BIRD
RESEARCH IN THE GREAT WESTERN WOODLANDS
Harry
F. Recher
Ted Davis (Boston University) and I have been
studying birds in the Great Western Woodlands (GWW) since 1997 when we
first visited the Yellowdine area east of Southern Cross to study
birds in Salmon Gum woodlands (Recher and Davis 2002). Earlier we had
worked in Wandoo woodlands at Dryandra (Recher and Davis 1998). In
2000, I initiated a study of birds in York Gum and Salmon Gum
woodlands on Mt Gibson Station (Recher and Davis 2010) and in 2003 we
commenced work on birds in eucalypt woodlands along the Norseman-Hyden
Road 10-45 km west of Norseman. Commencing in 2005 we were able to
join an ARC funded project with The Wilderness Society and people from
the Australian National University (Recher et al. 2007). We’ve
continued this work through 2010 using our original study areas at
Yellowdine and Norseman, while adding new sites in woodlands west of
Widgiemooltha 10-45 km along Cave Hill Road and north of Norseman in
similar woodlands 25-35 km along the Coolgardie-Norseman Road. I’m
happy to provide GPS coordinates to anyone wanting to visit these
areas, especially as these represent some of the best woodlands
remaining in Australia and are under significant threat from a variety
of human impacts, including climate change, tourism, mining, and
increased fire frequency, so if you want to see them you need to be
quick.
I’ve only mentioned the more conspicuous
eucalypts in each region and have ignored the mallees, which is an
injustice to the rich flora of the GWW (see Watson et al. 2008). Ted
and I began working in the GWW because we wanted to study a eucalypt
woodland avifauna that might still be intact. The GWW appeared to fit
this demand as a core 7.5m ha of its ~21m ha has never been grazed by
domestic stock and there was little evidence of feral goats, camels,
or rabbits away from pastoral and agricultural lands. Although the GWW
is hardly undisturbed, with more than a century long history of mining
and logging (pit props, timber, fuel-wood), including extensive
clear-felling, as well as mammal extinctions, I still think it comes
closer to having a pristine or original woodland avifauna than
anywhere else in Australia. However, this does not mean the avifauna
is unchanged. I am now of the view that nomadic and migratory species,
particularly nectar-feeders, have been adversely affected by the
clearing of the wheatbelt to the west and south of the GWW and by the
degradation of pastoral lands throughout the mulga country north and
east of the GWW. Although numbers of nomadic and migratory species can
at times be quite extraordinary, this does not mean they or any
particular species are abundant. Nomads and migrants commonly
congregate at particularly rich sources of food, such as flowering
eucalypts or outbreaks of psyllid insects (lerp), creating an illusion
of abundance, when in fact there are relatively few birds when the GWW
as a whole is taken into account. The really abundant birds in the GWW
are the residents, mainly sedentary species, such as Weebill, Inland
and Chestnut-rumped Thornbill, Redthroat, and Yellow-plumed
Honeyeater. These occur throughout the GWW, often in considerable
densities.
We had a primary goal of coming to
understand and quantifying the ecology of eucalypt woodland birds,
with the aim of using this information to better inform conservation
management of eucalypt woodlands throughout Australia. While there has
been considerable research on birds in Australia, we really know very
little about the details of their lives, the foods they eat, where
they feed, how they use or do not use different kinds of plants for
foraging and nesting, how abundant they are, how numbers change with
time or in response to drought and fire, when and where they nest, and
so on. Moreover, some of the most widely accepted facts about even
common Australian birds are just plain incorrect, but are perpetuated
from one generation to the next because there are really very few
people who take the time to study birds in the wild. The approach Ted
and I took was to concentrate on avian foraging behaviour (how and
where birds foraged and the foods they ate) for all species
encountered. Our procedures are described in the references given
below. We worked mainly from late winter to late spring as this was a
time we could also obtain information on breeding and nesting and
because is a time when numbers of birds are relatively stable. We’d
be the first to admit that much more needs to be known about our birds
during winter and summer; summer in particular. Spring is also an
efficient time to work as it is relatively cool and birds are active
for long periods during the day. Obtaining foraging data is therefore
relatively easy. By including all species and having multiple sites
(we have more than 80 plots in the GWW) we can quickly acquire
quantitative natural history information for a large number of
species.
Natural history information is the backbone
of ecological research from which testable theories and models are
derived. It is also the core of good conservation management, but not
enough is done these days in Australia with the emphasis on
experimentation, experimental design, computer modelling, and
statistical analysis. Too much time is spent in the cloisters and not
enough in the field. We no longer teach natural history at school or
university, with the result that increasingly few Australians have any
understanding or regard for their environment or concern for other
species. This includes many biologists and people being trained in
resource and environmental management.
I’m probably digressing here, but I think
understanding why people do research is as important as understanding
how they do it.
In all of the GWW there are about 215
species of birds, including water and wading birds (Watson et al.
2008), but I consider this an overestimate. Keeping in mind that we
only work in eucalypt woodlands and exclude mallee and shrublands from
our studies, Ted and I have recorded 86 species of birds on our plots
at Yellowdine, Widgiemooltha, and Norseman. Foraging and nesting data
have been obtained for most of these.
Not all species occur in all of those
localities and most make quite specific habitat choices. Many, more
mature and closed woodlands, especially those with Dundas Blackbutt
and Red Morrell, are dominated by Yellow-plumed Honeyeaters, which
exclude most smaller birds, such as Weebills, pardalotes and
thornbills from their colonies. Thornbills, in particular, are most
abundant in the more open woodlands with a well developed and species
rich understorey and shrub layer. So long as there is a eucalypt
canopy with lerp and no Yellow-plumed Honeyeaters, there will be
Weebills and Striated Pardalotes. Gilbert Whistler appear most
frequently where there is an abundance of Exocarpos
aphyllus and feed heavily on Exocarpos
fruit at all stages of ripeness (Davis and Recher 2009). Similarly
we only find an abundance of nectar-feeders where eucalypts are in
bloom. Eucalypts are almost the only source of nectar on our plots and
provide the only really rich flows of nectar. The recent prolonged
drought in the GWW has meant reduced numbers of nectar-feeders, both
honeyeaters and Purple-crowned Lorikeet, and raises the question of
where these birds go when nectar is not available in the GWW. I
suspect many used to move west and south into higher rainfall zones
where there is a greater variety of nectar-rich plants, but much of
this land has been cleared for farming. It is likely that the numbers
of nectar-feeders in the GWW were reduced many years ago, as the
wheatbelt was cleared; the abundance of a species will always be
determined by the least abundant resource. In the instance of
nectar-feeders in the GWW, that would be nectar during times of
drought.
The drought in the GWW has also affected
other birds, with ground-foraging species, such as Chestnut-rumped
Thornbill, Dusky Woodswallow, and Rufous Treecreeper, showing signs of
decline since 2003/2005. Others, such as Inland Thornbill, have
shifted their foraging habits and now feed higher in the canopy.
Presumably eucalypts are better able to maintain productivity during
drought and will therefore sustain invertebrates as food for birds
longer, but that is really a hypothesis, not an answer. In 2008, food
chasers, such as trillers failed to appear, and now some of the canopy
foraging insect-eaters, such as Black-faced Cuckoo Shrike are present
only in greatly reduced numbers. The absence of big flocks of
nectar-feeders also led to the decline of birds of prey, such as
Little Falcon and Brown Goshawk.
Drought, of course, leads to fire and in
2006 we set up a study to monitor the recolonization of woodlands
burnt in a wildfire north of Norseman in December 2005. Our aim was
not just to record what species and when birds return to the burnt
area, but how each species uses the new vegetation for foraging and
nesting. I’ve conducted extensive post-fire studies on birds in
eastern Australia and have never encountered anything so different as
the post-fire environment on those Norseman plots. Recovery is slow,
with many trees killed and regrowth occurring from seeds and
lignotubers, with almost no epicormic growth. Five years post-fire and
the birds using the burnt area are a tiny subset of the original
avifauna, as judged by the birds in adjacent unburnt forest. It will
be decades or longer before a complete woodland avifauna is recovered
highlighting the long-term consequences of more fires from more
frequent drought with climate change and from simply having more
people, more tourists, more miners, more bird-watchers using the GWW.
This is probably enough for you to have an
idea of what Ted and I have been doing in the GWW. Details can be
found in the papers we've published and you can also find an overview
of the application of our studies in Recher et al. (2010). The bulk of
our work is now being prepared for a book, as I am fed up with the
long delays, especially from referees, encountered with publishing in
most scientific journals and the need to assign copyright to
multinational publishing houses. You can also probably guess my
disdain of referees who seem to think natural history studies do not
merit publication unless accompanied by tedious and unnecessary
statistical analyses. Ted and I have either paid for our research
ourselves or it has been paid for by you and other tax payers and
should not be used for profit by big (or small) corporations. If our
original goals and aims in this research are to be achieved, then our
work must not only be published, but it must be free and freely
available to everyone needing or wanting to use it.
Harry F. Recher
Edith
Cowan University
School
of Natural Sciences, Joondalup, WA 6027
email:
hjrecher@bigpond.com
Davis,
W. E., Jr. and Recher, H. F. (2009) Use of native cherry (Exocarpos aphyllus) (Santalaceae) by birds in the Great Western
Woodlands, Western Australia. W.
A. Naturalist 26: 278-283.
Recher,
H. F. and Davis, W. E. 1998. Foraging profile of a wandoo woodland
avifauna during spring. Australian
Journal of Ecology 23, 514-28.
Recher,
H. F. and Davis, W. E. 2002. Foraging profile of a Salmon Gum woodland
avifauna in Western Australia. J.
Royal Society of Western Australia 85(2), 103-111.
Recher,
H. F., Majer, J. D. and Davis, W. E., Jr. (2010) The eucalypt woodlands
of Western Australia – Lessons from the birds. pp. 63-72 in
‘Temperate Woodland Conservation and Management’. ed by D.
Lindenmayer, A. Bennett, and R. Hobbs. CSIRO Publ., Collingwood.
Recher,
H. F. and Davis, W. E., Jr. (2010) The foraging behaviour of woodland
birds along the mulga-eucalypt line in Western Australia during late
winter and spring. Amytornis 2:
29-41
Recher,
H., Davis, W. Jr., Berry, S., Mackey, B. Watson, A. and Watson, J. 2007.
Conservation inverted: birds in the Great Western Woodlands. Wingspan
17:16-19.
Watson,
A., Judd, S., Lam, A., Watson, J., and Mackenzie, D. 2008. The
Extraordinary Nature of the Great Western Woodlands. The Wilderness
Society, Perth.