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TIS
SOCIETY OF QUEENSLAND
published by
THE ENTOMOLOGICAL
ISSN 1320 6133
Volume 33, Part 1, 12 March 2006
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THE AUSTRALIAN ENTOMOLOGIST
ABN#: 15 875 103 670
The Australian Entomologist is a non-profit journal published in four parts annually
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ENTOMOLOGICAL SOCIETY OF QUEENSLAND
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Cover: This undescribed ant spider (Zodariidae), known only from the Expedition
Range, is one of about 25 new Habronestes species from Queensland. In Australia,
Habronestes is one of the most diverse genera of ant spiders with almost 130 species,
of which only about one fifth are described. They are small to medium-sized spiders
(2 — 12 mm in length) and most can be recognised by the bright yellow or orange
spots on their backs and the distinctive palps of the males. Illustration by Barbara
Baehr.
Australian Entomologist, 2006, 33 (1): 1-4
THE INSECT COMPLEX INHABITING GALLS FORMED BY
CECIDOMYIA ACACIAELONGIFOLIAE SKUSE (DIPTERA:
CECIDOMYIIDAE) ON BLACKWOOD (ACACIA MELANOXYLON)
IN TASMANIA
R. BASHFORD
Forestry Tasmania, GPO Box 207, Hobart, Tas 7001
(email: dick. bashford@forestrytas.com.au)
Abstract
Cecidomyia acaciaelongifoliae Skuse is newly recorded from Tasmania, where it forms galls on
blackwood, Acacia melanoxylon, a new host record. Five species of Lepidoptera and four species
of Hymenoptera were found to be associated with the galls.
Introduction
Blackwood, Acacia melanoxylon R. Br. (Mimosaceae), is a valued timber
tree, endemic to eastern Australia and Tasmania and introduced to other
countries such as South Africa and New Zealand. The timber is the basis of
an important furniture and veneer industry in Tasmania and the expansion of
the blackwood estate through plantation development has been an important
development in adding value to Tasmania’s forest industry. As a tree species
it has few insect pests of significance to growth increment (Jennings 1991).
In New Zealand, 18 species of insects have been recorded feeding on
blackwood (Appleton and Walsh 1997).
Flower bud gall formation on blackwood has not been recorded previously
from Tasmania (Bashford 2004), although Trichilogaster acaciaelongifoliae
(Froggatt) (Hymenoptera: Pteromalidae) galls have been reported on
blackwood in South Africa (Dennill et al. 1993). Froggatt (1923) described
the wattle gall-fly, Cecidomyia acaciaelongifoliae Skuse, as being common
on the foreshores of Sydney Harbour, NSW, on long-leafed wattles.
McKeown (1942) reported C. acaciaelongifoliae attacking the flower buds of
several Acacia species in New South Wales, causing a twisted mass of green
tubes which later turned brown as they dried.
Materials and methods
Galls were initially collected in March 2000, from several blackwood trees
growing in Lauriston Reserve near George Town in northern Tasmania. Both
green (Fig. 1) and dried, brown galls were collected in January and February
2001. The galls were placed in paper bags and transferred to laboratories in
Hobart the same day. The galls were then placed individually into plastic
food containers with perforated lids to prevent condensation. The containers
were placed in a controlled temperature room at 18°C and examined weekly
for insect emergence. Single, galled blackwood trees were also detected in
recreational parks at Burnie and Deloraine. All infested trees located were
exposed trees in open situations. Routine surveys of blackwood plantations
by Forest Health officers found no other evidence of galled plants.
2 Australian Entomologist, 2006, 33 (1)
Specimens of the cecidomyiid fly and hymenopteran parasitoids reared from
the galls were sent to the Australian National Insect Collection in Canberra
for identification.
Fig. 1. Developing galls on Acacia melanoxylon in Tasmania, caused by Cecidomyia
acaciaelongifoliae.
Results
The ten insect species reared from the galls are listed in Table 1. Apart from
Cecidomyia acaciaelongifoliae, five species of Lepidoptera and four species
of Hymenoptera were recorded.
Discussion
Cecidomyia acaciaelongifoliae is newly recorded from Tasmania and Acacia
melanoxylon is a new host record.
All Lepidoptera species emerging from the galls were recorded from other
Acacia galls in previous studies (Bashford 2002, 2004). Of the four species of
Hymenoptera recorded, the ichneumonid Glabridorsum stokesii (Cameron) is
a common parasitoid of Lepidoptera larvae inhabiting galls in Tasmania.
Platygasterids are mainly parasitoids of cecidomyiids (Masner 1993, J.
LaSalle pers. comm.) and species of Torymoides Walker (Torymidae) are
known mainly from dipteran galls, including those caused by cecidomyiids
(J. LaSalle pers. comm.). Species of Sierola Cameron (Bethylidae) have been
reared from other types of gall on Acacia species in Tasmania, usually
associated with lepidopteran inquilines (Bashford 2004).
Australian Entomologist, 2006, 33 ( 1) 3
The large number and unusual structure of the galls found on the affected
trees in Tasmania caused shoot dieback and reduced seed production
markedly. Any biotic agent that has an impact on growth increment and form
needs to be identified and its impact risk factored into growth models. The
establishment of plantations off-site may result in an increase in biotic loads,
especially if trees are under stress, and knowledge of insect pests and diseases
1s an Important component in developing high quality sustainable timber
products. Records of insect pests that have the potential to become a problem
in a rapidly increasing blackwood plantation estate are of value in
determining management decisions.
Table l. Insect species reared from flower bud galls formed by Cecidomyia
acaciaelongifoliae on Acacia melanoxylon in Tasmania.
Insect species Family Number of
specimens
DIPTERA
Cecidomyia acaciaelongifoliae Skuse Cecidomyiidae 237
LEPIDOPTERA
Erechthias mustacinella (Walker) Tineidae 66
Opogona comptella (Walker) Tineidae 3
Polysoma eumetalla (Meyrick) Gracillariidae 6
Stathmopoda chalcotypa Meyrick Oecophoridae 22
Macrobathra sp. Cosmopterigidae 3
HYMENOPTERA
Glabridorsum stokesii (Cameron) Ichneumonidae 12
Sierola sp. Bethylidae 32
Torymoides sp Torymidae 154
Genus and species indet. Platygasteridae 287
Acknowledgements
I thank Dr John LaSalle at the Australian National Insect Collection for his
help in examining the Hymenoptera and Dr Don Colless for confirming the
identification of the cecidomyiid gall former. I also thank Comalco
Aluminium (Bell Bay) Limited for allowing access to trees in Lauriston
Reserve.
References
APPLETON, C. and WALSH, P. 1997. Insect pests associated with Blackwood (Acacia
melanoxylon) in New Zealand. New Zealand Tree Grower 18(1): 38-39.
BASHFORD, R. 2002. The insect fauna inhabiting Uromycladium (Uredinales) rust galls on
silver wattle (Acacia dealbata) in Tasmania. Australian Entomologist 29(3): 81-95.
4 Australian Entomologist, 2006, 33 (1)
BASHFORD, R. 2004. The insects associated with galls formed by Trichilogaster
acaciaelongifoliae (Froggatt) (Hymenoptera: Pteromalidae) on Acacia species in Tasmania.
Australian Entomologist 31(1): 5-12.
DENNILL, G.B., DONNELLY, D. and CHOWN, S.L. 1993. Expansion of the host-plant range
of a biocontrol agent of Trichilogaster acaciaelongifoliae (Pteromalidae) released against the
weed Acacia longifolia in South Africa. Agriculture, Ecosystems and Environment 43:1-10.
FROGGATT, W.W. 1923. Other insects of the wattle. P. 121, in: Forest insects of Australia.
Government Printer, Sydney.
JENNINGS, S.M. 1991. Blackwood. Native Forest Silviculture Technical Bulletin No, 10.
Forestry Commission, Tasmania; 28 pp.
MASNER, L. 1993. Superfamily Platygasteroidea. Pp 558-565, in: Goulet, H. and Huber, J.
(eds), Hymenoptera of the world: an identification guide to families. Research Branch,
Agriculture Canada, Ottawa; 668 pp.
McKEOWN, K.C. 1942. Flies. P. 221, in: Australian insects. Royal Zoological Society of New
South Wales Handbook.
Australian Entomologist, 2006, 33 (1): 5-7 5
FIRST CONFIRMED OBSERVATION OF HETERONYMPHA
CORDACE WILSONI BURNS (LEPIDOPTERA: NYMPHALIDAE:
SATYRINAE) IN SOUTH AUSTRALIA
BRYAN T. HAYWOOD! and VICKI NATT?
'CMB, Moorak, SA 5291
?1] Wilhelmina St, Kingston SE, SA 5275
Abstract
A population of Heteronympha cordace wilsoni Burns was discovered in South Australia east of
Port MacDonnell in December 2004. Although it is unknown if the species is breeding at or near
this site, due to the apparent lack of its host plant, this appears likely because of the extremely
fresh condition of some of the specimens observed. H. cordace wilsoni was presumed extinct
from various localities where it was once common and this is the first documented observation
for over 27 years.
Introduction
The bright-eyed brown, Heteronympha cordace (Geyer), is a geographically
variable satyrine with two subspecies found in southeastern Australia and
three others restricted to Tasmania (Braby 2000). Subspecies H. c. wilsoni
Burns has been recorded only from southwestern Victoria, from the Wannon
River in the Grampians southwest to Dartmoor and Nelson (Braby 2000,
Dunn et al. 1994, Sands and New 2002). It was suspected (but not confirmed)
to occur in South Australia by Grund (1998).
Dunn ef al. (1994) rated the conservation status of H. c. wilsoni as
‘Vulnerable’, Grund (1998) as ‘Endangered’ in South Australia and Sands
and New (2002) as ‘Critically Endangered’ throughout its range. Previous
reports and studies (Fisher 1978, Grund and Hunt 2000) failed to record
and/or find this species in South Australia but Grund and Hunt (2000)
suggested it could be present as suitable habitat occurs.
H. c. wilsoni occurs in swampy areas where its host plant Carex appressa is
present (Grund and Hunt 2000, Sands and New 2002, Dunn ef al. 1994).
Adults are not known to fly far from sites where the larval food plant occurs
and have a slow, meandering flight close to the ground among the larval food
plants, unlike other species of Heteronympha Wallengren (Braby 2000).
H. c. wilsoni is smaller and paler than typical H. c. cordace, the orange
markings on the upperside are paler and more extensive and the eyespots
much smaller. The underside ground colour is paler, with the markings on the
hind wing obscure and ill-defined. The eyespots on the underside are smaller
or absent (Dunn et al. 1994, Braby 2000, Sands and New 2002).
First South Australian observations
Observers. Vicki Natt, Elaine Lawson, Jean Haywood and Bryan Haywood.
Locality. Between the South Australia/Victoria border and Port MacDonnell
in the lower southeast of South Australia.
6 Australian Entomologist, 2006, 33 (1)
Habitat. Leptospermum lanigerum shrubland with Phragmites australis,
Myoporum insulare, Acacia longfolia var sophorae and various species of
Cyperaceae.
Observations. In mid to late afternoon on 30 December 2004, in fine, mild
weather, V. Natt, E. Lawson and J. Haywood noticed three to four small,
orange butterflies flitting around and feeding on creeping brookweed
(Samolus repens) flowers that bordered the rushes. After being disturbed they
did not fly far and usually alighted on or near another Samolus flower. They
were similar in colouring to the common brown, Heteronympha merope
merope (Fabricius), but smaller, with a much more distinctive black and
orange pattern that was striking on the upperside of both fore and hind wings
and on the underside of the forewing. The underside of the forewing had less
distinct, more subdued pattern/colouring.
The individuals observed (Figs 1-2) had eyespots with blue centres on both
fore and hind wings. On limited occasions we observed them open their
wings, when we could see a very tiny eyespot at the top of the upperside of
the hind wing. Several digital photographs were taken and these were enough
to work from for an identification using Braby (2000).
Subsequent visits to the site in January 2005 by B. Haywood found that the
butterfly was still flying and both sexes were present. On several occasions
observations were made of a smaller and paler (presumed male) individual
pursuing a larger (presumed female) individual throughout the site. The last
visit to the site was on 24 January, with one male and one female observed.
Discussion
The individuals of H. c. wilsoni observed at the site were identical to those
described in Braby (2000) and Dunn et al. (1994); however, there are a few
additional features to report. A photograph of one specimen had one bluish-
white spot above the subtornal eyespot on the underside of the hind wing.
Also, minute white spots are evident between the two upperside hind wing
eyespots, and one below the apical eyespot on the forewing. Specimens
photographed in the field showed much variation in these markings and they
were not always present. Further taxonomic investigations are warranted on
this population.
Drainage, wildfire and cattle grazing have been identified as threatening
processes against the long-term survival of this species. In South Australia,
these Carex swamp habitats are now severely degraded and fragmented
(Grund and Hunt 2000). Alterations to hydrology in potential habitat areas
should be closely scrutinised before permission to alter these areas is granted.
Sands and New (2002) highlighted the poor dispersal ability of this butterfly,
rendering isolated populations susceptible to extinction from habitat loss or
degradation. This fact highlights the importance of connectivity between
colonies, as natural re-colonisation is unlikely in a fragmented landscape.
Australian Entomologist, 2006, 33 (1) 7
Figs 1-2. Heteronympha cordace wilsoni in South Australia. (1) perched on reed; (2)
basking.
Braby (2000), Grund and Hunt (2000) and Grund (1998) all noted that this
species flies close to the ground amongst the larval food plant. Carex
appressa was not observed where the butterflies were flying, so this is
inconsistent with our observations. Further surveys should be undertaken in
South Australia and Victoria to ascertain whether past populations are still
extant, whether new populations can be found, and if they are using a
different host plant.
Acknowledgements
We thank Jan Forrest (South Australian Museum, Adelaide) for information
on specimens held in the Museum, Dianne Smith (DEH Library, Canberra)
for assistance in accessing reference material, and Lucy Brindley and Luke
Campbell for providing additional photographs for analysis. Fabian Douglas
and Roger Grund are especially thanked for their input, interest and
enthusiasm towards this finding and future work on this species.
References
BRABY, M.F. 2000. Butterflies of Australia: their identification, biology and distribution. 2
Vols. CSIRO Publishing, Melbourne; xx + 976 pp.
DUNN, K.L., KITCHING, R.L. and DEXTER, E.M. 1994. The conservation status of Australian
butterflies. Australian National Parks and Wildlife Service, Canberra.
FISHER, R.H. 1978. Butterflies of South Australia (Lepidoptera: Hesperioidea, Papilionoidea).
Government Printer, South Australia; 272 pp.
GRUND, R. 1998. Butterflies of South Australia website. www.chariot.net.au/~rgrund
GRUND, R. and HUNT, L. 2000. Butterfly conservation in the Lower South East Region.
National Parks Foundation Inc., Adelaide.
SANDS, D.P.A. and NEW, T.R. 2002. The action plan for Australian butterflies. Environment
Australia, Canberra; 378 pp.
8 Australian Entomologist, 2006, 33 (1)
RECENT ENTOMOLOGICAL LITERATURE
ANDERSEN, N.M. and WEIR, T.A.
2004 Australian water bugs: their biology and identification (Hemiptera-Heteroptera,
Gerromorpha & Nepomorpha). Entomonograph Volume 14. CSIRO Publishing,
Collingwood & Apollo Books; 344 pp.
BALKE, M. and RIBERA, I.
2004 Jumping across Wallace’s line: Allodessus Guignot and Limbodessus Guignot revisited
(Coleoptera: Dytiscidse: Bidessini) based on molecular-phylogenetic and morphological
data. Australian Journal of Entomology 43(2): 114-128.
BARTON, P.S., ABERTON, J.G. and KAY, B.H.
2004 Spatial and temporal definition of Ochlerotatus camptorhynchus (Thomson) (Diptera:
Culicidae) in the Gippsland Lakes system of eastern Victoria. Australian Journal of
Entomology 43(1): 16-22.
BELOKOBYLSKIJ, S.A., WHARTON, R.A. and LA SALLE, J.
2004 Australian species of the genus Opius Wesmael (Hymenoptera: Braconidae) attacking
leaf-mining Agromyzidae, with the description of a new species from South-east Asia.
Australian Journal of Entomology 43(2): 138-147.
BRABY, M.F., TRUEMAN, J.W.H. and EASTWOOD, R.
2005 When and where did troidine butterflies (Lepidoptera: Papilionidae) evolve?
Phylogenetic and biogeographic evidence suggests an origin in remnant Gondwana in
the late Cretaceous. /nvertebrate Systematics 19(2): 113-143.
CHRISTIDIS, F. and DEAN, J.C.
2005 Three new species of Austrophlebioides Campbell and Suter (Ephemeroptera:
Leptophlebiidae: Atalophlebiinae) from the wet tropics bioregion of north-eastern
Australia. Australian Journal of Entomology 44(2): 132-143.
DAWES-GROMADZKI, T.Z.
2005 The termite (Isoptera) fauna of a monsoonal rainforest near Darwin, northern Australia.
Australian Journal of Entomology 44(2): 152-157.
de JONG, R.
2003 Are there butterflies with Gondwanan ancestry in the Australian region? Invertebrate
Systematics 17: 143-156.
EDWARDS, C.M. and LA SALLE, J. j
2004 A new species of Closterocerus Westwood (Hymenoptera: Eulophidae), a parasitoid of
serpentine leafminers (Diptera: Agromyzidae) from Australia. Australian Journal of
Entomology 43(2): 129-132.
ELLIOTT, M.G.
2005 First record of the genus Brachygaster Leach (Hymenoptera: Evaniidae) from Australia
with the description of a new species. Australian Journal of Entomology 44(1): 2-5.
GILCHRIST, A.S., SVED, J.A. and MEATS, A.
2004 Genetic relations between outbreaks of the Queensland fruit fly, Bactrocera tryoni
(Froggatt) (Diptera: Tephritidae) in Adelaide in 2000 and 2002. Australian Journal of
Entomology 43(2): 157-163.
HETERICK, B.E.
2005 Identity of Monomorium occidaneum Crawley, a species inquirenda, and status of
Monomorium micron Crawley (Hymenoptera: Formicidae). Australian Journal of
Entomology 44(2): 122-131.
Australian Entomologist, 2006, 33 (1): 9-22 9
BUTTERFLY (LEPIDOPTERA) RECORDS FROM THE DARWIN
REGION, NORTHERN TERRITORY
C.E. MEYER’, R.P. WEIR? and D.N. WILSON?
110 Anne Clark Avenue, Nicholls, ACT 2913
?] Longwood Avenue, Leanyer, NT 0812
?28 Mahaffey Road, Howard Springs, NT 0835
Abstract
From 1990 to 2005, 87 of the 111 butterfly species recorded from Darwin in the Northern
Territory were reared or collected by the authors from within a 15 km radius of the city centre.
Details of localities and months of capture are provided, together with notes on the additional 24
recorded species not collected during the survey.
Introduction
The remoteness of Darwin, in the ‘Top End’ of the Northern Territory in
Australia, is the principal reason why only a small number of butterfly
workers visited the region in the past. Early butterfly workers, such as F.P.
Dodd in 1908 and 1909, had to endure long sea journeys (Monteith 1991)
and, on arrival, were faced with limited access to potential collecting areas.
Much of the early collecting was restricted to the local Port Darwin area or
from sites such as Rum Jungle, Adelaide River, Brocks Creek and Pine
Creek, all sidings along the rail line south from Port Darwin, as road access
was limited. In recent years, improvements in road conditions and readily
accessible air travel has seen more butterfly workers visiting Darwin yet, to
the best of our knowledge, no checklist of butterflies for the Darwin region
has ever been published.
For the purposes of this paper, the Darwin ‘region’ is defined as the area
within a 15 km radius of the city centre. Collecting localities are mapped in
Figure 1 and listed, together with habitat data, in Table 1. Over the past 15
years we have recorded 87 butterfly species from the Darwin region. These
records are listed in Table 2, along with locality and months of capture or
emergence. Literature records for a further 24 species from Darwin are
reviewed and discussed, all of which require further data to confirm their
existence in the Darwin region.
We follow the scientific nomenclature of Common and Waterhouse (1981) in
order to maintain consistency with the International Code of Zoological
Nomenclature, and have retained historical subspecies names except where a
taxonomic revision of a species or subspecies has been published.
Darwin plant habitats
Brock (1993) described three broad categories of habitat, showing a natural
progression from sandstone through lowland to coastal plant communities.
The Darwin region consists of lowland to coastal plant communities,
although on Channel Island a remnant sandstone plant community exists,
supporting Baronia lanceolata (Rutaceae), a food plant for Nesolycaena
10 Australian Entomologist, 2006, 33 (1)
urumelia (Tindale) (Edwards 1980, Meyer 1996b). Brock (1993) further
subdivided these lowland and coastal habitats into plant communities
associated with open forest or woodland, monsoon vine forests, swamps and
mangroves. We follow Brock’s descriptions for the data provided in Table 1,
except that an additional habitat of parkland has been added to cover parks
and reserve areas in suburban Darwin, where council plantings of Pongamia
pinnata (Fabaceae), Calophyllum inophyllum (Clusiaceae) and host trees
supporting the mistletoe Decaisnina signata (Loranthaceae) can be readily
found.
i
A!
li
20 1124
Northern |
Suburbs mae
13,4 are 24
4
(NM Jh; v^
| fo |
S SES [ss | |
ITS EG ||
^ 26 ; t
ees a
Berrimah
mt Ji
VON
Darwin CBD
East Arm
ae
Humpty Doo
Fig. 1. Map of collecting localities in the Darwin region. (Based on a map taken from
http://uluru.nt.gov.au/prod/bams/inventory/index.cfm?fuseaction-inventory&hreflink
=D11)
Australian Entomologist, 2006, 33 (1)
Table 1. Key to butterfly locality and habitat data for sites shown in Fig. 1. The letters
under the Habitat heading refer to the following plant community keys: Open
Locality Habitat
l Darwin Esplanade P,V
2 Doctors Gully P
3 Administrators Hill P
4 Francis Bay P
5 Stuart Park Jungle V
6 Stuart Park Primary School P
7 Myilly Point P
8 Fannie Bay P
9 Darwin High School P
10 Parap P
|l] East Point Reserve V
12 Nightcliff Beach V
13 Nightcliff Esplanade P
14 Rapid Creek P
15 Coconut Grove P
16 Velodrome, McMillians P
Road
Woodland (O); Monsoon Vine Forest (V); Swamp (S); Mangroves (M); Parkland (P).
Locality Habitat
17 Bagot Reserve ` P
18 |. Darwin Golf Club P
19 — Wagaman P
20 Casuarina Beach P
21 Lee Point V
22 Buffalo Creek off Lee Point VO
Road
23 Buffalo Creek Jungle V,M,S
24 . Leanyer P
25 Holmes Jungle V
26 Winnellie (0)
27 Berrimah (0)
28 Bens Hill, Trade Oo
Development Zone
29 + Thorak Road O
30 Shoal Bay V,M,S,O
31 Palmerston P
32 Channel Island via V,M,O
Palmerston
Table 2. Darwin butterflies collected or reared by the authors from 1990-2005.
Species
HESPERIIDAE
Hasora chromus chromus (Cramer)
Hasora hurama hurama (Butler)
Badamia exclamationis (Fabricius)
Chaetocneme denitza (Hewitson)
Neohesperilla xiphiphora (Lower)
Neohesperilla crocea (Miskin)
Neohesperilla senta (Miskin)
Hesperilla sexguttata Herrich-Schäffer
Taractrocera anisomorpha (Lower)
Taractrocera dolon diomedes Waterhouse
Taractrocera ina Waterhouse
Ocybadistes flavovittatus vesta
(Waterhouse)
Ocybadistes walkeri olivia Waterhouse
Ocybadistes hypomeloma vaga
(Waterhouse)
Suniana lascivia larrakia Couchman
Localities
(see Table 1)
7,13,14,22,30
22
11,21,22,27,30
31
28
27,29
27
22,23,30
29
1,3
1,2,5,6,22,29,31
31
1,5,22,29,31
5,27
1,3,5,6,29
Months collected / emerged
JFMAMJJASOND
X
x
X
XX XX
Species
Suniana sunias sauda Waterhouse
Telicota colon argeus (Plótz)
Telicota augias argilus Waterhouse
Cephrenes trichopepla (Lower)
Cephrenes augiades (C. Felder) ssp.
Parnara amalia (Semper)
Borbo impar lavinia (Waterhouse)
Pelopidas lyelli lyelli (Rothschild)
PAPILIONIDAE
Graphium eurypylus nyctimus (Waterhouse
& Lyell)
Papilio fuscus canopus Westwood
Papilio demoleus sthenelus W.S. Macleay
Cressida cressida cassandra (Waterhouse &
Lyell)
PIERIDAE
Catopsilia pomona pomona (Fabricius)
Catopsilia scylla etesia (Hewitson)
Eurema hecabe hecabe (Linnaeus)
Eurema alitha (C. & R. Felder)
Eurema laeta sana (Butler)
Elodina walkeri Butler
Delias argenthona fragalactea (Butler)
Delias mysis aestiva Butler
Belenois java teutonia (Fabricius)
Cepora perimale scyllara (W.S. Macleay)
Appias paulina ega (Boisduval)
NYMPHALIDAE
Danaus petilia (Stoll)
Danaus affinis affinis (Fabricius)
Tirumala hamata hamata (W.S. Macleay)
Euploea core corinna (W.S. Macleay)
Euploea sylvester pelor Doubleday
Australian Entomologist, 2006, 33 (1)
Localities
(see Table 1)
1,5,27
5,21,29,31
5,11,20,21,22,
29,30,32
17,22,26,28,30,
31
5,11
11,22,23,27,28
5,6,22,31
5,6,11,21,22,27
1,5,11,20,21,22,
32
5,11,20,21,22,
23,30,31,32
4,11,20,30,31
11,21,26,27,28,
30,31,32
7,11,14,20,21,
22,30,31,32
1,11,31
1,10,11,28,30,
31,32
11,28,32
21,30
1,11,20,21,22,
30,32
6,8,9,10,13,14,
15,16,28,31
5,2327
30
11,21,22,30
11,21,22,30
11,21,22,23,30,
31,32
11,21,22,23,30,
31,32
6,30
11,20,22,23,30,
31,32
11,21,30,32
Months collected / emerged
JFMAMJJASOND
X
Xx
XXX
X
x X
Xx X
Xx X
X X
X X
X
X X
X
Xx X
X
X
X
X
X X
Xx
X
X
X
XX
X
Australian Entomologist, 2006, 33 (1)
Species
Euploea darchia darchia (W.S. Macleay)
Melanitis leda bankia (Fabricius)
Mycalesis sirius sirius (Fabricius)
Mycalesis perseus perseus (Fabricius)
Hypocysta adiante antirius Butler
Ypthima arctous arctous (Fabricius)
Polyura sempronius sempronius (Fabricius)
Hypolimnas bolina nerina (Fabricius)
Hypolimnas misippus (Linnaeus)
Hypolimnas alimena darwinensis
Waterhouse & Lyell]
Junonia hedonia zelima (Fabricius)
Junonia villida calybe (Godart)
Junonia orithya albicincta Butler
Cethosia penthesilea paksha Fruhstorfer
Phalanta phalantha araca (Waterhouse &
Lyell)
Acraea andromacha andromacha
(Fabricius)
Libythea geoffroy genia Waterhouse
LYCAENIDAE
Liphyra brassolis major Rothschild
Hypochrysops ignitus erythrinus
(Waterhouse & Lyell)
Hypochrysops apelles apelles (Fabricius)
Arhopala centaurus asopus Waterhouse &
Lyell
Arhopala micale amydon Waterhouse
Ogyris zosine typhon Waterhouse & Lyell
Ogyris amaryllis hewitsoni (Waterhouse)
Hypolycaena phorbas ingura Tindale
Deudorix smilis dalyensis (Le Souéf &
Tindale)
Anthene seltuttus affinis (Waterhouse &
R.E. Turner)
Anthene lycaenoides godeffroyi (Semper)
Candalides gilberti Waterhouse
Candalides erinus erinus (Fabricius)
Nesolycaena urumelia (Tindale)
Localities
(see Table 1)
5,11,21,22,23,
30
1,5,6
l
11,22,23
5,19,29
29,30
1,27,28
1,11,20,21,22,
27,30,31,32
20,21,27,30
1,11,22,30
11,30
11,30,31
11,30,31
11,30,32
11,21,22,27,31
11,28,32
31
6,18,27,31
27,28
23,32
28
8,10,11,13,14
9,16
12,32
1,20,21,28,30,
32
11,21,22,23
1,10,13
1,5,11,20,22,23,
32
1,6,8,9,10,13,
14,16,31
21,28,29,30
13
Months collected / emerged
JFMAMJJASOND
X X
~ KK MK
~*
X
XX
XXX
x x x x
14 Australian Entomologist, 2006, 33 (1)
Species Localities Months collected / emerged
(see Table 1) JFMAMJJASOND
Prosotas dubiosa dubiosa (Semper) 11,30,32 XxxX Xx
Catopyrops florinda estrella (Waterhouse & 1,11 Xx x
Lyell)
Theclinisthes miskini miskini (T.P. Lucas) 11,18,26,29,30 XXXX x
Theclinisthes sulpitius (Miskin) 24,30 x <a X
Jamides phaseli (Mathew) 13 xx
Catochrysops panormus platissa (Herrich- 18,30 X
Scháffer)
Lampides boeticus (Linnaeus) 27 x
Zizeeria karsandra (Moore) 22,30 Xx x X
Zizina labradus labradus (Godart) 28 x
Famegana alsulus alsulus (Herrich- 21,30 XN
Scháffer)
Zizula hylax attenuata (T.P. Lucas) 5 X XX
Euchrysops cnejus cnidus Waterhouse & 1,11 Xx
Lyell
Freyeria putli putli (Kollar) 27 X
Additional literature records
HESPERIIDAE
Proeidosa polysema (Lower)
Lower (1911) first recorded this species (as Anisynta polysema) from Port
Darwin, based on a single male collected by F.P. Dodd in February 1909.
Dodd and his son Walter were based in Port Darwin for 10 months from
August 1908, exploring the East Point rainforest north to Rapid Creek
(Monteith 1991). Waterhouse and Lyell (1914) recorded the holotype female
from Petford near Chillagoe, Queensland, taken in February, and two males
from Port Darwin. They incorrectly listed January, February and March as
the months of capture for the two Port Darwin males. Waterhouse (1933)
recorded an allotype male from Port Darwin, collected in February 1909, in
the South Australian Museum, Adelaide, a paratype male from Port Darwin,
collected in February 1909, in the Australian Museum, Sydney and other
males from Port Darwin, collected in January and March, plus a female
collected in April. Subsequent authors (Common and Waterhouse 1972,
1981, Dunn and Dunn 1991, Braby 2000) have continued to refer to the Port
Darwin records in the distribution of this butterfly in the Northern Territory.
The larvae of this species feed on Triodia spp. (Poaceae), generally found
growing on rocky sandstone outcrops and slopes. Triodia records for the
Darwin region are sketchy but there have been records from Casuarina Beach
(Darwin Herbarium). It is not known whether the 7riodia was of the coastal
dunes variety or those found in the more arid regions. We have collected this
butterfly from the sandstone escarpment country behind a radio repeater
Australian Entomologist, 2006, 33 (1) 15
station, 15 km south of the Adelaide River township, along the old Stuart
Highway. Further data are required to determine whether it exists in the
Darwin region. We believe it is unlikely that it will be encountered there in
the future, due to a lack of suitable habitat.
Taractrocera ilia ilia Waterhouse
Waterhouse (1932a) described this species (as Taractrocera udraka ilia)
from four males and two females from the King River, one male from Port
Darwin in the South Australian Museum and a female from Melville Island.
Waterhouse (1932a) noted that the Port Darwin specimen was collected in
November and bore a label in Lower's handwriting ‘T. flavogattata Plótz
male’. Waterhouse (1932b), Common and Waterhouse (1972, 1981), Dunn
and Dunn (1991) and Braby (2000) all listed Darwin in the distribution of this
butterfly. We are not aware of any records of this butterfly from Darwin other
than the original male referred to by Waterhouse (1932a). Most records for
this butterfly appear to be from the King River eastwards into Arnhem Land
and we have found it to be common locally at Little Nourlangie Rock,
Kakadu National Park. Further data are required to determine whether it
exists in the Darwin region. We believe it is unlikely that it will be
encountered there in the future, due to a lack of suitable habitat.
Oriens augustulus (Herrich-Scháffer)
Evans (1949) recorded a single male, labelled Port Darwin, in The Natural
History Museum (BMNH), London. This butterfly is native to Fiji. Common
and Waterhouse (1981) questioned the natural occurrence of the butterfly in
Australia and Braby (2000) noted that it might have been introduced
accidentally, as there are no recent records to support its establishment in
Australia. Edwards et al. (2001) stated ‘it was probably not permanently
established in Australia’. Further data are required to determine whether it
exists in the Darwin region. We believe it is unlikely that it will be
encountered there in the future and is probably a locality label error.
Telicota ancilla baudina Evans
Lower (1911) recorded this species from Sydney to Port Darwin. Evans
(1949) included three males and one female from Port Darwin in his
description of the subspecies. Braby (2000) noted that a female collected by
Dunn in 1979, from Lameroo Beach (Dunn and Dunn 1991), is actually
Telicota augias (Linnaeus). We are unaware of any further records of this
butterfly from Darwin. In July 2004, we found three larvae of what we
believe to be this butterfly feeding on /mperata sp. (Poaceae), a known food
plant, at Robin Falls on the old highway south of the Adelaide River
township. Unfortunately, we were unsuccessful in rearing them to adults. The
larvae closely resembled those T. ancilla ancilla (Herrich-Scháffer) from the
east coast. Further data are required to confirm its existence in the Darwin
region.
16 Australian Entomologist, 2006, 33 (1)
Telicota mesoptis mesoptis Lower
Peters (1969) recorded a single male, labelled Port Darwin, NT, 24.xi.1902,
G. Turner, in the Australian Museum, Sydney. This is the only known record
of this butterfly from the Northern Territory and Braby (2000) noted that
further surveys were required to determine whether it exists in the Northern
Territory. We believe it is unlikely that it will be encountered in the Darwin
region in the future and is probably a locality label error.
Borbo cinnara (Wallace)
Angel (1951) first recorded collecting specimens of this butterfly at Adelaide
River, Darwin and Berry Springs, where it was supposedly more plentiful
than Borbo impar lavinia, during a collecting trip that he and F.E. Parsons
undertook during April and May 1948. Couchman (1951) provided
comments on the specimens collected by Angel and Parsons during this trip
and noted that a single male had been collected at Darwin on 7 May 1948.
Dunn and Dunn (1991) incorrectly referred the Darwin record to Couchman,
assigning only the Adelaide River records to Angel. Braby (2000) assigned
all records to Angel and noted that very few records were known. Braby
(2000) suggested that the butterfly may have been overlooked because of its
superficial resemblance to the more common Pelopidas Walker species.
Further data are required to confirm its existence in the Darwin region.
Pseudoborbo bevani (Moore)
Waterhouse (1932a) first recorded this species from Australia (as Baoris
bevani) based on three undated specimens in the South Australian Museum,
labelled Port Darwin. These three specimens are the only records from
Australia (Braby 2000). Waterhouse (1932a, 1937) believed the species may
have been introduced, as its larvae feed on rice. Experimental rice crops have
been grown in the Darwin region from as early as 1879 and, more recently,
Territory Rice Ltd operated on the Adelaide River flood plains from 1952 to
1960, when operations were abandoned (Powell 2000). Systematic searching
over the years by the present authors around the old Adelaide River rice
project areas at Tortilla Flats, Harrison Dam and Fogg Dam failed to turn up
any specimens. Further data are required to determine whether it exists in the
Darwin region.
Pelopidas agna dingo Evans
Angel (1951) recorded specimens from Darwin and Berry Springs during the
first week of May 1948 and noted that it was only seen occasionally.
Couchman (1951) provided comments on the specimens collected by Angel
and Parsons during this trip and noted that the single male collected by them
on 7 May 1948 was the first to be recorded from Darwin. Dunn and Dunn
(1991) recorded specimens in the Museum of Victoria, Melbourne and the
Australian National Insect Collection (ANIC), Canberra; however, they noted
that most records were based on females. A female collected by E.D.
Edwards from Holmes Jungle on 15 May 1973, in the ANIC, would appear to
Australian Entomologist, 2006, 33 (1) 17
be this species since it agrees with the description provided by Braby (2000)
on how to separate females of P. /yelli lyelli from those of P. agna dingo. We
have numerous females of Pelopidas spp. and many are difficult to separate.
Further data are required to confirm its existence in the Darwin region.
PAPILIONIDAE
Papilio aegeus aegeus Donovan
Dunn and Dunn (1991) first recorded this species from Darwin based on a
specimen in the J.T. St Leger Moss collection and they were followed by
Braby (2000). The Darwin record is probably the result of the nursery trade,
as it would appear that the butterfly has not established itself in Darwin
despite the abundance of citrus host plants. Further data are required to
determine whether it still exists in the Darwin region.
PIERIDAE
Catopsila pyranthe crokera (W.S. Macleay)
Braby (2000) attributed the Darwin record for this species to T.L. Fenner;
however, this record is in error (T.L. Fenner pers. comm.). Adults may be
encountered in Darwin in the future during irregular seasonal migrations but
little is known of the butterfly's behaviour in the northern areas of its
distribution (Braby 2000). Further data are required to determine whether it
currently exists in the Darwin region.
Eurema brigitta australis (Wallace)
Waterhouse and Lyell (1914) first recorded this species (as Terias libythea
zoraide Felder) from Darwin, with specimens collected in February and
March (presumed to be F.P. Dodd specimens). Dunn and Dunn (1991) noted
no other records and Braby (2000) also made reference to Darwin within the
butterfly's distribution. Further data are required to confirm its existence in
the Darwin region.
Eurema smilax smilax (Donovan)
Waterhouse and Lyell (1914) first recorded this species (as Terias smilax)
from Darwin, with specimens collected in March. Subsequent authors
(Common and Waterhouse 1972, 1981, Dunn and Dunn 1991, Braby 2000)
all detailed an Australia-wide distribution, although none specifically referred
to Darwin. There is a single male in the ANIC, Canberra, from Darwin
collected on 5 May 1948, originally from the F.E. Parsons collection. The
butterfly is known to be an opportunistic migrant (Braby 2000) and it might
be encountered in the Darwin region in the future; however, further data are
required to determine whether it currently exists there.
Eurema herla (W.S. Macleay)
Peters (1969) first recorded this species from Port Darwin from four males
and two females dated 16.ii.-19.iii.1909, plus three undated males all
collected by F.P. Dodd. These specimens are in the Australian Museum,
18 Australian Entomologist, 2006, 33 (1)
Sydney. We have collected this butterfly from Marrakai Road, approximately
70 km south of Darwin. Further data are required to confirm its existence in
the Darwin region.
Appias albina albina (Boisduval)
Waterhouse and Lyell (1914) first recorded this species from Darwin in
March. Subsequent authors (Waterhouse 1932b, Common and Waterhouse
1972, 1981, Dunn and Dunn 1991, Braby 2000) all included Darwin within
the butterfly’s distribution. There is a single female in the ANIC, Canberra,
collected in January 1977 by Gary Fitt. Recently, a single male was collected
from East Point Reserve on 3 March 2000 (C.G. Miller pers. comm.), flying
with Appias paulina ega and Cepora perimale scyllara. Braby (2000)
suggested that populations of this butterfly may be resident in Darwin but
further data are required to determine whether or not this is the case.
NYMPHALIDAE
Danaus genutia alexis (Waterhouse & Lyell)
Waterhouse and Lyell (1914) first recorded this species from Derby, Western
Australia and Darwin (as Danaida plexippus alexis) from four males and
three females. The Darwin specimens were collected in January and February
(presumed to be F.P. Dodd specimens). Subsequent authors (Waterhouse
1932b, Common and Waterhouse 1972, 1981, Dunn and Dunn 1991, Braby
2000) also list Darwin in the distribution of this butterfly. We have collected
it from Fog Bay on the Cox Peninsula and from Oolloo Crossing on the Daly
River, where adults have been observed using the river as a flight corridor
and pausing to feed at flowers along the river bank (Meyer 1995). Further
data are required to confirm its existence in the Darwin region.
Hypolimnas anomala albula (Wallace)
Waterhouse and Lyell (1914) first recorded this species (as H. antilope
albula) from Darwin from a single male collected in March. Subsequent
authors (Waterhouse 1932b, Common and Waterhouse 1972, 1981, Dunn and
Dunn 1991, Braby 2000) also referred to this record. Dunn and Dunn (1991)
recorded three specimens from the Arnhem phytogeographic region in
March. Braby (2000) noted that that the original specimen was taken in 1909,
probably by F.P. Dodd, although Braby (2000) did not mention the collector.
Braby (2000) also recorded another male collected by C.G. Miller at East
Point Reserve on 10 February 1987, flying around a track through the vine
forest (C.G. Miller pers. comm.). Further data are required to confirm its
existence within the Darwin region.
Yoma sabina parva (Butler)
Waterhouse and Lyell (1914) first recorded this species from Darwin in
March, probably collected by F.P. Dodd in 1909. We are unaware of any
further records of this butterfly from Darwin and further data are required to
confirm its existence in the Darwin region.
Australian Entomologist, 2006, 33 (1) 19
LYCAENIDAE
Ogyris iphis doddi (Waterhouse & Lyell)
Waterhouse and Lyell (1914) first recorded this species from Darwin from
two males and two females, collected in September and November,
presumably by F.P. Dodd in 1908. Dunn and Dunn (1991) recorded seven
specimens from the Arnhem phytogeographic region taken in September,
November and February (presumed also to be the original F.P. Dodd
specimens). Braby (2000) noted that the butterfly had not been collected from
Darwin since 1909, although an adult resembling this species was observed
hill-topping in March 1992 on Bens Hill behind the Trade Development Zone
(S.S. Brown pers. comm.). The last known record from the Northern
Territory is a single female, taken at light (E.D. Edwards pers. comm.) during
Operation Raleigh, from Pularumpi, Melville Island (11°4'S, 130°25'E) on 30
June 1986. The specimen is in the Northern Territory Museum collection and
Braby (2000) attributed this record to P. Homer [actually P. Horner]. Despite
extensive searching, we have not located any breeding colonies. Further data
are required to confirm its existence in the Darwin region.
Deudorix diovis Hewitson
Dunn and Dunn (1991) first recorded this butterfly from Darwin from a
single undated female collected by W. Graham. Braby (2000) also referred to
the Dunn and Dunn (1991) record. The specimen was a female collected on
the Darwin esplanade, flying in the company of Hypolycaena phorbas ingura
on 25 May 1983 (W. Graham pers. comm.). It is probable that this butterfly
occurs naturally in Darwin but has been overlooked in the past, as one of the
known food plants, Cupaniopsis anarcardioides (Sapindaceae), grows
prevalently along the esplanade. Further data are required to confirm its
existence in the Darwin region.
Nacaduba kurava felsina Waterhouse & Lyell
Waterhouse and Lyell (1914) first recorded this species from Port Darwin (as
Nacaduba perusia felsina) from three males and five females, collected in
January, February, September and November (presumed to be the original
F.P. Dodd specimens). Dunn and Dunn (1991) also included Darwin in the
butterfly’s records, based on specimens in the Museum of Victoria. We are
unaware of any recent records from Darwin; however, it is quite possible that
suitable habitat supporting the food plant Embelia curvinervia (Myrsinaceae)
(Meyer 1996a, 1996b) still exists. We have collected and reared this butterfly
from Marrakai Road, approximately 70 km south of Darwin, from Oolloo
Crossing on the Daly River and from adjacent to the Adelaide River bridge
on the Daly River Road. Further data are required to confirm its existence in
the Darwin region.
Nacaduba biocellata biocellata (C. & R. Felder)
Common and Waterhouse (1981) first recorded this species from Darwin,
attributing the record to K.L. Dunn. Dunn and Dunn (1991) and Braby (2000)
20 Australian Entomologist, 2006, 33 (1)
did not specifically list Darwin but gave an Australia-wide distribution for the
butterfly. Further data are required to confirm its existence in the Darwin
region.
Theclinesthes onycha capricornia Sibatani & Grund
Waterhouse and Lyell (1914) first recorded this species from Darwin (as
Theclinesthes onycha onycha Hewitson) from specimens collected in August,
September and October. Sibatani and Grund (1978) determined that in fact
only one male from Port Darwin, collected by F.P. Dodd, belonged to this
species, with the remaining records belonging to T. miskini miskini (T.P.
Lucas). Common and Waterhouse (1981), Dunn and Dunn (1991) and Braby
(2000) all referred to this single record. Larvae of this butterfly feed on the
soft new growth of Cycas sp. (Cycadaceae) and Macrozamia sp. (Zamiaceae)
(Braby 2000). Cycas armstrongii and Cycas calcicola both occur in the
Darwin region (Brock 1993) and may prove to be the food plant near Darwin.
Further data are required to confirm its existence in the Darwin region.
Sahulana scintillata (T.P. Lucas)
Waterhouse and Lyell (1914) first recorded this species from Darwin (as
Theclinesthes scintillata Lucas) from specimens collected in September.
Dunn and Dunn (1991) also recorded it from Darwin in September, based on
two specimens in the Museum of Victoria, Melbourne (assumed to be
original F.P. Dodd specimens), and noted that the underside markings of the
females from Darwin are more contrasting than in females from Queensland
or New South Wales. On 16 June 2003, four specimens were collected flying
around the tops of trees adjacent to mangroves at Buffalo Creek (12.3528,
130.035E) (S.J. Johnson pers. comm.). It has also been collected at
Melaleuca sp. (Myrtaceae) blossom in reasonable numbers from the Hunting
Reserve, 10 km east of the Adelaide River bridge, and from adjacent to the
Mary River bridge, both on the Arnhem Highway, in June 1994 by R.
Stoodley, T. Woodger and J. O'Dell (R. Stoodley pers. comm.). Further data
are required to confirm its existence in the Darwin region.
Everes lacturnus australis Couchman
Nowhere in the literature is this butterfly specifically recorded from Darwin,
although the distribution maps contained in Common and Waterhouse (1972,
1981) and Braby (2000) encompass Darwin. We are not aware of any current
or previous records of this butterfly from the Darwin region. We have
collected it from Marrakai Road, approximately 70 km south of Darwin.
Further data are required to confirm its existence in the Darwin region.
Summary
One hundred and eleven butterfly species have been recorded from the
Darwin region to date, representing approximately 2596 of Australia's known
butterfly species. The present authors have recorded 87 of the 111 recorded
species from the Darwin region since 1990. We believe it is unlikely that
Australian Entomologist, 2006, 33 (1) 21
Proeidosa polysema and Taractrocera ilia will be encountered in the Darwin
region in the future, due to loss of suitable habitat. We also believe that the
records of Oriens augustulus and Telicota mesoptis mesoptis are probably the
result of incorrect labelling by their collectors. Further data are required to
confirm the existence of the remaining 20 species recorded previously in the
literature. In time, some of these records may also prove to be labelling
errors, as some of the early butterfly workers, including F.P. Dodd, have been
known to err with their label data. It is hoped that the data presented in this
paper will help stimulate future butterfly workers in determining the
existence or otherwise of the remaining 20 species in the Darwin region.
Acknowledgements
We would like to thank Bill Graham, Steve Brown, Russell Stoodley, Grant
Miller and Steve Johnson for the inclusion of their specimen data and Ted
Edwards for the loan of literature and for his constructive comments on a
draft of this paper.
References
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descriptions of new species. Transactions of the Royal Society of South Australia 74: 6-14, pl. 1.
BRABY, M.F. 2000. Butterflies of Australia: their identification, biology and distribution.
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BROCK, J. 1993. Native plants of northern Australia. Reed, Chatswood; xii + 355 pp.
COMMON, I.F.B. and WATERHOUSE, D.F. 1972. Butterflies of Australia. Angus and
Robertson, Sydney; xii + 498 pp, 41 pls.
COMMON, I.F.B. and WATERHOUSE, D.F. 1981. Butterflies of Australia. 2nd ed. Angus and
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Northern Territory. Transactions of the Royal Society of South Australia 74: 15-17, pl. 1, figs 5-
6.
DUNN, K.L. and DUNN, L.E. 1991. Review of Australian butterflies: distribution, life history
and taxonomy. Parts 1-4. Privately published by the authors, Melbourne; 660 pp.
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pls.
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Society of South Australia 32: 311-317.
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of South Australia 35: 112-172.
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(Lepidoptera: Nymphalidae: Danainae). Australian Entomologist 22: 137-139.
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Lyell (Lepidoptera: Lycaenidae). Australian Entomologist 23: 73-74.
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Australian Entomologist, 2006, 33 (1): 23-25 23
RE-COLLECTION AND TENTATIVE HOST RECORD FOR AYGIA
(AUSTRALOCOLPURA) SANDARACINE BRAILOVSKY
(HEMIPTERA: COREIDAE: COLPURINI)
MARTIN J. STEINBAUER
University of Tasmania, CRC for Sustainable Production Forestry, c/- CSIRO Entomology,
GPO Box 1700, Canberra, ACT 2601
Address for correspondence: Australian Plague Locust Commission, Australian Government —
Department of Agriculture, Fisheries and Forestry, GPO Box 858, Canberra, ACT 2601
(email: martin.steinbauer@daff.gov.au)
Abstract
A second collection at the original type locality of the rare Australian colpurine coreid Hygia
(Australocolpura) sandaracine Brailovsky is recorded, with an apparent feeding record on the
tree fern Dicksonia antarctica Labill. (Dicksoniaceae).
Introduction
The coreid tribe Colpurini contains 21 species in Australia (Brailovsky 2001,
Cassis and Gross 2002). Little is recorded of their biology although
Brailovsky (1993) described them as ‘typically species of the rainforest’.
Collection records indicate that most colpurines are taken on the ground and
among leaf litter. The only references to their food plants in Australia are
those by Kumar (1966), who recorded Pachycolpura manca Breddin on
Urtica, Coreopsis, tomato and pumpkin, and Steinbauer and Clarke (1996),
who noted a possible association between Acantholybas kirkaldyi Bergroth
and Eucalyptus. In New Zealand, the introduced Australian species
Acantholybas brunneus (Breddin) feeds on a wide variety of plants,
summarised by Steinbauer and Clarke (1996). Extralimital host records on
cacao and taro in New Guinea for the Australian species Agathyrna
praecellens Stal were summarised by Cassis and Gross (2002).
Hygia (Australocolpura) sandaracine Brailovsky was described from a single
collection of two specimens in New England National Park, northern New
South Wales (Brailovsky 1993). This paper documents a re-collection of the
species and a possible food plant.
Observations
On January 1, 2004, a group of 10-15 individuals (including 3 pairs in cop.)
and 5-10 nymphs (of early to late instar) of H. sandaracine were observed on
fronds of the soft tree fern Dicksonia antarctica Labill. (Dicksoniaceae), on
the Lyrebird Walk in New England National Park. At this point the track
passes through ‘myrtle forest (temperate rainforest with Nothofagus
cunninghamii (Hook.) Oerst.) at about 1300-1400 m altitude at the base of
the eastern escarpment cliffs. A few individuals were observed with their
rostra touching the central leader of the frond, apparently feeding. Five males
and two females (Fig. 1) were collected for identification and have been
deposited in the Australian National Insect Collection (ANIC), Canberra.
24 Australian Entomologist, 2006, 33 (1)
When handled, they released a pungent, ester-smelling odour, similar to that
of other coreids (Steinbauer and Davies 1995).
Discussion
Records of heteropterans feeding on ferns are rare. The only member of the
Pentatomomorpha recorded in Australia on ferns, in the summary by Cassis
and Gross (2002), is the highly polyphagous rhyparochromid Remaudiereana
inornata (Walker). Only gymnosperms and angiosperms were listed for
world Coreidae (including only one Colpurini) by Schaefer and Mitchell
(1983). No lower vascular plants were listed for Coreidae in a review of
economically important species (Mitchell 2000). Schaefer (1965) regarded
the Colpurini as ‘primitive’ within the Coreidae. If H. sandaracine can be
shown to be monophagous on ferns it would support this view. However, this
may be unlikely in view of the wide range of plants used by Acantholybas
brunneus in New Zealand (see above). Clearly, more information on the host
plants of native Australian Coreidae is required.
Fig. 1. Hygia (Australocolpura) sandaracine Brailovsky. (A-B) dorsal and lateral
views of adult female, (C-D) dorsal and lateral views of adult male. Scale bar = 5 mm.
Australian Entomologist, 2006, 33 (1) 25
Acknowledgements
I thank Ben Boyd (ANIC, Canberra) for Fig. 1, Tony Prior (NSW National
Parks and Wildlife Service, Dorrigo) for assistance in determining the
identity of the host plant, Tom Weir (ANIC, Canberra) for confirmation of
the initial species determination and an anonymous reviewer for beneficial
revisions to the text.
References
BRAILOVSKY, H. 1993. A revision of the tribe Colpurini from Australia (Hemiptera-
Heteroptera-Coreidae). Memoirs of the Queensland Museum 34: 35-60.
BRAILOVSKY, H. 2001. A further contribution to the Australian systematics of the tribe
Colpurini (Hemiptera: Heteroptera: Coreidae: Coreinae). Pan-Pacific Entomologist 77: 79-89.
CASSIS, G. and GROSS, G.F. 2002. Hemiptera: Heteroptera (Pentatomomorpha). In Houston,
W.W.K. and Wells, A. (eds), Zoological Catalogue of Australia. Vol. 27.3B. CSIRO Publishing,
Melbourne; xiv + 737 pp.
KUMAR, R. 1966. Studies on the biology, immature stages, and relative growth of some
Australian bugs of the superfamily Coreoidea (Hemiptera: Heteroptera). Australian Journal of
Zoology 14: 895-991.
MITCHELL, P.L. 2000. Leaf-footed bugs (Coreidae). Pp 337-403, in: Schaefer, C.W. and
Panizzi, A.R. (eds), Heteroptera of economic importance. CRC Press, Boca Raton; 828 pp.
SCHAEFER, C.W. 1965. The morphology and higher classification of the Coreoidea
(Hemiptera-Heteroptera). Part II. The families Rhopalidae, Alydidae, and Coreidae.
Miscellaneous Publications of the Entomological Society of America 5: 1-76.
SCHAEFER, C.W. and MITCHELL, P.L. 1983. Food plants of the Coreoidea (Hemiptera:
Heteroptera), Annals of the Entomological Society of America 76: 591-615.
STEINBAUER, M.J. and CLARKE, A.R. 1996. Revision of the genus Acantholybas Breddin
(Hemiptera: Coreidae). Annals of the Entomological Society of America 89: 519-525.
STEINBAUER, M.J. and DAVIES, N.W. 1995. The defensive secretions of Amorbus
obscuricornis (Westwood), A. rubiginosus (Guérin-Méneville) and Gelonus tasmanicus (Le
Guillou) (Hemiptera: Coreidae). Journal of the Australian Entomological Society 34: 75-78.
26 Australian Entomologist, 2006, 33 (1)
BIRNA, ANEW NAME FOR LINEA McDONALD
(HEMIPTERA: PENTATOMIDAE)
F.J.D. MCDONALD
Faculty of Agriculture, Food and Natural Resources, University of Sydney, NSW 2006
Abstract
Birna nom. n. is proposed as a replacement name for the genus Linea McDonald, 2003,
preoccupied by Linea Schroder, Medioli & Scott, 1989. Birna griggae (McDonald), comb. n., is
transferred from Linea McDonald.
Introduction
McDonald (2003) proposed the name Linea McDonald for a new genus of
Pentatomidae (Hemiptera) from northern Australia. This name is preoccupied
in the Foraminifera (Schroder et al. 1989) and a replacement name is
provided below.
Birna nom. n.
Linea McDonald, 2003: 17. Not Linea Schroder, Medioli & Scott, 1989.
Type species (automatic): Linea griggae McDonald.
Etymology. Birna is the word for bug in the Yindjibarndi language spoken by
the indigenous people of the Pilbara region in Western Australia. The gender
is to be taken as feminine.
Birna griggae (McDonald), comb. n.
Linea griggae McDonald, 2003: 19.
Description. See McDonald (2003).
Acknowledgements
I should like to thank David Rider (North Dakota State University and the
Zoological Record) for alerting me to the homonymy of Linea McDonald. I
should also like to thank David McAlpine (Australian Museum, Sydney) for
his help in correctly formatting this paper.
References
McDONALD, F.J.D. 2003. A new genus and species of Pentatomidae (Hemiptera: Heteroptera)
from northern Australia. Australian Entomologist 30(1): 17-20.
SCHRODER, C.J., MEDIOLI, F.S. and SCOTT, D.B. 1989. Fragile abyssal Foraminifera
(including new Komokiacea) from the Nares abyssal plain. Micropaleontology (New York)
35(1): 10-48.
Australian Entomologist, 2006, 33 (1): 27-30 27
THE RETURN MIGRATION OF BOGONG MOTHS, AGROTIS
INFUSA (BOISDUVAL) (LEPIDOPTERA: NOCTUIDAE), FROM
THE SNOWY MOUNTAINS, NEW SOUTH WALES
KEN GREEN
Snowy Mountains Region, NPWS, PO Box 2228, Jindabyne, NSW 2627
(email: ken.green@environment.nsw.gov.au)
Abstract
The return (autumnal) migration of Agrotis infusa (Boisduval) from the Snowy Mountains
commences after most plants have finished flowering, and the return journey to the plains to
breed is generally against the general direction of the wind. At the commencement of these
flights, bogong moths were recorded flying into the wind, which was a head wind at all altitudes
up to 4000 m, and were observed feeding on honeydew.
Introduction
The bogong moth, Agrotis infusa (Boisduval), has a mixed biology. In some
populations there are spring and autumn generations and no migration. Other
populations are univoltine, with adults emerging in spring and migrating up
to 1000 km from the western slopes and plains of New South Wales and
southern Queensland, to aestivate in rock crevices in the mountains on and
adjacent to the Great Dividing Range (Common 1954). The spring migration
has been well documented (Common 1954), but post-diapause migrations of
insects are generally not as obvious nor as well described as pre-diapause
flights, because there are fewer insects involved and the migration flight is
thought to be more scattered (Johnson 1969).
During the spring migration, bogong moths have been reported feeding on a
number of plants, such as forest and orchard trees, garden flowers and shrubs
(McCarthy 1945) and nectar of eucalypt and other flowers (Common 1981).
Common (1981) reported bogong moths ‘migrating back to their breeding
areas, where nectar is again sought before mating’ but did not comment on
the food used during the actual migration. Moths must make the return
migration at a time in autumn when temperatures are low, winds are
generally not favourable, most plants have finished flowering, and the moth’s
body fat is depleted. In these conditions, the food that provides fuel for the
return migration is crucial but has not as yet been documented.
Results and discussion
On 10 April 2005, at about 1800 h on an island in Valentines Creek at 1800
m asl, SSE of Mt Jagungal (36°08.5’S, 148°23.2E), I observed fast-flying
moths moving unidirectionally northward to where the sky was still light just
after sunset; there was no moon. The direction of flight was almost exactly
northerly, just off the wind which was from the NNW averaging 8 km/hr and
peaking at 14.5 km/hr during observations with a hand-held weather station
(Kestrel 3000). The temperature was 14.5°C, in humid conditions leading to a
thunderstorm within an hour of the observations.
28 Australian Entomologist, 2006, 33 (1)
Looking south, where it was almost dark, and without moving my head, I
counted all fast-flying moths passing my vision until 200 had passed. This
took 3.5 minutes, which equals 57 moths per minute. The angle of view was
small and unquantifiable. Common (1954) used a vertical light beam to count
return migration of bogong moths from Mt Gingera and, on 11 April 1952,
counted 13-27 per minute at 2-5 m off the ground, which was the
approximate height of the flight I observed. Moths were flying fast into a
wind that was coming up-valley from the NNW.
There are two distinct ways in which moths migrate. In the first, they may
ascend to considerable altitude in rising, warm air and be transported
downwind (Drake and Farrow 1988, Gatehouse 1997). In this type of
migration the moths cannot feed, have little control over their ultimate
destination and may travel great distances in a short time. Alternatively, the
moths remain close to the ground (in the boundary layer) and control the
direction in which they fly, often having to fly upwind (Johnson 1969). They
are able to feed during the migration, may take much longer to travel long
distances and may arrive at a definite destination.
Moths migrating close to the ground may be caught in updrafts and taken
downwind for great distances, particularly in spring when winds are more
violent. Bogong moths trapped like this may reach New Zealand (Common
1981). Captures of moths in northern NSW suggest downwind movement in
the geostrophic layer (Gregg et al. 1994). In nearly all autumnal records by
Common (1954), the wind at ground level was either a cross wind or a head
wind, as in the present observations where moths were flying fast into a
gentle breeze. There were no favourable winds at higher altitudes. Bureau of
Meteorology recordings from Canberra Airport (120 km to the north),
throughout the day and into the evening of 10 April 2005, showed
consistently NW to N winds at all altitudes up to above 4000 m (15000 feet),
moderáting from 100 km/hr in the morning to 40 km/hr in the evening
(Bureau of Meteorology, pers. comm.).
There has been much research into the assistance that wind gives to migrating
insects (Drake and Farrow 1988, Gregg et al. 1994), with the implication that
bogong moths are just passengers on the wind. However, to be able to locate
the same mountain tops for aestivation suggests some control over the
direction taken by the moths, as does the ability to migrate back to natal sites
against generally unfavourable wind conditions. In these unassisted
conditions, autumnal migration would be energetically more expensive, with
access to food critical for moths that are returning to breed.
After counting the moths, the shrubs on the island were examined. This
revealed thousands of bogong moths, with up to 50 moths on a single shrub.
Shrubs containing moths were both epacrids: Epacris microphylla s.l. and E.
paludosa. Other shrubs in the vicinity, viz. Kunzea muelleri, Olearia algida,
Australian Entomologist, 2006, 33 (1) 29
Grevillea australis, Nematolepis (Phebalium) ovatifolium and the heath
Richea continentis, had no moths.
Several plants of the two Epacris species were examined; only FE.
microphylla that had lerps (Homoptera: Psyllidae) had any moths on them,
whereas all E. paludosa had lerps and all also had bogong moths. The moths
were examined closely by headlamp; all had their proboscides extended and
appeared to be feeding. Feeding on the sugary exudate (honeydew) of lerp-
forming bugs has been recorded for noctuids (Common 1990), but this is the
first record for bogong moths (Ted Edwards pers. comm.). Epacris paludosa
grew mainly along the rocky banks of Valentines Creek but no moths were
observed drinking in the creek.
Light traps set for five years on Point Lookout (1560 m) in northern NSW,
about 50 km inland from Coffs Harbour, showed spring numbers of bogong
moths (going south) peaking in October or November, with the return
migration peak in February/March and a decrease in numbers in April (Gregg
et al. 1993). The migration recorded in the present study was past the peak
recorded by Gregg et al. (1993), but the timing was not particularly late.
Although return migration to the natal grounds commences in about March
(Common 1954), Green (2003) recorded bogong moths in the mountains,
sunning themselves on rocks in May, and bogong moth remains in fox scats
in June. Presumably, there is a balance of advantages and disadvantages in
the timing of the return migration; the later the migration the greater the
chance of autumnal rains and plant growth in the natal sites but also the
greater the lack of food for the return journey. The use of honeydew may well
alleviate this lack of flowering plants on the return migration.
Acknowledgements
I thank Ted Edwards for many discussions on bogong moths and comments
on the manuscript. Dave Woods identified some of the plants.
References
COMMON, LF.B. 1954. A study of the ecology of the adult bogong moth, Agrotis infusa
(Boisd.) (Lepidoptera: Noctuidae), with special reference to its behaviour during migration and
aestivation. Australian Journal of Zoology 2: 223-263.
COMMON, LF.B. 1981. The bogong moth. Bogong 2(6): 4-5.
COMMON, I.F.B. 1990. Moths of Australia. Melbourne University Press, Carlton; vi + 535 pp.
DRAKE, V.A. and FARROW, R.A. 1988. The influence of atmospheric structure and motions
on insect migration. Annual Review of Entomology 33: 183-210.
GATEHOUSE, A.G. 1997. Behaviour and ecological genetics of wind-borne migration by
insects. Annual Review of Entomology 42: 475-502.
GREEN, K. 2003. Altitudinal and temporal differences in the food of foxes (Vulpes vulpes) at
alpine and subalpine altitudes in the Snowy Mountains. Wildlife Research 30: 245-253.
30 Australian Entomologist, 2006, 33 (1)
GREGG, P.C., FITT, G.P., COOMBS, M. and HENDERSON, G.S. 1993. Migrating moths
(Lepidoptera) collected in tower-mounted light traps in northern New South Wales, Australia:
species composition and seasonal abundance. Bulletin of Entomological Research 83: 563-578.
GREGG, P.C., FITT, G.P., COOMBS, M. and HENDERSON, G.S. 1994. Migrating moths
collected in tower-mounted light traps in northern New South Wales, Australia: influence of
local and synoptic weather. Bulletin of Entomological Research 84: 17-30.
JOHNSON, C.G. 1969. Migration and dispersal of insects by flight. Methuen, London; xvi +
763 pp.
McCARTHY, T. 1945. The. bugong moth (Agrotis infusa) The Agricultural Gazette of New
South Wales 56: 2.
Australian Entomologist, 2006, 33 (1): 31-34 31
LIFE HISTORY NOTES ON LEUCOMONIA BETHIA (KIRBY)
(LEPIDOPTERA: SPHINGIDAE)
D.A. LANE
3 Janda St, Atherton, Qld 4883
Abstract
Notes are presented on the life history of Leucomonia bethia (Kirby). The larval food plant is
Clerodendrum floribundum R. Br. (Verbenaceae).
Introduction
Leucomonia bethia (Kirby) is the only known species within the genus
Leucomonia Rothschild & Jordan. It has a wide distribution across northern
Australia (D'Abrera 1987) but nothing has been published to date on its
biology. During January and February 2005, eggs and early instar larvae of L.
bethia were found near Granite Creek, 15 km northwest of Atherton in
northern Queensland. These were reared through to adults and the following
observations recorded.
Life history
Food plant. Clerodendrum floribundum R. Br. (Verbenaceae).
Egg (Fig. 1). Spherical; 1.5 mm in diameter; pale green; laid singly on upper
or undersurface of food plant leaf.
First instar larva (Fig. 2). Length 5-8 mm. Head, body and legs light green
(almost translucent). Caudal horn dark brown, directed backwards and
extending away from body, turned upwards slightly with extreme upper tip
bifurcate.
Second instar larva (Fig. 3). Length 8-20 mm. Body and legs light green; a
mid-lateral band, adorned with fine pale yellow spots, extends along thoracic
and abdominal segments. Head and anal claspers darker green, also adorned
with fine yellow spots. Caudal horn brown, clothed in brown setae, raised at
approximately 30° and turned upwards slightly, with extreme upper tip also
bifurcate but not as distinctly as in the first instar.
Third instar larva (Fig. 4). Length 20-32 mm. Head, body and legs green
(darker than first and second instars). Head, body and upper prolegs with
slightly raised yellow spots; seven pale yellow oblique stripes along
abdominal segments 1-8, arising anterior to and below spiracles and
terminating on dorsal surface of abdomen; posterior stripe terminating at base
of caudal horn. Caudal horn brown, nearly straight, angled at approximately
45°, with brown setae.
Fourth instar larva (Fig. 5). Length 32-55 mm. Head, body and legs green,
with slightly raised fine yellow tubercles. Thorax with legs light brown; a
series of raised green or brown tubercles on anal prolegs and on dorsal
surface of thoracic segments; lateral oblique stripes more prominent,
32 Australian Entomologist, 2006, 33 (1)
coloured yellow with upper dark green edging. Caudal horn straight, brown
with yellow underside, clothed in fine, raised tubercles. Spiracles brown, with
surrounding narrow yellow ring.
Fifth instar larva (Figs 6-8). Length 55-80 mm. Head, body and legs with
markings as in fourth instar, but larva more stocky. Green or brown tubercles
on anal prolegs prominent; yellow tubercles on body often less prominent and
in green colour form (see below) often lacking; lateral oblique stripes
coloured white with upper dark green edging. Caudal horn dark brown,
curved slightly backwards, with raised brown tubercles. Raised tubercles on
thoracic segments either green or brown. Fifth instar larvae occur in both
green (Fig. 6) and brown (Fig. 7) colour forms, with intermediate (Fig. 8)
forms occurring.
Pupa (Fig. 9). Dark brown; haustellum case well developed and about one
quarter length of pupa. Cremaster black, deeply pitted, in dorsal view nearly
an equilateral triangle, terminating in a pair of distally directed, sharp spines
about one third width of length; these spines are basally wider and angled
more obtusely away from body axis compared with those on the pupal
cremaster of Psilogramma argos Moulds & Lane. In lateral view, cremaster
sides nearly straight and parallel sided, tilting upward from body axis. Pupa
similar in overall shape and form, but much darker brown in colour, than that
of P. argos (Moulds and Lane 1999).
Observations
Larvae normally rest on the undersurface of food plant leaves and are
remarkably well camouflaged, as the combination of green colouration with
diagonal striping gives the impression of filtered sunlight. During particularly
hot days, mature larvae (especially brown colour forms) were observed at the
base of food plant trees, resting head upwards with caudal horns touching the
ground. This situation possibly afforded more shade and slightly cooler
conditions, and also may have aided camouflage.
At the time of year observed (January-February), third to fifth instar larvae
were heavily parasitised by tachinid flies, with up to 9096 mortality rate. Such
final instar larvae continued to feed, but developed slowly. Attempts at
pupation usually failed, as the limp larval body rapidly decomposed after
multiple fly larvae exited.
Before pupating, final instar larvae first turn a purplish colour, then leave the
food plant and may wander considerable distances before finding a suitable
pupation site.
Australian Entomologist, 2006, 33 (1)
33
Figs 1-9. Leucomonia bethia. (1) egg; (2) first instar larva; (3) second instar larva; (4)
third instar larva; (5) fourth instar larva; (6-8) fifth instar larvae: (6) green colour form
(note the parasitic strike marks on abdominal segment 1); (7) brown colour form; (8)
intermediate colour form; (9) pupa, lateral view.
34 Australian Entomologist, 2006, 33 (1)
In captivity, purplish coloured larvae were placed in suitable containers
containing 150 mm of bedding soil. Some burrowed immediately and others
wandered for up to several hours before burrowing to pupate. In this
situation, they constructed cells made of soil lined with silk and pupated
within these cells. Adults emerged from pupae after two to three weeks.
Acknowledgements
Thanks are extended to Garry Sankowsky (Tolga) for food plant
identifications, to Dr. M.S. Moulds (Sydney) for constructive criticism and
advice, and to the Queensland Parks and Wildlife Service for permits
allowing research within State Forest areas under their jurisdiction.
References
D'ABRERA, B. 1987. Sphingidae Mundi, hawkmoths of the world. Based on a checklist by Alan
Hayes and the collection he curated in the British Museum (Natural History). E.W. Classey,
Faringdon; ix + 226 pp.
MOULDS, M.S. and LANE, D.A. 1999. A new hawkmoth from Northern Australia with notes
on its life history (Lepidoptera: Sphingidae). Australian Entomologist 26(2): 37-44.
Australian Entomologist, 2006, 33 (1): 35-38 35
A SURVEY OF INSECT PESTS BREEDING IN MANGO FRUIT IN
DILI, EAST TIMOR
GLENN A. BELLIS!, RAFAEL FALICIANO?, AUGUSTINO ALVES’ and
MARK HEARNDEN?
! Northern Australia Quarantine Strategy, Australian Quarantine and Inspection Service, PO Box
37846, Winnellie, NT 0821 (email: glenn. bellis@aqis.gov.au)
"National University of East Timor, Dili, East Timor
"Northern Territory Department of Primary Industry, Fisheries and Mines, GPO Box 3000,
Darwin, NT 0801
Abstract
A survey of 1345 mango fruit from 231 trees in Dili detected a 9.5% prevalence of Deanolis
sublimbalis Snellen (Lepidoptera: Pyralidae) and a 14.7% prevalence of Bactrocera spp. fruit
flies (Diptera: Tephritidae). No other mango fruit borers were detected and it is very unlikely that
they occur in Dili. The absence of Sternochetus frigidis F. and S. mangiferae (F.) (Coleoptera:
Curculionidae) suggests a low probability of their presence in East Timor.
Introduction
In Southeast Asia, a number of insects have been reported breeding in mango
fruit, particularly red-banded mango caterpillar, Deanolis sublimbalis Snellen
(Lepidoptera: Pyralidae), mango pulp weevil, Sternochetus frigidis Fabricius
and mango seed weevil, Sternochetus mangiferae (Fabricius) (Coleoptera:
Curculionidae), several Bactrocera Macquart species (Diptera: Tephritidae)
and an undescribed species of Nephopteryx Hiibner (Lepidoptera: Pyralidac)
(Kalshoven 1981, Waterhouse 1993, Allwood et al. 1999, Anon 1999, Smith
1999). These pests not only affect fruit production through reduction in yields
but can also impinge on exports, since many countries impose strict
quarantine requirements on the import of fruit potentially infested with one or
more of these pests.
Deanolis sublimbalis, S. frigidis and Bactrocera spp. have been reported
from Indonesia but confirmed records from many of the individual islands in
the Indonesian archipelago, including Timor, are lacking (Kalshoven 1981,
Anon 1993, Drew and Hancock 1994). Consequently, the status of these pests
on mango fruit in East Timor, a newly independent country which lies in this
archipelago, is unclear.
Many species that breed in mango fruit are difficult to find as the only means
of detection is to sample fruit destructively. Additionally, mangoes are very
seasonal and provide only a brief window of opportunity to sample fruit. In
many areas, fallen fruit is quickly eaten by domestic animals, making large
scale sampling difficult. This paper reports the results of a recent survey for
mango fruit pests in Dili, East Timor.
Materials and methods
Mango fruit were collected from fruiting trees in backyards in Dili in
December 2003 and January 2004. In most cases, five fruit were picked from
36 Australian Entomologist, 2006, 33 (1)
each tree, although fallen fruit were also sampled opportunistically. In areas
where fruiting trees were scarce, ten fruit were sampled from each tree.
Samples from each tree were treated as a unit, so infestation levels were
calculated for individual trees rather than for individual fruits. Tree owners
were shown photographs and specimens of D. sublimbalis and Sternochetus
sp. larvae and asked if these insects ever occurred in their fruit.
Fruit maturity, as gauged by flesh colour, was recorded for each mango
sampled. Mangoes, including seeds, were dissected using a knife or secateurs
and examined for the presence of borers or borer damage. The position within
the fruit of borers or damage was recorded and all borers were collected,
immersed in freshly boiled water for 5 minutes, then preserved in 70%
ethanol for subsequent morphological examination.
The confidence level that pest specimens not detected in the samples were
absent from the sampled population, was calculated using the formula of
Cannon and Roe (1982):
DISP P PEN DA
a]
where N is the estimated population size, d is the number of positives in the
population and n is the number sampled. Confidence levels were calculated
using an upper and a lower estimate for N, the number of fruit in the Dili
growing region using a lower estimate of 90,000 (300 trees each producing
an average of 300 fruit) and an upper estimate of 200,000 (400 trees each
producing an average of 500 fruit), and d was given the value of 1. The result
is the confidence level expressed as the probability of finding less than 1
infected fruit in the sample.
Results
Ten fruits from each of 38 trees and five fruits from each of 193 trees were
sampled, giving a total of 1345 fruit from 231 trees. It was estimated that the
majority of fruiting trees in Dili were sampled. A total of 1221 fruit (90.8%)
were picked from trees, while 124 fruit (9.2%) were collected from the
ground beneath fruiting trees. Three maturity stages were represented, with
114 mature (orange flesh), 102 partially mature (yellow flesh) and 15
immature (white/pale yellow flesh) samples respectively.
Deanolis sublimbalis and tephritid fruit flies were the only primary pests
observed. Forty-eight specimens of D. sublimbalis were collected from 22
trees, indicating a prevalence of infestation of trees of 9.5%. D. sublimbalis
were only collected from picked fruit. The infestation rates relative to fruit
maturity are given in Table 1. All specimens of D. sublimbalis were found in
the seed, although damage to flesh was usually also evident.
Australian Entomologist, 2006, 33 (1) 37
Table 1. Infestation rate of Deanolis sublimbalis relative to maturity of mango fruit
examined in Dili, East Timor.
Fruit maturity % of larvae collected Infestation rate (%)
Mature 45 7.9
Partially mature 10 2.9
Immature 44 i 66.7
Fruit fly larvae (Bactrocera spp.) were present in 34 (14.7%) samples. All but
four of the samples infested by D. sublimbalis were also infested by fruit flies
and all but one of the samples infested by fruit flies were also infested by
opportunistic beetle species (adult scarabaeids and nitidulids). Tree owners
agreed that these were the only insects ever seen in the fruit.
The probability (level of confidence) that mango fruit-boring insects not
detected in the samples are absent from the Dili mango growing region was
calculated to be between 98.5% and 99.3%, depending on which estimate of
the number of fruit produced in Dili was used.
Discussion
Dili serves as a major market for fruit grown in surrounding areas of East
Timor. Consequently, pests able to be transported in infested fruit would be
expected to be continuously brought into Dili for sale and subsequently
become established there. Their absence in Dili suggests that other areas of
East Timor may also be free of such pests. This is particularly true for
Sternochetus frigidis and S. mangiferae, which can infest up to 80% of
mango fruit and do not affect the external appearance (Cunningham 1991,
Kalshoven 1981). Where these pests are present, infested fruit are likely to be
harvested and sold in the marketplace.
The presence of Deanolis sublimbalis in East Timor is not surprising. This
species has been reported from across Indonesia as far east as Papua New
Guinea (Kumar 2001). A prevalence of 9.5% is comparable with that
observed in the Philippines by Golez (1991) and probably does not impinge
significantly on mango production. Mangoes of varying states of maturity
harboured caterpillars, which agrees with the observations of Golez (1991).
The relatively higher infestation rate of immature fruit may be due to a
tendency for infested fruit to fall prematurely (Kalshoven 1981), thereby
reducing the proportion that remain on the tree until maturity.
Several species of fruit fly, e.g. Bactrocera papayae Drew & Hancock, B.
carambolae Drew & Hancock and B. albistrigata (de Meijere), which are
important pests of mangoes, are known to be present in Timor (Drew and
Hancock 1994, Allwood et al. 1999, Bellis and Brito unpublished data). No
attempt was made in this study to identify larvae collected in this study so the
actual species involved are not known. The prevalence of fruit flies in
38 Australian Entomologist, 2006, 33 (1)
mangoes may underestimate true rates as many immature fruit were sampled
and these are often less frequently attacked by fruit flies than are mature fruit.
Acknowledgements
This work was funded by the Australian Quarantine and Inspection Service.
We are grateful to Ir Flaviano Soares and Robert Williams of the National
University of East Timor for logistical support in Dili and to E.S.C. Smith
(NTDPIFM) for advice on experimental design. Jane Royer (QDPIF) and
Judy Grimshaw (AQIS) provided reference material of D. sublimbalis.
Graham Goodyer (AQIS) confirmed identifications.
References
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records for fruit flies (Diptera: Tephritidae) in South East Asia. Raffles Bulletin of Zoology
Supplement 7: 1-92.
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Inspection Service, Canberra; 26 pp.
CANNON, R.M. and ROE, R.T. 1982. Livestock disease surveys: A field manual for
veterinarians. Australian Government Publishing Service, Canberra; 35 pp.
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417.
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(Diptera, Tephritidae, Dacinae) in Asia. Bulletin of Entomological Research Supplement 2: 1-68.
GOLEZ, H.G. 1991. Bionomics and control of the mango seed borer, Noorda albizonalis
Hampson (Pyralidae, Lepidoptera). Acta Horticulturae 291: 418-424.
KALSHOVEN, L.G.E. 1981. Pests of crops in Indonesia. P.T., Ichtiar Baru, Van Hoeve,
Jakarta; 701 pp.
KUMAR, R. 2001. Insect pests of agriculture in Papua New Guinea, Part 1. Principles and
practice, pests of tree crops and stored products. Science in New Guinea, PNG; 723 pp.
SMITH, E.S.C. 1999. Report to AQIS on two visits to the Republic of the Philippines in
connection with area freedom of mango pulp and seed weevils during 1999. Unpublished report
to Australian Quarantine and Inspection Service, Canberra; 36 pp.
WATERHOUSE, D.F. 1993. The major arthropod pests and weeds of agriculture in Southeast
Asia: distribution, importance and origin. ACIAR. Monograph No. 21; 141 pp.
Australian Entomologist, 2006, 33 (1): 39-48 39
THE BUTTERFLIES (LEPIDOPTERA) OF MIDDLE, MONDRAIN,
SANDY HOOK, WOODY AND GOOSE ISLANDS IN THE
RECHERCHE ARCHIPELAGO, WESTERN AUSTRALIA
ANDREW A.E. WILLIAMS! and ROBERT J. POWELL?
! Department of Conservation and Land Management, W.A. Wildlife Research Centre,
PO Box 51, Wanneroo, WA 6065
254 Bournemouth Crescent, Wembley Downs, WA 6019
Abstract
Twelve butterfly species are recorded from Middle, Mondrain, Sandy Hook, Woody and Goose
Islands in the Recherche Archipelago, Western Australia: Hesperilla chrysotricha chrysotricha
(Meyrick & Lower), Delias aganippe (Donovan), Pieris rapae rapae (Linnaeus), Geitoneura
klugii (Guérin-Méneville), Heteronympha merope duboulayi (Butler), Junonia villida calybe
(Godart), Vanessa kershawi (McCoy), Vanessa itea (Fabricius), Nacaduba biocellata biocellata
(C. & R. Felder), Theclinesthes serpentata serpentata (Herrich-Scháffer), Neolucia agricola
occidens Waterhouse & Lyell and Zizina labradus labradus (Godart). Their status on the islands
is discussed and the butterfly fauna compared with that of other Western Australian islands.
Introduction
The islands of the Recherche Archipelago are located off the southern
coastline of Western Australia, from Esperance eastwards. About 200 islands
make up the archipelago; some lie close to the coast while others are a
considerable distance off shore. The furthest, Salisbury Island, is 50 km
southeast of the mainland at Cape Arid. In November of 1998, 1999 and
2003, we surveyed five of the larger islands for butterflies: Middle (34?06'S,
123°11’E); Mondrain (34?08'S, 122°15’E); Sandy Hook (34°02’S,
122°00’E); Woody (33°58’S, 122°01’E); and Goose (34?05'S, 123?11'E).
Prior to these visits, no butterflies had been recorded from the archipelago.
The islands are mostly granitic remnants of the Precambrian Shield (Brown et
al. 1984). Middle Island (1060 ha) is the largest and physiographically most
diverse of the islands. It lies about 8.5 km SSE of Cape Arid and 120 km ESE
of Esperance. Its topography is dominated by Flinders Peak (174 m), a large
granite dome at the western end of the island. The coastline is very irregular,
with numerous promontories and coves with white sandy beaches. In some
places limestone overlies the granite substrate. Lake Hillier, a pink,
hypersaline lake, is located in the northeast of the island. The vegetation on
Middle Island is diverse and 20 vegetation associations have been mapped
(Hopkins 1981); 235 plant species are now recorded (Keighery 1995). Half
the island was burnt in a fire in 1972 and almost all the rest in 1977. The
areas burnt now support dense regrowth vegetation.
Mondrain Island (787 ha) is the second largest island in the Recherche. It lies
42 km SE of Esperance and some 11 km from the mainland. It is irregular in
shape, 6 km long and 2.8 km wide at its widest point. Permanent or semi-
permanent water is found in seepage areas on the western side of the island
and in rock pools on Baudin Peak (222 m), the island's highest point. The
40 Australian Entomologist, 2006, 33 (1)
island is characterised by a series of granite domes with large expanses of
bare rock. The vegetation is varied and some 283 native species are recorded
(Pearson et al. 2004). In shallow soils between the granite domes is dense
scrub, predominantly of Melaleuca globifera, Acacia conniana and
Allocasuarina huegeliana. In swales, where the soil is deeper, low forest of
Eucalyptus lehmanni occurs. Open sandy areas support Carpobrotus
virescens and meadows of yellow-flowered Senecio lautus, especially where
nesting shearwaters have enriched the soil. In other areas dense Rhagodia
baccata and Atriplex cinerea occur.
Sandy Hook Island (238 ha) is located 9 km WSW of Cape Le Grand and 22
km WNW of Mondrain Island. Like other islands in the archipelago it is
characterised by large granite domes and boulders. Much of the interior is a
high plateau overlain with shallow sand and gravel, which supports a dense
eucalypt and shrub association (Willis 1953). On the southeastern side of the
island is a small sandy cove, above which is a sheltered wooded gully. The
gully vegetation is dominated by Eucalyptus conglobata, Acacia and Hakea
species. Introduced grasses, thick in places, are well established.
Woody Island (196 ha) is located in Esperance Bay, 7 km from the mainland
and 15 km SE of Esperance. It is about 2 km (E-W) by 1.5 km (N-S) and
rises at its centre to 130 m. It is composed of granite, which is frequently
exposed between areas of shallow overlying soil. The island is well
vegetated. The shallow soils support variable heath and mallee formations.
Eucalypt forest is found in areas of deeper soil. Abbott and Black (1978)
recognised six vegetation classes; the two main ones are low open-heath on
the western half of the island and Eucalyptus-dominated closed forest on the
sheltered slopes south and east of the summit. The island has been grazed in
the past and parts of the northeastern portion are still cleared.
Goose Island (56 ha) is the smallest of the islands to be surveyed for
butterflies. It lies less than a kilometre to the north of Middle I. and 7.5 km
from the mainland. Its highest point is a gently sloping, exposed granite
dome.. Limestone cliffs are found on the eastern side of the island. The
vegetation is generally very low, in response to the shallow soils and
probably also to grazing by rabbits, which have been introduced to the island.
The presence of rabbits probably also explains, to a large degree, the extent to
which this vegetation differs in composition from that of nearby Middle I.
Dominant species such as Rhagodia baccata, Senecio lautus and
Carpobrotus virescens are uncommon on Middle I. R. baccata is found in
sandy areas honeycombed with petrel burrows. Shrubs of Pimelea ferruginea
occur in shallow soils near sheets of exposed granite.
Methods
Butterfly surveys of the Recherche islands were carried out in November of
1998, 1999 and 2003, at the time of year when peak butterfly activity is to be
expected on the adjacent mainland. It was not possible to visit all five islands
Australian Entomologist, 2006, 33 (1) 41
in a single year. Most time was devoted to the largest islands, Middle and
Mondrain, with their more diverse habitats. Four days were spent on Middle
Island, in 2003, and a total of five days on Mondrain, in 1998 and 1999.
Woody Island was visited for one day and Sandy Hook Island for just a few
hours in November 1998. A further day spent on Sandy Hook Island in 1999
by one of us (AW) was generally unproductive, due to cool, cloudy
conditions. Goose Island was surveyed for a few hours in November 2003
during the Middle Island expedition. Suitable sunny conditions for butterflies
were experienced on each survey trip. One of us (RP) spent a few hours on
Woody Island in December 1993, and his opportunistic observations are
included in this paper.
Prior to visiting the islands, we identified the major habitat types, with the aid
of aerial photographs and published data on the topography and vegetation.
Published plant lists were scrutinised for known butterfly food plants. During
our surveys, all accessible types of habitat were carefully explored and food
plants, when encountered, were examined for signs of larvae. Accessible
hilltops were monitored for hilltopping butterflies. Botanical nomenclature
follows Green (1985).
Results
The results of our survey are summarised in Table 1. Voucher specimens
have been lodged in the Insect Collection of the Department of Conservation
and Land Management or (plants) in the Western Australian Herbarium.
HESPERIIDAE
Hesperilla chrysotricha chrysotricha (Meyrick & Lower)
Recorded from Middle I. Locally abundant around the food plant, Gahnia
trifida (Cyperaceae), growing in a narrow belt along the eastern shoreline of
Lake Hillier. In the early mornings, males were observed flying amongst the
Gahnia foliage, presumably in search of emerging females. Several pupae
were found in typical sealed cylindrical shelters on the food plant.
PIERIDAE
Delias aganippe (Donovan)
Recorded from Woody I. This species was not observed during the surveys in
1998, 1999 and 2003. However, several specimens were seen by one of us
(RP) on an earlier trip to Woody I. in December 1993.
Pieris rapae rapae (Linnaeus)
Recorded from Mondrain, Sandy Hook and Woody Is. On Woody I., a few
individuals were seen on the eastern side of the island, particularly in cleared
areas near the landing point. On Sandy Hook I. the species was not seen in
1998. A single individual was observed in November 1999, even though the
weather on that visit was cool and overcast. On Mondrain I. P. r. rapae was
usually uncommon. However, in 1998, after a period of off-shore north-
easterly winds, the species suddenly became abundant.
42 Australian Entomologist, 2006, 33 (1)
Table 1. Butterflies recorded from Middle, Mondrain, Sandy Hook, Woody and
Goose Islands of the Recherche Archipelago.
Family and species Middle Mond- Sandy Woody Goose
rain Hook
HESPERIIDAE
Hesperilla chrysotricha chrysotricha °
PIERIDAE
Delias aganippe °
Pieris rapae rapae e e °
NYMPHALIDAE
Geitoneura klugii e
Heteronympha merope duboulayi °
Vanessa kershawi ° e. e. e
Vanessa itea ° ° °
Junonia villida calybe e. ° °
LYCAENIDAE
Nacaduba biocellata biocellata °
Neolucia agricola occidens ° e e e
Theclinesthes serpentata serpentata ° ° ° °
Zizina labradus labradus ° e e
Total number of species: 12 6 7 4 10 2
NYMPHALIDAE
Geitoneura klugii (Guérin-Méneville)
Recorded from Sandy Hook I. This species was encountered only on the
eastern side of the island, in a sheltered valley above the landing beach.
Butterflies were collected around patches of Austrostipa flavescens Labill.
(Poaceae), a known larval food plant.
Heteronympha merope duboulayi (Butler)
Recorded from Woody I. The common brown was not recorded during the
surveys in 1998, 1999 or 2003, which took place in the first half of
November and may have preceded the butterfly's appearance. RP, in his brief.
visit to Woody I. on 28 December 1993, recorded one female. Robyn Benken
(pers. comm.) found the species to be abundant during her visit on 12-13
December 2004; all specimens she was able to observe closely were male.
Vanessa kershawi (McCoy)
Recorded from Middle, Mondrain, Woody and Goose Is. On Middle I.,
numbers of fresh specimens were observed along the sheltered north-facing
and eastern coastline. Inland they were also common around Lake Hillier.
The butterflies were often seen feeding at flowering shrubs of Pimelea
ferruginea and Senecio lautus. On Mondrain I. the species was encountered
in 1998 and 1999. Butterflies were commonest in open meadows of
flowering Senecio lautus and Carpobrotus virescens. This habitat is often
Australian Entomologist, 2006, 33 (1) 43
found in nutrient enriched soils honeycombed with the burrows of the fleshy-
footed shearwater (Puffinus carneipes Gould). On Woody I., V. kershawi was
common in cleared areas near the landing point on the eastern side of the
island. Adults were seen feeding on the flowers of Senecio lautus and the
introduced Arctotheca calendula. A. calendula (Asteraceae) is a known food
plant and V. kershawi was seen ovipositing on this plant. On Goose I. two
specimens were observed, feeding on the flowers of Pimelea ferruginea.
Vanessa itea (Fabricius)
Recorded from Middle, Mondrain and Woody Is. The yellow admiral was
commonest on Mondrain and Woody Is, where its food plant Parietaria
debilis (Urticaceae) was abundant. On Mondrain L, adults were seen in
coastal areas and upland meadows of flowering Senecio lautus and
Carpobrotus virescens. Large numbers of larvae were found on P. debilis,
which was growing profusely under dense stands of Melaleuca lanceolata.
Some were collected and subsequently reared in captivity. On Woody 1.,
about six adults were seen in the late morning to early afternoon. Four or
more were seen hilltopping after 1630 h at the island's highest point. P.
debilis was abundant and typical larval shelters were found in three or more
places. On both Mondrain and Woody Is, many of the V. itea were freshly
emerged. On Middle I. only a few plants of P. debilis were found, under a
small stand of M. lanceolata north of Lake Hillier that had escaped the two
major fires. On this island V. itea was uncommon; only about six individuals
were seen over four days. Some of these fed briefly at the flowers of Pimelea
ferruginea. One of the plants of P. debilis had a typical larval shelter.
Junonia villida calybe (Godart)
Recorded from Middle, Mondrain and Woody Is. On Middle I., the species
was encountered only on the rocky promontory between Coverdale Cove and
Cormorant Cove. At this site three worn males had established territories
along the rocky shoreline. On Mondrain I. the species was also scarce. A
fresh specimen was captured on an exposed granite sheet in November 1998,
and none was seen in 1999. Only on Woody I. was the butterfly common.
Several specimens were observed and collected at the eastern end of the
island near the landing point. The species was observed with V. kershawi on
flowering Senecio lautus and flying along pathways and in open areas.
LYCAENIDAE
Nacaduba biocelata biocellata (C. & R. Felder)
Recorded from Woody I. This common lycaenid was encountered only on
Woody I. A few individuals were seen near the summit of the island, around
freshly opened flowers of Acacia rostellifera.
Neolucia agricola occidens Waterhouse & Lyell
Recorded from Middle, Mondrain, Sandy Hook and Woody Is. Fringed
heath-blues were found on all but Goose I. On Middle I. they were plentiful.
44 Australian Entomologist, 2006, 33 (1)
Butterflies were almost always seen close to flowering shrubs of Pultenaea
obcordata or Eutaxia obovata, which were common on the southeastern side
of Lake Hillier and along the northern and eastern coastline. By contrast, the
species was uncommon on the other islands. One freshly emerged specimen
was captured on a low flowering Acacia rostellifera near the summit of
Woody I. On Sandy Hook I., a specimen was collected flying round a Hakea
shrub. On Mondrain L, one butterfly was collected in 1998 and another
closely observed on a shrub at the northern end of the island in 1999.
Theclinesthes serpentata serpentata (Herrich-Schaffer)
Recorded from Mondrain, Sandy Hook, Woody and Goose Is. Saltbush blues
were seen mostly near one of their food plants, Rhagodia baccata
(Chenopodiaceae); no other species of food plant was encountered. We
recorded this butterfly on all the islands except Middle L, where we found
very few Rhagodia specimens. On Middle I. it was evident that this plant's
occurrence had been much reduced by grazing Tammar wallabies (Macropus
eugenii (Desmarest)). On Mondrain I., the butterflies were abundant in 1998,
around Rhagodia baccata above the landing beach on the northeastern side of
the island. On the return visit, in 1999, the butterflies were absent from this
site. On Sandy Hook I. one butterfly was seen (but not collected) in 1998. On
Woody I. the species was moderately common in low-lying, partly cleared
areas on the sheltered northeastern side. Here, too, the butterflies were found
near R. baccata. On Goose I., where succulent mats of R. baccata grow
extensively in nutrient enriched sandy areas honeycombed with shearwater
burrows, freshly emerged butterflies were abundant.
Zizina labradus labradus (Godart)
Recorded from Middle, Mondrain and Woody Is. On Middle I. the species
was uncommon. Two individuals were found on the northern coastline
between Coverdale Cove and North East Point, one feeding on a flowering
Senecio lautus. On Mondrain I. it was recorded in 1998 and 1999. On our
first visit, Z. /. labradus was not seen for the first three days and appeared on
the island only after a prolonged period of strong off-shore winds. The
butterflies were first observed about 0930 h on 12 November 1998; by late
morning they had become abundant and were frequently seen on the slopes of
the hill at the northern end of the island, in meadows and around vegetation
between granite sheets. In 1999 only one butterfly was recorded. On Woody
I., Z. l. labradus was locally common near the landing point.
Discussion
In considering the behaviour and ecology of butterfly species on islands, of
particular interest is their status. They can be present either permanently or
temporarily, referred to here as ‘permanent’ or ‘temporary’ species.
For a permanent species, the population is likely to be composed entirely or
largely of individuals that are resident on the island. There may be a viable,
Australian Entomologist, 2006, 33 (1) 45
isolated population, comprising resident individuals with no influx from
elsewhere, or such an influx may occur, boosting a resident population. In the
latter case, the resident population may to some degree rely on the influx for
its viability. If the butterfly population is to remain permanent, however, it
cannot rely on that influx too heavily, since there are bound to be years or
times when the usual influx does not occur (for example, as a result of a
mainland population being destroyed by fire).
Most of the permanent species might be expected to have a single generation
a year, since such species need a food plant only at the time the larvae are
feeding. Those species that have continuous generations would normally
need to have food plants available in a suitable state of growth throughout the
year, to allow each new generation to breed; this is unlikely on islands, with
their limited number of plant species. An influx of adults from elsewhere
cannot be relied on to maintain the presence of a species with continuous
generations at times of the year when it is unable to breed.
The temporary species will all be ones able to travel to the island from
elsewhere. Some may go there deliberately, either to breed when the season
or conditions are right or to rest during a migration. Others may be there by
accident, having the intention of remaining on the mainland but being
displaced out to sea by off-shore winds.
Four of the species we recorded - Hesperilla chrysotricha chrysotricha,
Geitoneura klugii, Heteronympha merope duboulayi and Neolucia agricola
occidens - are likely to be permanent species on the islands where found.
In Western Australia, Hesperilla chrysotricha has one or possibly two
generations a year (Braby 2000). Breeding was confirmed on Middle Island.
For most of the year the larvae or pupae remain in shelters on the Gahnia
trifida food plant. This island population is likely to be an isolated one, viable
enough to have persisted since the island was formed. The fire in 1972 burnt
the eastern part of the island, including the Gahnia vegetation fringing the
eastern side of Lake Hillier. However, isolated clumps of the food plant may
have survived on the northern side of the lake. Moreover, G. trifida occurs
also on the lower eastern slopes of Flinders Peak (A.J.M. Hopkins, pers.
comm.). Either part of the lakeside population may have survived, or
recolonization may have occurred from a population at Flinders Peak.
Neolucia agricola has one generation a year (Braby 2000) and is not known
to be very mobile. Its populations on the islands are likely to be isolated ones
that have persisted. On Middle Island the butterflies were very common and
were habitually seen around flowering shrubs of Pultenaea obcordata and
Eutaxia obovata. (Fabaceae). These are likely food plants, as other Pultenaea
and Eutaxia species are known larval food plants. A potential food plant,
Bossiaea dentata, occurs on the other islands where N. agricola was
recorded.
46 Australian Entomologist, 2006, 33 (1)
Geitoneura klugii has only one generation a year (Braby 2000). It is not
known to be a very mobile species; our experience in Perth is that it wanders
barely at all from the bushlands where it breeds. The population on Sandy
Hook I., 8 km from the mainland, is likely to be an isolated one, where the
species almost certainly breeds on the native grass Austrostipa flavescens.
Given that Heteronympha merope has only one generation a year (Braby
2000) and that the grasses on Woody Island include two of its known food
plants, Cynodon dactylon and Poa poiformis, this butterfly may be a
permanent breeding species on this island. This likelihood is further
emphasized by the apparent abundance of the species on the island. H. m.
duboulayi has been found to be quite mobile, even though it is not known to
migrate (Braby 2000). A specimen recorded on Garden Island may have
travelled 2 km or more from the Perth mainland (Williams 1997) and the
Woody Island population may possibly be boosted by occasional arrivals
from the mainland. Whether or not H. m. duboulayi occurs on other islands in
the Recherche would need to be determined by surveys in summer.
Most of the eight remaining species are likely to be temporary. For Vanessa
itea, V. kershawi and Junonia villida, this is partly because they have
continuous generations and partly because they are highly mobile migrants
(Braby 2000). That we have recorded them from most of the islands we have
visited, including those of the Houtman Abrolhos, 60-80 km off the coast
(Williams and Powell 1998), suggests they are easily capable of travelling the
much shorter distances between the mainland and the Recherche islands
surveyed. Being swift, powerful fliers, they probably rely less on favourable
winds for such journeys than do other, less powerful species.
On the Recherche islands, V. ifea breeds on Parietaria debilis and probably
also on Urtica urens, which is available on Woody Island (Western
Australian Herbarium Collection). Both these plants are annuals, which
germinate in May or June and die off in November to December. V. itea
would be unable to persist on the islands over the four to five months when
its food plants are unavailable.
V. kershawi likely breeds from time to time on the islands, where likely food
plants include Arctotheca calendula, Gnaphalium sp. and Rhodanthe sp.
Likewise, J. villida may breed on known food plants such as Centaurium
spicatum and Scaevola aemula. It is unlikely, however, that either species
would breed on the Recherche islands over the whole year.
Both Delias aganippe and Pieris rapae are somewhat mobile (Braby 2000).
D. aganippe is clearly a temporary species on at least Woody Island, since
none of its food plants is present. Although we did not find it on any of the
other islands, it is likely to visit other islands in the archipelago from time to
time, and could breed on Middle Island where a known food plant, Amyema
melaleucae, occurs. The sudden increase in numbers of P. rapae observed on
Australian Entomologist, 2006, 33 (1) 47
Mondrain Island after a period of off-shore winds suggests that this species
will travel from the mainland to the islands, at least when the winds are
favourable. Cakile maritima (Brassicaceae), a possible food plant, grows on
many of the islands. On the mainland the species is certainly mobile. It was
introduced to Melbourne in 1939, and within three years had reached the west
coast (Thomas and Lewington 1991). In Europe, large migratory flights occur
from time to time.
Although the number of generations a year of Zizina labradus labradus has
not been recorded, the presence of the adults throughout the year in temperate
Australia (Braby 2000) suggests that it breeds continuously. It is therefore
probably a temporary species on the Recherche islands. The sudden
abundance of this species on Mondrain Island following its apparent absence,
and after a period of off-shore winds, strongly suggests that it travels to the
islands from the mainland, at least when the winds are favourable.
From the present information, the status on the islands of the remaining two
species, Nacaduba biocellata and Theclinesthes serpentata, is difficult to
determine. It is unknown whether N. biocellata has a single generation or a
succession of generations (Braby 2000), or whether it is sufficiently mobile
to travel between the mainland and the islands. The number of annual
generations of 7. serpentata has not been established (Braby 2000). Its
absence from the portion of Mondrain Island surveyed in 1999, following an
abundance in 1998, indicates that its occurrence on the island may be only
temporary. If the Mondrain population is temporary, the same can be
expected for the populations on Woody and Goose Islands.
The butterfly fauna on the adjacent mainland has a direct bearing on what
butterflies may be expected to occur on off-shore islands. Some species
appear to have remained on the islands since their separation from the
mainland, supported there by surviving available food plants. Others are now
known to be regular visitors to the islands.
V. kershawi, V. itea, J. villida and Z. labradus, have been recorded on all the
island groups surveyed: Bernier and Dorre Is, the Houtman Abrolhos,
Rottnest, Garden and the Recherche Archipelago (Williams and Hall 1993,
Williams 1997, Williams et al. 1998, Williams and Powell 1998, Williams et
al. 2000). All are temporary species, which either visit the islands under their
own power or are carried there by off-shore winds.
The silver-spotted ochre, Trapezites argenteoornatus (Hewitson), is well
established on all but the Recherche islands. Its success can be attributed to
the abundance of its food plant Acanthocarpus preissii on the west coast
islands. Two lycaenids, 7. serpentata and N. agricola, are successful island
species. T. serpentata occurs on all but Garden Island, where its saltbush food
plant is lacking. N. agricola appears to breed and maintain stable populations
on the Abrolhos and Recherche islands.
48 Australian Entomologist, 2006, 33 (1)
Acknowledgements
We are grateful to regional staff of the Department of Conservation and Land
Management in Esperance, particularly Bernie Haberley, who organised our
boat transport to and from Mondrain and Sandy Hook Islands, and Geoff
Young, who made arrangements for us to travel to Middle Island with
Department field staff Ray (Moey) Ramsden, Craig Clements and Wayne
Williams. Greg Keighery of the Deparment of Conservation and Land
Management identified plant specimens from Middle Island.
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Australian Entomologist, 2006, 33 (1): 49- 55 49
A KEY TO SOME AUSTRALIAN GENERA OF LARGE
NOCTURNAL ICHNEUMONIDAE (HYMENOPTERA), INCLUDING
FLIGHT PERIODICITIES AND INFLUENCE OF MOON PHASE ON
LIGHT TRAP CATCHES
MARK W. SHORT'?, STEFAN SCHMIDT? * and MARTIN J.
STEINBAUER'?
'Co-operative Research Centre for Sustainable Production Forestry & CSIRO Entomology,
GPO Box 1700, Canberra, ACT 2601
?Present address: Health Registers and Cancer Monitoring Unit, Australian Government -
Australian Institute of Health and Welfare, GPO Box 570, Canberra, ACT 2601
3CSIRO Entomology, GPO Box 1700, Canberra, ACT 2601
"Present address: State Museum of Zoology, Hymenoptera Section, Miinchhausenstr. 21, 81247
Münich, Germany
* Address for correspondence: Australian Plague Locust Commission, Australian Government —
Department of Agriculture, Fisheries and Forestry, GPO Box 858, Canberra, ACT 2601
(email: martin.steinbauer@daff.gov.au)
Abstract
A simple key to some of the genera of large, nocturnal ichneumonid wasps found in southeastern
Australia is provided, along with information about their flight periodicities and the influence of
moon phase on light trap catches. Approximately 74% of wasps caught were active between
2130 and 0245 h and more were caught on new moon nights than on full moon nights.
Introduction
Large (ie. forewing 2 15 mm long), nocturnal ichneumonid wasps are
commonly caught when UV light trapping in southeastern Australia and
undoubtedly form an important guild of natural enemies of other insects.
Similarities in morphology and colouration between different genera may
deter non-taxonomists from identifying them, thus limiting the recording of
their diversity and abundance.
Nocturnal wasps generally have swollen ocelli, very long antennae and are
entirely or almost entirely orange-brown in colour (Fig. 1). This appearance
is called the *ophionoid facies" and occurs mainly in the Ichneumonoidea
(Braconidae and Ichneumonidae) and some tropical Chalcidoidea and
Vespoidea (Huddleston and Gauld 1988). Many nocturnal parasitic wasps
attack the nocturnally active larvae of Lepidoptera (e.g. Noctuidae) and
Symphyta, some of which are of significant economic importance
(Huddleston and Gauld 1988; hosts listed in Table 1). Although similarities
in circadian rhythms and their parasitoid lifecycle might logically place them
in a single functional group (i.e. ‘natural enemies’), such a grouping would
provide only limited insight into the specific impacts of the different taxa on
other biota in a given ecosystem.
Large nocturnal wasps are distinctive and easily extracted from a typical light
trap catch. In our studies, Ichneumonidae accounted for all but one of many
hundreds of specimens examined from light traps in southeastern Australia,
50 Australian Entomologist, 2006, 33 (1)
Table 1. Host records for large nocturnal ichneumonids of Australia (compiled from
Gauld 1984). Host families lepidopteran except Pergidae (Hymenoptera).
Ichneumonid Host family Host species
taxon
Cidaphus No records Non-Australian species are secondary parasitoids
of moths and sawflies via Ichneumonidae
Hypopheltes Pergidae Perga sp., Pseudoperga belinda Kirby
Megaceria Geometridae Mnesampela privata (Guenée), Paralaea Guest (as
Stathmorrhopa sp.)
Notodontidae ^ Unidentified pupa
Netelia Noctuidae Agrotis infusa (Boisduval), Agrotis munda Walker,
Helicoverpa armigera (Hübner), Helicoverpa sp.,
Mythimna convecta (Walker), Mythimna separata
(Walker) ^ Persectania ewingii (Westwood),
Spodoptera exempta (Walker), Spodoptera litura
(Fabricius)
Pieridae Pieris rapae (Linnaeus)
Ophioninae Anthelidae Anthela varia (Walker), Anthela sp.
Geometridae Chlenias sp.
Lymantriidae ^ Acyphas sp.
Noctuidae Mythimna separata (Walker), Mythimna sp.,
Persectania sp.
SN =
RN ees
Fig. 1. Netelia sp., female. Habitus illustrating an ichneumonid with ophionoid facies
(length 18 mm from face to tip of abdomen, excluding ovipositor).
Australian Entomologist, 2006, 33 (1) 51
the exception belonging to the family Aulacidae. We collated information
about this group while conducting routine light-trapping as part of another
study. Accordingly, we compiled a key to the large, nocturnal ichneumonid
genera (excluding the Ophioninae — see below). The key is aimed at non-
taxonomists and is much less formidable than the keys to Australia's
Ichneumonidae provided by Gauld (1984).
We used Gauld (1984) as a guide to the Australian genera of nocturnal
Ichneumonidae, supplemented by material in the Australian National Insect
Collection, CSIRO Entomology, Canberra, and our own material. The key
was constructed by compiling information from Gauld (1984) and with
reference to Gauld and Huddleston (1976) and Huddleston and Gauld (1988).
Key to some Australian genera of large nocturnal Ichneumonidae
This key is designed for non-taxonomists and uses only easy-to-see
characters of the forewing. However, the eight Australian genera of
Ophioninae cannot be separated so easily and have not been included; keys to
these genera can be found in Gauld (1977, 1984). Our key is applicable to
any ichneumonid with ophionoid facies and a forewing at least 12 mm in
length. A key covering smaller ichneumonids would need to include Anacis
Porter, Mesochorus Gravenhorst and perhaps other genera. Light traps also
occasionally catch wasps that do not exhibit ophionoid facies. These wasps
are probably not nocturnal but might be crepuscular or have been disturbed
by the setting up or operation of the trap (Gauld and Huddleston 1976).
1 Forewing with two intercubital veins that enclose a small cell, the areolet
(Fig. 2); in Netelia lower part of distal intercubital vein often missing .... 2
— Forewing with a single intercubital vein and no areolet (Fig. 3) ................
irr ETETO HXIMITEIINI E E s E E PI eee Ophioninae (not keyed further)
2 First subdiscal cell of forewing much higher at distal end than at proximal
endi(EigT4) pete ENTRE Ie I IR TRITT Megaceria Szépligeti
— First subdiscal cell of forewing about same height at each end (Fig. 5) ... 3
3 Forewing vein 2m-cu with two widely separated bullae (unpigmented
portions of the vein crossed by flexion lines) (Fig. 6) ............ Netelia Gray
— Forewing vein 2m-cu with a single long bulla (Fig. 7) ............................. 4
4 Areolet approximately rectangular, about twice as long as wide (Fig. 8,
lower arrow); pterostigma (thickened vein about halfway along anterior
margin of forewing) moderately broad, r-rs vein arising near its centre
(Hig S Xuppenarrow)leme eu EE Cidaphus Forster
— Areolet diamond-shaped (Fig. 9, lower arrow); pterostigma long and
narrow, r-rs vein arising near its proximal end (Fig. 9, upper arrow) .........
UTOTONI EEOAE YAYAT LIIITE EIDA or Hypopheltes Cushman
52 Australian Entomologist, 2006, 33 (1)
Figs 2-9. Venation of the distal portions of the forewings of large nocturnal
ichneumonids, encompassing the genera Megaceria (Fig. 4), Netelia (Fig. 6),
Cidaphus (Fig. 8) and Hypopheltes (Fig. 9). Venation typical of species belonging to
the Ophioninae is shown in Fig. 3. Arrows indicate locations of features mentioned in
the key. Compiled from Gauld (1984).
Australian Entomologist, 2006, 33 (1) 53
Summary of light trap catches
The study site was an experimental planting of 500 eucalypts located near
Hall, ACT (35?09'55.7"S, 149?02'49.9"E; altitude 615 m a.s.l.). The two
light traps used were custom made so that they could sub-sample in seven
periods from 1800 to 0600 h (illustrated in Steinbauer 2003).
We did not develop the above key until after our trapping was complete.
Consequently, the following findings relate to large nocturnal ichneumonids
as a whole rather than individual genera or species. Our light trapping yielded
a total of 625 large nocturnal wasps. Based on a small sub-sample, we
estimate that approximately 75% of the wasps were species of Netelia and the
remainder Ophioninae.
The number of wasps caught fluctuated considerably from night to night but
there was a clear downward trend in numbers from December to May (Fig.
10; see also Steinbauer eft al. 2001, p. 530). The numbers of wasps caught
showed a clear peak between 2130 and 0245 h, with 73.696 of them being
caught in this period (Fig. 11). The phase of the moon also appears to have
influenced the number of wasps collected, with more caught near the new
moon than near the full moon (Fig. 12).
30
N N
© a
Total number of wasps caught
a
Dec99 : Jan0O : Feb0O : Mar0O : AprO0 ; May00
Month
Fig. 10. Total number of large nocturnal wasps caught in light traps versus day of year
(n = 625 individuals).
54 Australian Entomologist, 2006, 33 (1)
Total number of wasps caught
"- B E ag
| 1800-1945 1945-2130 2130-2315 2315-0100 0100-0245 0245-0430 0430-0600 |
| " |
| Time of night (24 hrs) |
L - - E CM. en Pm a >
Fig. 11. Total number of large nocturnal wasps caught in light traps versus time of
night (n = 625 individuals).
| 16.0
[O Full E Last Qtr m New & First Qtr |
A
| B I
Jan00 : Feb00 : Mar00
140 4
12.0 4
10.0 |
8.0 +
60.
40 4
2.0 4
Mean number of wasps caught per night
Poe.
Apr00 : May00
0.0 -
n
i
1
i
Month
Fig. 12. Average number of large nocturnal wasps caught in light traps versus phase
of moon (average computed for phase + 2 nights).
Australian Entomologist, 2006, 33 (1) 55
Acknowledgements
We thank Colin Tann (CSIRO Entomology, Narrabri) for donating the two
light traps, Brett Brewer, Craig Szabadics and Roger Williams (CSIRO
Entomology, Canberra) for modifications and repairs to the traps, John
Dowse, Michelle Michie and Rex Sutherland (CSIRO Entomology,
Canberra) for assistance with trapping and two anonymous referees for
helpful comments on an earlier version of the text.
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(Natural History), London; 413 pp.
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traits of Mnesampela privata that exacerbate population responses to eucalypt plantations:
comparisons with Australian and outbreak species of forest geometrid from the northern-
hemisphere. Austral Ecology 26: 525-534.
56 Australian Entomologist, 2006, 33 (1)
RECENT ENTOMOLOGICAL LITERATURE
LUSHAI, G., ZALUCKI, M.P., SMITH, D.A.S., GOULSON, D. and DANIELS, G.
2005 The lesser wanderer butterfly, Danaus petilia (Stoll 1790) stat. rev. (Lepidoptera:
Danainae), reinstated as a species. Australian Journal of Entomology 44(1): 6-14.
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2005 One new genus and three new species of Orsillinae (Hemiptera: Lygaeidae) from
Australia. Australian Journal of Entomology 44(2): 122-131.
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2003 Polyrhachis loweryi (Formicinae), a guest ant parasitizing Rhytidoponera sp.
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2003 Incipient founder populations of Mediterranean and Queensland fruit flies in Australia,
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butterflies. Australian Journal of Entomology 43(3): 258-270.
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2003 Twenty-five new Dytiscidae (Coleoptera) of the genera Tjirtudessus Watts &
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THE AUSTRALIAN
Entomologist
Volume 33, Part 1, 12 March 2006
CONTENTS
BASHFORD, R.
The insect complex inhabiting galls formed by Cecidomyia acaciaelongifoliae Skuse
(Diptera: Cecidomyiidae) on blackwood (Acacia melanoxylon) in Tasmania.
BELLIS, G.A., FALICIANO, R., ALVES, A. AND HEARNDEN, M.
A survey of insect pests breeding in mango fruit in Dili, East Timor.
GREEN, K.
The return migration of bogong moths, Agrotis infusa (Boisduval) (Lepidoptera:
Noctuidae), from the Snowy Mountains, New South Wales.
HAYWOOD, B.T. AND NATT, V.
First confirmed observation of Heteronympha cordace wilsoni Burns
(Lepidoptera: Nymphalidae: Satyrinae) in South Australia.
LANE, D.A.
Life history notes on Leucomonia bethia (Kirby) (Lepidoptera: Sphingidae).
MCDONALD, F.J.D.
Birna, a new name for Linea McDonald (Hemiptera: Pentatomidae).
peines sss A SS suique ENDE ee
MEYER, C.E., WEIR, R.P. AND WILSON, D.N.
Butterfly (Lepidoptera) records from the Darwin region, Northern Territory.
SHORT, M.W., SCHMIDT, S. AND STEINBAUER, M.J.
A key to some Australian genera of large nocturnal Ichneumonidae (Hymenoptera),
including flight periodicities and influence of moon phase on light trap catches.
STEINBAUER, MJ.
Re-collection and tentative host record for Hygia (Australocopura) sandaracinae
Brailovsky (Hemiptera: Coreidae: Colpurini).
WILLIAMS, A.A.E AND POWELL, RJ.
The butterflies (Lepidoptera) of Middle, Mondrain, Sandy Hook, Woody and
Goose Islands in the Recherche Archipelago, Western Australia.
RECENT ENTOMOLOGICAL LITERATURE
ISSN 1320 6133 e
T