THE UNIQUE COOPER CREEK CATFISH FROM CENTRAL
AUSTRALIA
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Peter J. Unmack
Introduction
The Cooper Creek
catfish is an undescribed species and genus in the family Plotosidae (eeltailed
catfish). It possesses a number of
unusual features compared to other plotosids including low fecundity, large
eggs, good eyesight, and very aggressive behaviour towards other fish. It appears to have no close relatives and
occurs only in the Cooper Creek system in Queensland and South Australia which
is part of the internal Lake Eyre drainage.
The first museum specimens were collected in 1918 and again in 1938
(Queensland Museum specimens), however, the species was not recognised as being
different until the late 1960's when Hamar Midgley collected additional
specimens (Lake 1971). Since then, it
has been collected infrequently, few specimens exist in museum collections and
this species has rarely been kept in aquaria.
All comparisons made here between Cooper Creek catfish and other
plotosids are based on my experiences with the following Australian species,
Hyrtl's catfish (Neosilurus hyrtlii),
black catfish (N. ater), Dalhousie
catfish (Neosilurus sp), silver
tandan (Porochilus argenteus),
Rendahl's catfish (P. rendahli), and
freshwater catfish (Tandanus tandanus). Thus, when I refer to plotosids I am
referring to these species only.
Description
The Cooper Creek
catfish grows to at least 600mm (2ft) and has a very blunt head and relatively
small eyes compared to other plotosids.
It's mouth is underslung with bony tooth plates capable of drawing blood
from unsuspecting fingers. Colouration
in the wild is typically creamy brown with dark speckles along the upper body
and tail. Under aquarium conditions,
colour varies considerably from a light blue grey to a darker shade of blue
grey depending upon light intensity and mood of the fish. Speckling along the body and tail varies
from slightly lighter than the background colouration to white against a dark
background. Only two photographs have
previously been published (Lake 1978, Steptoe 1988).
Habitat
Cooper Creek
catfish is common, though not abundant throughout the Cooper Creek system. It is usually found in larger, more
permanent waterholes with an earthen/clay substrate (very few central Australian
waterholes can be considered strictly permanent). As far as I'm aware they are yet to be collected from very
ephemeral waterholes, making it one of only two riverine species [the other
being Welch's grunter (Bidyanus welchi)]
which I have not recorded from ephemeral waterholes in central Australia. Water conditions vary considerably depending
upon time of year and hydrological conditions. The water is almost invariably
turbid with no visibility, although occasionally the river runs clear after major
flooding, as occurred in the Barcoo River after massive floods in 1990. After initial turbid runoff, the river is
fed by ephemeral springs which release clear water until their supply runs out,
then the river's flow ceases and turbidity increases again. (Spring discharge is determined by the
quantity of rainfall received; significant spring flow occurs only after severe
rainfall events).
Conservation Status
They are not
presently considered to be in any danger of extinction.
Collection and transport
I have captured
Cooper Creek catfish by angling only.
Specimens may be captured in a variety of nets (illegal without relevant
fisheries permits), however, despite considerable sampling effort with small
seine nets I have never captured them this way. I have transported them with no losses from Queensland to
Victoria in drums of about 70 litres with two large fish per container at
temperatures up to about 32oC.
No aeration was required unless the vehicle stopped moving for more than
an hour or so.
Aquarium care
I have maintained
Cooper Creek catfish in aquaria between 12-32oC with preferred
temperatures probably being around 24-28oC and a pH range of 6.8 to
7.5, although they can tolerate more acidic conditions. In the wild, based on the stomach contents
of a few fish, they appear to feed on snails.
In captivity they have accepted small live fish, fillets of fish,
shrimps, earthworms and artificial pellets.
Unlike most plotosids, this species must be kept alone as they are very
aggressive, both amongst themselves and with different species, usually killing
other fish in a short time. They are also likely to attack siphon hoses, human
appendages and anything else placed in the aquarium.
Breeding biology
Virtually nothing
is known of their breeding biology. No
specimens less than 160mm (6˝") are found in museum collections and I am
yet to meet anyone who claims to have caught any smaller fish. Most plotosids are easily sexed by examining
their urinogenital papilla (H. Midgley pers. comm.), and Cooper Creek catfish
are no exception. Males posses a
longer, thinner pointed urinogenital papilla, while that of the female's is
somewhat shorter, broader and flatter (see fig. 1). The urinogenital papilla size of both sexes varies depending with
age and time of year.
During December
1993, a breeding attempt was made by R. Lewis, P. Unmack, C. Brumley, and A.
Moore. Two eggs were extracted from a
female (460mm total length) using a catheter.
They were cloudy, yellowish, non adhesive and slightly distorted in
shape by the catheter. The eggs were
not sufficiently developed to attempt to fertilise and no sperm could be
extracted from the male; thus the experiment was terminated.
In comparison to
published information on other Australian plotosids, Cooper Creek catfish have
a much lower fecundity with significantly larger eggs, (see Table 1.).
Table 1. Comparison of available data on fecundity
and egg size for various Australian plotosids
species |
length (mm) |
weight (grams) |
no. of eggs |
egg size (mm) |
reference |
Cooper Creek catfish |
460 |
- |
1000 § |
3×4, 2.75×3.75 |
this paper |
Dalhousie catfish |
72-120 |
- |
136-1197 |
1 |
Glover 1989 |
black catfish |
348-440 |
- |
14600-20400 |
2.6 ‡ |
Orr and Milward 1984 |
Hyrtl’s catfish |
186-267 |
- |
1600-15300 |
1-1.5 † |
Orr and
Milward 1984 |
freshwater catfish |
470-550 |
1250-2000 |
18000-26000 |
2.5-2.9* |
Lake 1967a, b |
freshwater catfish |
- |
675-2275 |
2000-20600 |
2.28-3.05* |
Davis 1977 |
* from running ripe fish ‡ after fertilisation § estimated by R. Lewis † estimated by R. Wager (pers. comm.)
A number of
factors need investigation before we begin to understand the breeding biology
of Cooper Creek catfish. This includes
investigation of environmental factors that stimulate reproduction, whether
they are egg scatterers or nest builders (no nests have been reported), time to
hatching, size of fry, time until first feeding, and the size at which they
mature.
I believe this
species will spawn at temperatures around 26oC based on the
observation that the female's urinogenital papilla appears to be most extended
and swollen around this temperature.
Based on the low fecundity I believe spawning occurs annually, although
good recruitment is probably linked to major flooding when fry food is more
abundant. I suspect, given their low
fecundity, they will either guard their eggs or mouth brood them. Based on the egg size, fry will be large and
well developed at hatching.
General discussion
Due to the
limited collection of this species, one is forced to speculate and infer from
knowledge of other species, thus what is said in this section should not be
taken as fact.
I believe the
Cooper Creek catfish is a relict that does not exhibit the usual adaptations to
desert conditions. They would appear to
be better suited to an environment with stable or seasonal conditions and
clearer water. Based on aquarium observations,
the plotosids that I have kept have relatively poor eyesight. Species such as Hyrtl's catfish and silver
tandan appear to find food by chance or smell, not eyesight. As food is dropped in the tank they stumble
across it on the bottom of the tank. In
addition to an excellent sense of smell (like most plotosids), Cooper Creek
catfish have very good eyesight and will usually rise off the bottom to take
food as it falls through the water.
They are also more efficient at catching live fish and shrimp than other
plotosids. This poses the question of
why a fish needs good eyesight to live in waterholes so turbid that most of the
time visibility is no greater than 2cm.
Presumably its ancestors lived in a clear water environment where good
eyesight is advantageous. Usually,
species with smaller eyes have poorer eyesight relative to those with larger
eyes. In contrast to this, the Cooper
Creek catfish has the smallest eyes, but the best eyesight among plotosids.
Compared to other
fish from the Australian arid zone, Cooper Creek catfish have the largest eggs
and lowest fecundity per body weight to egg ratio. Low fecundity combined with large egg size is not usually
associated with fish in desert rivers.
It is more likely to be encountered in fishes living in stable
environments with regular seasons.
Cooper Creek
catfish, based on its general appearance (morphology) and what little else is
known of it, doesn't appear to have any close relatives, at least not at the
generic level of classification. Where
have its relatives gone? What has it
evolved from? Perhaps it is the last in
a plotosid evolutionary branch that was once widespread, or alternatively one
that evolved in a particular area and never became widespread. Only details from the fossil record and
examination of plotosid osteology or genetics may answer this. Irrespective of all that, Cooper Creek
catfish would have most likely been widespread in the Lake Eyre drainage during
recent wetter phases in central Australia's history such as when Lake Dieri is
thought to have existed. Lake Dieri is
the ancestral Lake Eyre which is thought to have existed sometime in the last
20-45 000 years before present when central Australia experienced higher
rainfall. During this period, Lake
Dieri was probably larger than the present day Lake Eyre and contained a
permanent body of freshwater (Dulhunty 1982, 1983) [There is some dispute as to the timing, size and existence of
precursors to Lake Eyre, see Stevens (1991).]
Cooper Creek catfish were probably one of the higher predators in the
system (with the advantage of good eyesight), along with yellowbelly/golden
perch (Macquaria ambigua) and
possibly other species no longer found in central Australia. I believe increasing aridity eliminated
Cooper Creek catfish from most of their range and they were only able to
persist in Cooper Creek because it has more permanent waterholes than other
central Australian rivers. If the
hypothesised reduction in range in central Australia with increasing aridity is
correct, and aridity increases in the future, Cooper Creek catfish will
probably join the dinosaurs in extinction.
I predict that
detailed research into the biology and taxonomy of Australia's largely unknown
plotosids will increase the number of unique and interesting features
recognised in the Cooper Creek catfish.
Conclusions
The Cooper Creek
catfish is not for the faint hearted.
It has a voracious appetite, an aggressive manner, and requires a large
tank. Despite this, its rewarding to
keep and specimens become very responsive towards their owners.
Acknowledgments
Thanks to R.
Lewis, C. Brumley, and A. Moore for their assistance in trying to breed this
species. Thanks also to those who
commented on earlier drafts.
References
Davis, T. L.
O. 1977. Reproductive biology of the freshwater catfish, Tandanus tandanus Mitchell, in the
Gwydir River, Australia II. Gonadal
cycle and fecundity. Australian Journal of Freshwater and Marine
Research. 28: 159-169.
Dulhunty, J.
A. 1982. Holocene sedimentary environments in Lake Eyre, South
Australia. Journal of the Geological Society of Australia. 29: 437-442.
Dulhunty, J.
A. 1983. Lake Dieri and its Pleistocene environment of sedimentation,
South Australia. Journal and Proceedings, Royal Society of New South Wales. 116: 11-15.
Glover, C. J. M. 1989. Fishes. In Natural
History of Dalhousie Springs. Ed. Zeidler, W. & Ponder, W. F. South Australian Museum, Adelaide. pp 89-112.
Lake, J. S. 1967a.
Rearing experiments with five species of Australian freshwater fishes
I. Inducement to spawning. Australian
Journal of Freshwater and Marine Research.
18: 137-153.
Lake, J. S. 1967b.
Rearing experiments with five species of Australian freshwater fishes
II. Morphogenesis and ontogeny. Australian
Journal of Freshwater and Marine Research.
18: 155-173.
Lake, J. S. 1971.
Freshwater fishes and rivers in
Australia. Nelson, Melbourne. 61pp.
Lake, J. S. 1978.
Freshwater fishes of
Australia. An Illustrated Field Guide Nelson, Melbourne. 160pp.
Orr, T. M. and
Milward, N. E. 1984. Reproduction and development of Neosilurus ater (Perugia) and Neosilurus hyrtlii Steindachner
(Teleostei: Plotosidae) in a tropical Queensland stream. Australian
Journal of Freshwater and Marine Research.
35: 187-195.
Steptoe, W. 1988.
Expedition to Min Min country. Modern Fishing. December 1988.
Stevens, B. P.
J. 1991. Some aligned claypans in the Strzelecki dunefield, central
Australia. Australian Journal of Earth Sciences. 38: 485-495.