. Smith appears to have been aware of these problems because as well as the pressed specimens White sent him there were also sketches; these were pro- bably done by the convict artist Thomas Watling (Rientis, 1963). The seventh Banksia spp. at that time discovered had to be described was B. spinulosa. The pressed specimen is still in the Linnean Society’s herbarium and is in a remarkably good state of preservation; it consists of 3 sprays with 3 flowers in various stages of development. The “worked up’’ coloured illustration is by James Sowerby who was also the publisher. Whilst the illustration is a lit- tle mechanical in its treatment, there is no doubt as to which species this is. This is of importance as there are a number of variants in the B. spinulosa complex. The species description supports the il- lustration and it is given below to il- lustrate the nature of the botany of this period, the dual role that it served, and the mixture of science with the dissemination of popular gardening in- formation. ‘*Banksia spinulosa Prickly-leaved Banksia Gen. Char. Receptaculum commune elongatum, squamosum. Cor. tetrapetala. Stamina limbo inserta. Cap- sula_ bivalvis, disperma_ interjecto seminibus dissep imento mibili Common receptacle elongated, scaly. Cor. of four petals Stamina inserted into the limb. Capsule with two valves, two seeds and a moveable partition between them. Spec. Char. B. foliis linearibus mucronulatis apicem versus denticulato- spinosis. Leaves linear, revolute, with a little sharp point, and with spinous denticula- tions towards the top. This hitherto non-descript (undescrib- ed) species of Banksia has a woody 108 branched stem, the branches commonly three or more together, curved upwards, leaves irregularly scattered, closely covering the branches, on very short footstalks (petioles), but little spreading, from an inch and half to two inches in length, linear, very narrow, revolute in the margin, green and smooth above, white and downy beneath, ending very abruptly, tipped with three little spines and having several of the same kind hooked upwards in the margin par- ticularly towards the top. The young leaves are very downy. Flowers thick set in a cylindrical erect spike arising from the divarications of the branches. Their common receptacle is cylindrical, rather obtuse covered with closely imbricated downy scales, some of the lowermost of which terminate in a long downy arista and from among the rest the flowers come out in pairs. The structure of the flower is well expressed in the annexed plate. We suspect the fruit figures in Mr White’s voyage page 225 fig 1. may belong to this species but we have no positive proof to assert it. Our Banksia spinulosa differs from B. ericaefolia (sic) of Linnaeus (Herb. Linn.) in having leaves at least four times as long, obtuse but with a small central sharp point on the mid rib bet- ween the other two terminal points as well as having a greater or lesser of small sharp-hooked lateral teeth towards the end of each leaf. The natives of New south Wales call it ‘Wattangre’.’’ The cone illustrated by White (1790) is probably not as suggested from the B. spinulosa described by Smith but, may be from another member of the complex or from one of the forms of B. ericifolia. There is evidence that White sent other Banksia specimens to Smith. The Linnean Society holds a number of specimens of B. integrifolia as well as one labelled B. cuneata which appears to be the juvenile foliage of B. integrifolia but may be one of the forms of the com- plex it forms with B. marginata. There is Vic. Nat. Vol. 98 also a specimen of 8B. serratifolia Salisb., (B. aemula R. Br.) and another of B. asplentifolia Salisb., (B. oblongifolia Cav.) and it is the presence of these in the Linnean Society Her- barium which is an important clue to one of the bitterest controversies in banksia taxonomy. Other Anderson descriptions that are still valid are Callicoma serralifolia, Crowea saligna, Daviesia ulicifolia, Persoonia linearis, Styphelia tubiflora, S. viridis, Ziera Smithii. REFERENCES Andrews, H. C, 1797-1804. Repository 10 vols. London Curtis, W. 1797-1810 Curtis’s Botanical Magazine Vols 1-32. London. Gilbert, L. A. 1962. Botanical investigations of the eastern seaboard of Australia 1788-1810. Un- published. M.A. Thesis, University of New England. Keneally, T, 1967. Penguin. Australia. Rientis R. and T. 1963. Early Artists of Australia. Halstead Press. Sydney. Scott, E, 1916. A Short History of Australia. Oxford University Press, London. Smith, J. E. 1793-5. A Specimen of The Botany of New Holland. Sowerby. London. Smith, J. E. 1804-5. Exotic Botany. 2 Vols. Sowerby. London, Stafleu, F. A. 1966. Introduction to the facsimile edition of Novae hollandiae plantarum specimen (a Billardiere 1804) Historia Naturalis Classica, Weinberg. White, J. 1790. Journal of a Voyable to New South Wales. London. The Botanist’s Bring Larks and Heroes. Mammal Survey Group Contribution No.13 Mammals of the Wallaby Creek Catchment By B. A. CALLANAN* Introduction From September 1974 to November 1978 the mammal fauna of the Wallaby Creek Catchment of the Melbourne and Metropolitan Board of Works (MMBW) was examined by means of a series of sample surveys. A total of 1108 trap- nights and 42.4 spotlight hours resulted in nine native and five introduced mam- mal species being recorded. Wallaby Creek Catchment is situated on the Great Dividing Range approx- imately sixty kilometres north north-east of Melbourne. It adjoins the Broadford State Forest to the west and pine and hardwood forests, mixed farming, graz- ing and closer settlement to the east. The catchment forms part of Melbourne’s water supply system and public entry is prohibited. We are in- (*Mammal Survey Group, c/- Secretary 26 McCulloch Street, Nunawading.) May/June debted to the MMBW for permitting controlled entry of our group for these distribution studies. Logging is not undertaken within the area — manage- ment being oriented towards protection from fire and water supply interests. The extent of the examination is resolved for this report into seven specific study areas distributed throughout five major vegetation associations, defined as Mature Moun- tain Ash, Regrowth Mountain Ash, Unstocked Ash Site, Northern Mixed Eucalypt Species and Southern Mixed Eucalypt Species. These are shown in Fig. 1. Methods Within each study locality live trapping and spotlighting were the basic survey methods used. Chance sightings and daylight observations of mammals during the survey were recorded. Survey work included an examination of the 109 FIG1 WALLABY CREEK CATCHMENT (1 Mature Mountain Ash Co Regrowth Mountain. Ash Unstocked Ash Site [J Mixed Eucalypt Species 110 Vic. Nat. Vol. 98 habitat of each study locality. The method developed by Specht (1970) was used as the basis of vegetation description in the field. Where necessary to complete the structural definition of the vegeta- tion type, descriptions of intermediate, shrub and ground cover layers of vegetation have been used. Description of Study Area Geology and Physiography A detailed description of the geological features of the area local to Wallaby Creek has been publish- ed (Land Conservation Council 1973). The higher parts, including the mature Mountain Ash areas, are based on a granite formation which reaches its highest elevation of 800 m at Mount Disappointment just on the south-west boundary. The main plateau level corresponds to the Kinglake Geological surface. The localities of sample surveys varied in eleva- tion between 400 m on the southern escarpment to 750 m in the mature Mountain Ash area. Climate Table 1 gives rainfall and temperature figures for stations in the study area. They are from published data (Bureau of Meteorology 1966) and information supplied by the MMBW from the Disappointment Reference Area Management Plan, March 1979, MMBW. The Disappointment plateau is in a cool temperate zone with an average annual rainfall of approximately 1200 mm and a pronounced winter maximum. The plateau normally experiences wet winters and comparatively dry summers. Precipitation is generally in the form of rain with occasional hail and infrequent rapidly melting snow. Rainfall records have been kept since 1885 at the Wallaby Creek settlement on the north-eastern edge of the plateau. The table gives the monthly and an- nual long-term average rainfall at the settlement for the period 1885-1978, and for comparative pur- poses, Toorourrong which is south of the plateau and at a lower elevation, (1893-1978). Rainfall records taken on the plateau in mature Mountain Ash agree closely with the Wallaby Creek figures, Table 1. Climate. Temperature records for the plateau are not available. Estimates taken from mean isotherm charts (Director of Meteorology, 1968) are shown in Table 3. Temperature ranges are generally moderate, however frosts occur throughout the year and it could be expected that dew point is reached on most nights of the year. Summer temperatures can occa- sionally rise as high as 35°C or more. Streams The major streams draining the area form two groups, the first draining south into Toorourrong Reservoir, the remainder flowing north to where they are intercepted and channelled back across the Great Dividing Range into Toorourrong Reservoir. If not intercepted the south flowing streams would enter the Plenty River and the northerly streams would flow to the King Parrot Creek. Vegetation For the purpose of this report the habitats present in the Wallaby Creek catchment are divided into five types as follows: Mature Mountain Ash Regrowth Mountain Ash Unstocked Ash Site Northern Mixed Eucalypt Species (Northern Plateau) Southern Mixed Eucalypt Species (Foothills) Figure | outlines the distribution of the main habitat types. A general description of the vegetation of the area has been published (Land Conservation Council 1973), A brief description of the vegetation at each survey locality is given below. Species names are drawn from Willis (1970, 1972). Mature Mountain Ash Centred on the high dividing range to the east of Mt Disappointment, the mature Mountain Ash at Wallaby Creek was not destroyed by the 1926 and 1939 bushfires. The fire of 1926 burnt into part of this destroying some but leaving most, while the fires of 1939 did not approach near to the area. Rainfall (mm) — Monthly Means from all Records Jan Feb Mch Apr May Jne Wallaby Creek Settlement Oe OL A T2y SOF Toorourrong 54 56 S8 66 116 133 127 131 119 117 97 86 Jly Aug Sep Oct Nov Dec Year 1223 10m “G6 = GAS B86.) BZ FO 466 801 Temperature (°C) — Estimates from Mean Isotherm Charts (Director of Meteorology 1968) Catchment Plateau May/June Oct 16 6 The locations of specific survey efforts in this habitat type are shown in Fig. 1. The upper storey is a tall open forest of almost pure Mountain Ash standing 50 to 70 m high and having a canopy cover from 50 to 60 percent of total forest surface area. On the verge of the southern slopes Mountain Grey Gum Eucalyptus cypellocarpa merges pro- gressively with Mountain Ash as altitude decreases. The intermediate storey beneath the mature Mountain Ash varies from open to quite dense near the heads of gullies and streams. Species present in- clude Mountain Correa Correa lawrenciana, Silver Wattle Acacia dealbata, Blackwood Acacia melanoxylon, Hazel Pomaderris Pomaderris aspera, Musk Daisy Bush Olearia argophylla, Blanket-leaf Bedfordia salicina, taller Victorian Christmas Bush Prostanthera lasianthos, with occa- sional Southern Sassafras Atherosperma moschatum and Austral Mulberry Hedycaria angustifolia. Species present in the shrub and heath layer in- clude Silky Tree Fern Dioksonia antarctica, Rough Tree Fern Cyathea australis, Prickly Current Bush Coprosma quadrifida, Victorian Christmas Bush Prostanthera Jasianthos, Rough Coprosma Coprosma hirtella and Sweet Bursaria Bursaria spinosa. The density and variety of shrubs is greatest near streams and varies elsewhere with the amount of available light, At the heads of well lit south-east facing gullies tall shrubs are quite dense, including, with the above, Golden-tip Goodia lotifolia, Snowy Daisy- bush Olearia lirata, Common Dogwood Cassinia aculeata, Bootlace Bush Pimelea axiflora, Prickly Moses Acacia verticillata and Holly lomatia Lomatia ilicifolia. The ground cover beneath the Mountain Ash varies with the amount of light and moisture available. Leaf litter and fallen tree limbs are pre- sent throughout. Some areas are sparsely covered below the spindly stems and branches of Mountain Correa and hazel Pomaderris. In other relatively flat and more damp areas, ferns and sedges from knee to waist high form entanglements around fallen logs and hanging branches of tall shrubs. Ferns and creepers become more dense near streams when tree ferns do not completely block light penetration. Species present include the hard Water-fern Blechnum procerum, Fishbone Water-fern 8B. nudum, Mother Shield Fern Polystichum pro- liferum, Saw Sedge Gahnia sp, and Austral Bracken Pteridium escultenum. Grasses are present but sparse. In some more open areas the ground cover in- cludes Hop Goodenia Goodenia ovata, mat rushes and patches of non-stinging nettle. Regrowth Mountain Ash Two specific survey efforts in regrowth Mountain Ash were located centrally between Poley Creek and 112 Fig. 2. Mature Mountain Ash forest. the head of Stoney Creek, and to the northeast. (Ref. Fig. 1). The upper storey of this habitat type is a tall (‘poles’) open forest structure of almost pure young Mountain Ash approximately fifty years old and reaching forty five metres high. Amongst the closer trunks of the Mountain Ash regrowth the intermediate storey includes isolated Blackwood and Stinkwood Zieria anborescens but is much more sparse than in Mature Mountain Ash habitat. The shrub layer in this habitat type has the struc- ture of very sparse tall heath. Species present in- clude Tree Lomatia, Common Dogwood and Prick- ly Moses. Ground cover beneath the almost complete cover of young Mountain Ash is a light tangle of shrubs midst fallen forest debris. Species present include Austral Bracken, Clematis, Bootlace Bush and Hop Goodenia. Unstocked Ash Site Small isolated areas of the Wallaby Creek Catch- ment remain unstocked with the original Mountain Ash following its destruction by fire in 1926, The upper storey of the remaining tall scrub habitat includes species which are usually in- termediate beneath mature Mountain Ash habitat. The structure in some places particularly in the eastern area is a dense closed forest of Silver Wattle and Hazel Pomaderris groves. On more exposed positions in the central Unstocked Ash area the up- per storey gives way to open bracken. Vic. Nat. Vol. 98 The shrub layer of this habitat is almost absent in places where light does not penetrate. In more open areas Austral Bracken predominates and Sweet Bur- saria and Common Dogwood are occasionally pre- sent. Beneath the dense hazel and wattle, ground cover is sparse with some sedges and Prickly Starwort Stellaria pungens. Specific work in the unstocked ash habitat type was located at two sites: an eastern site and a central site north of Poley Creek. Southern Mixed Eucalypt Species Five specific survey efforts in this habitat type, which is quite distinct from Northern Mixed Euc. Species habitat, were located as shown in Fig. 1. These included crossings of the Plenty River and Jacks Creek. May/June The dominant vegetation of the southern excarp- ment is an open forest of mixed eucalypt species in- cluding Messmate Eucalyptus obliqua, Narrow leaf- ed Peppermint E. radiata with some Mountain Grey Gum. Isolated Manna Gum £. viminalis occurs near streams. The understorey and tall shrub layer is only noticeably present in damp gullies and includes Musk Daisy, Hazel Pomaderris, Blanket leaf, Vic- torian Christmas Bush, Silver Wattle and Prickly Tea Tree Leptospermum juniperinum. The shrub layer in this foothill forest is generally open however near streams it occasionally tangles together about 2 m from the ground. It includes Prickly Moses, Australian Clematis Clematis aristata, Silver Banksia Banksia marginata, Hop Goodenia Goodenia ovata, Narrow leafed Wattle Acacia mucronata, Bush Peas Pultenea sp. and Common Dogwood, Austral Bracken Fern dominates the forest floor. Occasional rushes and sedges are also present in the ground vegetation which is generally sparse varying from a fairly dense fern and low shrub community immediately by stream channels, through dense bracken patches to dry open cover of grasses thin leaf litter with some herbs including small rice flower Pimelea sp., violet Viola sp., and Pink-bells Tetratheca ciliata. Northern Mixed Eucalypt Species Four survey localities were situated in the nor- thern mixed eucalypt species habitat type including riparian habitat along Silver Creek. Pan Oy, 113 Spotlighting was carried out near the Wallaby Creek settlement in the east and also on the west side of the survey area. The upper stratum of this habitat type has a tall open forest structure at places closing to greater than 70% canopy cover. Species include Messmate, peppermint, Mountain Grey Gum with some Moun- tain Ash and Manna Gum. The intermediate storey is a tall shrubland struc- ture only really significant in cover and height near streams, Species include Silver Wattle, Prickly Moses and Hazel Pomaderris, In other areas a very open sapling understorey is occasionally present. The shrub layer forms an open heath structure of Austral Bracken, Hop Goodenia, Holly Lomatia Lomatia sp., Snowy Daisy Bush, Common Dogwood, Sweet Bursaria and Bush Pea. This merges with the ground cover which includes Kangaroo Fern Microsorium diversifolium and Common Ground Fern Culcita dubia. Results Table 2 lists all mammal species iden- tified in each specific study area with the corresponding extent of survey effort expressed in numbers of trapnights and spotlight hours. This table indicates whether the animals were recorded dur- ing trapping, while spotlighting, or by chance. Table 2 lists also the propor- tions of survey success per species in Cin iW ‘Ln Fig. 6, Northern Mixed Eucalypt forest, 114 each locality. For trapped species the figures in parentheses are the numbers captured per 100 trapnights while for species detected by spotlight the figures in parentheses are the numbers seen per 100 spotlight hours. These figures should only be used for comparison within each survey method for this report. In this table a dash means that the relevant survey method was not car- ried out whilst a zero indicates no positive results. Table 3 allocates the species recorded to specific minor grids numbered in ac- cordance with Brook (1976). Again recordings per 100 trapnights and 100 spotlight hours are entered in paren- theses for each species in each grid where applicable. The study area is situated mainly in the three minor (Smin x 5min) grid localities 867,25.4, 867,26.1 and 867,26.3 with a small part situated in minor grid locality 867,26.2. For the purposes of this report all species iden- tified are located within the three former grids. Notes on Species Recorded The specimen catalogue numbers refer to specimens lodged with either the Fisheries and Wildlife Division or the National Museum. ORDER MARSUPIALIA — Family Macropodidae 1. Grey Kangaroo — Macropus giganteus Shaw Two specimens were located along the boundary of the central Unstocked Ash and Northern Regrowth Ash, A further two specimens were sighted in the Southern Mixed Eucalypt Species habitat. 2. Black Wallaby — Wallabia bicolor (Desmarest) This species was recorded from five habitat types, two (12.5%) in Mature Mountain Ash, three (43%) in Central Ash Regrowth, one (chance) in Unstock- ed Ash Site, five (50%) in Northern Vic. Nat. Vol. 98 Table 2. Mammals Recorded SURVEY LOCALITIES Mature Ash Regrowth Unstocked Ash Site Mixed Eucalyptus Total Mountain Species Ash Northern Central Central Eastern Northern . } 2 3 4 5 6 1 Trap Nights 450 80 161 16 60 106 175 1108 Spotlight Hours 16 - 1 - - 8 4 42.4 Species Trapped (Numbered as in ‘Notes on Species’) 8 Antechinus stuartii 23(5.1) 0 8 (5.0) 0 0 0 17 (9.7) 48 (4.3) 9 Antechinus swainsonii 7(1.6) 0 2(1.2) 1 (1.3) 0 0 2(L.1) 12 (1.1) 10 Rattus fuscipes 73 (16.2) 16 (20.0) 6 (3.7) 10 (13.2) 6 (10.0) 11 (10.4) 7(4.0) 129 (11.6) 11 Rattus rattus 0 0 0 0 0 0 1 (0.6) 10.1) 14 Mustela putorius 0 0 0 0 1 (1.6) 0 0 1(0.1) Species Identified During Spotlighting 1 Macropus giganteus 0 - 1 (14.3) - - 0 0 1 (2.4) 2 Wallabia bicolor 2(12.5) - 3.(42.9) - - 4(50) 0 9 (21.2) 3 Trichosurus vulpecula 0 - 1 (14.3) - - 0 0 1 (2.4) 4 Pseudocheirus peregrinus 12(75.0) - 1 (14.3) - - 2(25) 0 15 (35.4) § Schoinobates volans 3 (18.8) - 0 - - 1 (13) 1 (8.8) 5 (11.8) 7 Vombatus ursinus 3(18.8) - 1 (14.3) - - 3 (38) 0 7 (16.5) 12 Oryctolagus cuniculus 0 - 0 - - 5 (63) 0 § (11.8) 13 Vulpes vulpes 0 - 0 - . 1 (13) 0 1 (2.4) 15 Cervus unicolor 0 - 0 - - 1 (13) 0 1 (2.4) Species Recorded by Chance During the Survey 1 Macropus giganteus 1 2 2 2 Wallabia bicolor 1 ! 3 5 6 Acrobates pygmaeus 2 2 7 Vombatus ursinus 1 I 2 12 Oryctolagus cuniculus 3 3 13 Vulpes vulpes 1 1 Figures in parentheses are — for trapped species — numbers captured per 100 trap nights. — for species detected by spotlight — numbers seen per 100 spotlight hours. Table 3, Minor Grid Location of Species, Minor Specific Mammal Species (numbered as in ‘Notes on Species’) No of Grid Survey Specie Location Effort 1 ep. sae ee SNS OF 9 1S ell ise is ae Ss ingnd (Mg) (Wb) (Tv) (Pp) (Sv) (Ap) (Vu) (Ast) (ASw) (Rf) (Rr) (Oc) (Vv) (Mp) (Su) Trap Spotlight nights Hours 867,25.4 60 - ee et em Toe lh 1 Oo fe 0 - =- = = = = = (3) (17) 0 0 -—- = 0 867,26.1 423 15 a a | 7 es ae eat Soe eee ae Sh Pg (6.7) (47) (6.7) (20) (6.7) 0 (27) (1.9) (0.7) (10) 0 (33) (6.7) 0 867,26.3 625 21.4 aeaetiva