Birds of “Carwoola”
Purpose of exercise
When we moved to Carwoola in
January 2007 I was pleased to find a regular article in the local news letter
“Stoney Creek Gazette” reporting on plants in flower in the area. I thought that the readership of the Gazette
might be interested in a similar column on birds. The editors agreed with me and I began
compiling a brief report on the birds I had seen each month.
Figure 1
The author at work (as seen by Wild Cattle Productions)
o
The initial reports were
effectively just a list of what I – and eventually others - had seen in the
area in the previous month but gradually included some commentary, varying
according to what I thought would be of interest to readers at the time. This occasionally included some references to
material in my blog, and when it became necessary to reduce the size of the
printed Gazette I reduced the hard copy to a very brief summary of highlights
and created a special blog for the detail.
The objective of the exercise
remains to inform local residents of what is happening with birds in the area,
and to encourage them to take an interest in this aspect of the natural
environment.
I maintain an ACCESS database of species recorded each month,
but not recording abundance or number of reports. This reflects:
·
the relatively ad-hoc nature of reports;
·
a recognition that most people do not wish to
commit to making detailed reports but are happy to note unusual sightings; and
·
the extra precision not being necessary for the
objectives of the study.
Of course, more formal reports
to the COG Atlas system or eBird (see below) contain full detail.
Metadata
What is the survey area?
The area covered by the reports
is effectively the catchment area of the Gazette. This includes the localities of Carwoola
(both Queanbeyan and Palerang components), Hoskinstown, Forbes Creek and
Primrose Valley and is illustrated in the sketch map below.
Figure 2
Sketch map of the study area
No part of Tallaganda National
Park or State Forest is included. The
edge of those areas is the Eastern edge of the survey area. The Northern edge is effectively a ridge parallel
to Briars –Sharrow Road and Captains Flat Road.
The Western boundary of the study area is the top of the Queanbeyan
escarpment meaning that most of Cuumbeun Nature Reserve is in the area, as are
Yanununbeyan State Conservation Area and Nature Reserve which form the Southern
end of the area.
Other than reports from
residents (see below) on their properties and forays into the public reserves
most of the birding is done from roads, either driving, jogging or cycling.
Key attributes
Most of the area is above the
750m contour line with some high points above 1000m. This means it is 200-400m higher than Central
Canberra. This often results in cooler
temperatures in the study area, and the Hoskinstown Plain (hereafter ‘the
Plain’) is effectively a large frost hollow.
Other than the public Reserves
the Northern half of the area is rural residential, with most blocks varying
from 4Ha to 25Ha in size. Most of the
Southern half of the area is contained in a few much larger commercial
properties.
A particularly interesting
phenomenon occurs in the Plain where woodland approaches the frost hollow from
both sides.
Figure 3
The ‘neck’ on the Hoskinstown Plain
This narrowing of the treeless area
has been the source of several sightings of unusual species, and seems to
reproduce the ‘point’ phenomenon in which migrating birds cluster at a point of
land, before moving across water. In
this case it might form a connection between Tallaganda to the East and
Yanununbeyan to the West. (Unfortunately
the observer who owned the property concerned has passed away so it no longer
gets daily attention, although parts of the area are visited approximately once
a month.)
There are many small farm dams
on the properties in the area and it is bisected by the Molonglo River. There are however very few large water
bodies. The best example, and the only
near‑permanent one, is a lagoon on Foxlow Station which can only be looked into
from a road some 400m away. In the past
much of the Hoskinstown Plain was a swamp but in recent years most of the area
has been much drier: when one swampy area (on private property) flooded in
2011-12 it provided an extraordinary range of observations, described under
case studies below. Unfortunately it has
been dry since.
Observer effort
For the first year or so the
reports were entirely my own observations.
Since then a variable number of other observers have reported, with
their efforts ranging from regular completion of an EXCEL spreadsheet to ad-hoc
reports of unusual or exciting single species sightings. This does mean that results from month to
month can be very variable. It is
particularly the case in July when many/all of the regular observers have gone
away for most of the month.
Between us we cover examples of
all the major habitat types, at least over the course of a year.
Relationship with other data collections
Myself and another observer maintain
COG Garden Bird Survey sheets for our home patches, data from which are
included in the monthly reports.
As the data is compiled on a
monthly basis and only covers presence/absence the material in my database is
not suitable for incorporating in either the COG data system or
Eremaea/eBird. However specific surveys
within the area do get submitted as with any other observations to whichever of
those systems the observer prefers. In
addition when a particularly interesting sighting is made by another resident I
encourage them to submit an ad-hoc report to one of the systems (or in some
cases make the submission on their behalf).
While the monthly time frame
could be accommodated by the Atlas of Living Australia, the area is
approximately 25km North-South and 16km east-West making it too coarse an area
to be useful in the Atlas. The same
comment applies to the Atlas of NSW Wildlife.
Comments on number of species observed
Species occurring
In the 8 years in which this project has been going 188
species have been recorded at least once in the study area. The number of species seen each calendar year
is summarised in Table 1.
Table 1 Number of species observed x Calendar Year
year
|
Count Of species
|
Notes
|
2007
|
106
|
Only one reporter
|
2008
|
116
|
|
2009
|
137
|
|
2010
|
146
|
|
2011
|
141
|
Low for unknown reasons
|
2012
|
150
|
|
2013
|
153
|
|
2014
|
150
|
|
2015
|
120
|
To end March
|
The number of species added each year is shown in Table 2,
and the pattern is shown in Figure 4.
Table 2 Number of species added x Calendar Year
Year
|
Additional species
|
Cumulant
|
2007
|
106
|
106
|
2008
|
19
|
125
|
2009
|
19
|
144
|
2010
|
17
|
161
|
2011
|
5
|
166
|
2012
|
11
|
177
|
2013
|
7
|
184
|
2014
|
2
|
186
|
2015
|
2
|
188
|
Figure 4
Cumulative number of species recorded in study area
As indicated by the value of R2 the series
of cumulative number of species recorded is a good fit to the quadratic trend function
represented by the red dashes. The
overall shape of the trend line is similar to many representations of time
series of observations, with a declining marginal rate.
Again the value for 2011 is below expectations:
possibly the low rainfall from March to October dissuaded ‘marginal’ species
from arriving in the area.
Species breeding
Commencing in 2009 I began
recording birds breeding in the area, using the COG set of breeding events and
codes. I also added in breeding records
from my GBS Chart for 2007 and 2008, mainly because the data was “just sitting
there”
In total 90 species have been
recorded undertaking some form of breeding activity in the area.
I have recorded species coded
to both the calendar year in which breeding was observed and the financial
year, which for most species gives a better break between the peak periods of
breeding activity. The number of species
recorded in each half year is shown in Table 3.
Table 3 Number of species
recorded undertaking breeding activity x Calendar half years
Breeding season
|
Observation Year
|
Number of species
|
2009-10
|
2009
|
28
|
2010
|
16
|
|
2010-11
|
2010
|
36
|
2011
|
30
|
|
2011-12
|
2011
|
40
|
2012
|
27
|
|
2012-13
|
2012
|
43
|
2013
|
16
|
|
2013-14
|
2013
|
44
|
2014
|
10
|
|
2014-15
|
2014
|
36
|
2015
|
12
|
The high number of species reported in the first half
of calendar 2011 (ie the second half of breeding season 2010-11) caused me to
re-examine the data. Nearly all the
records in that period were of dependent young so it appears that the very good
rains of October 2010 to February 2011 encouraged a number of species to fit in
a second brood. Looking at the results
for each complete breeding season, 2010-11 does not stand out from the
subsequent seasons.
Table 4 Number of species recorded undertaking breeding
activity x Breeding seasons
Breeding season
|
Number of species
|
2009-10
|
37
|
2010-11
|
50
|
2011-12
|
51
|
2012-13
|
49
|
2013-14
|
47
|
2014-15
|
41
|
Given that the breeding season for 2014-15 is
essentially complete at the time of writing I believe the low result for that
year reflects the unavailability of an observer, who is particularly good at
spotting breeding activity, in the first half of that season.
In terms of breeding activities, the number of species
and number records relating to various codes is shown in Table 5. The codes shown are those used by COG as
standard.
Table 5 Number and percentage of records x type of
breeding activity
code
|
# species
|
# records
|
% records
|
|
di
|
16
|
27
|
4.86
|
|
co
|
4
|
4
|
0.72
|
|
ih
|
7
|
11
|
1.98
|
|
nb
|
28
|
61
|
10.99
|
|
ne
|
6
|
9
|
1.62
|
|
on
|
38
|
90
|
16.22
|
|
ny
|
29
|
99
|
17.84
|
|
cf
|
12
|
12
|
2.16
|
|
dy
|
64
|
242
|
43.60
|
As expected the commonest code (43.6% of records) is for
Dependent Young. By way of contrast the
equivalent percentage for the Garden Bird Survey is 59%. I suspect the difference may reflect the fact
that most of the regular observers in this project are either retired or work
from their properties in the area (and thus spent a higher proportion of their
time on the study sites).
Relative to ACT
Impact of elevation
Due to the increased elevation of the area it could be
expected that events such as commencement of breeding or arrival of migrants
will be delayed by about 2 weeks compared to urban Canberra. Investigating that hypothesis is beyond the
scope of this report, but may be covered by a separate report.
Status of birds
The matter of whether a bird is
“officially unusual” is a major minefield and subject to change over time. For this report I have used a code in an
historic table which splits birds into three status groups equivalent to the
terms ‘common’, ‘uncommon’ and’ rare’ used in the COG Annual Bird report. While possibly out of date it is I believe
sufficient for this purpose. The status
of the 188 species recorded in Carwoola is shown in Table 6
Table 6 Number of species and
average number of months recorded x Frequency status.
Status
|
Number of species
|
Average number of months reported
|
Common
|
127
|
57.8
|
Uncommon
|
52
|
16.0
|
Rare
|
10
|
2.4
|
The project has been operating for 97 months
and thus the common birds average out being recorded in somewhat more the half
the months, while the rare species have only been recorded infrequently. A happy situation of expectations being met by
reality!
Common COGAOI birds
19 species have been reported in
every month of the project. They are marked
with a hash mark (#) in Appendix 1. All
of these are rated as Common in the COG status.
There are 14 species with a COG
status of “common” which have only been reported less than 10 months (which I
consider makes them at least uncommon) in Carwoola. It is possible to regard them in several
groups:
·
Birds of forests: While a good proportion of the
area is covered with woodland, there is little forest. Wonga Pigeon (Leucosarcia picata); Superb Lyrebird (Menura novaehollandiae); Satin Flycatcher (Myiagra cyanoleuca).
·
Waterbirds: The absence of large water bodies
has been noted above. Australian Pelican (Pelecanus
conspicillatus); Silver Gull (Chroicocephalus
novaehollandiae); Eastern Great Egret (Ardea
modesta). The third of these species,
recorded in only 6 months, offers an interesting contrast with the White-necked
Heron (Ardea pacifica), recorded in
47 months. Possibly this reflects the
differing diets with the Egret preferring fish and the Heron preferring other
small aquatic and terrestrial animals (Marchant and Higgins 1990)
·
Relatively infrequently reported in COG area:
Yellow-billed Spoonbill (Platalea
flavipes); Restless Flycatcher (Myiagra
inquieta – from chatline commentary appears to have been recorded more
frequently in the AOI in 2015); Rose Robin (Petroica
rosea); Brown Treecreeper (Climacteris
picumnus); Fuscous Honeyeater (Lichenostomus
fuscus); and Yellow‑tufted Honeyeater (Lichenostomus
melanops). The Annual Bird report for 2012-13 (COG 2014) ranks species by
number of records in the year: none of this group was in the top 120.
·
Not yet invaded Carwoola; Spotted Dove (Streptopelia chinensis); Little Corella
(Cacatua sanguinea). Observations of the Corella in Carwoola have
increased in 2014-15).
Uncommon COGAOI birds
I have identified 8 species
which are possibly more common in Carwoola (being seen in more than 30 months) than
implied by their COG status of uncommon.
Three of these are perhaps
marginal over-achievers. I mainly
identify Western Gerygone (Gerygone fusca:
reported in 34 months) by call and may have over-represented the species. Speckled Warbler (Chthonicola sagittata: also 34 months) is seen very irregularly in
Carwoola but when seen is often as a pair suggesting breeding activity in the
area. Southern Whiteface (Aphelocephala leucopsis: 47 months) has
become much harder to find in recent years despite checking previous hotspots.
However there is no doubt that the remaining 5 species are
more common in Carwoola than in the overall COG AOI . These are:
·
Grey Butcherbird (Cracticus torquatus 97 months – very common throughout the area,
and very young birds are frequently seen being fed in Spring, although no nest
has yet been found)
·
Little Raven (Corvus mellori 97 months very common on the Plain, at times in
flocks >100 birds. In the surrounding
more wooded areas they are not so frequent or numerous.)
·
Yellow-tailed Black Cockatoo (Calyptorhynchus funereus 96 months –
very common feeding in Pinus radiata
windbreaks);
·
Diamond Firetail (Stagonopleura guttata 70 months – very common in or near hawthorn
thickets especially on the Plain);
·
Eurasian Skylark (Alauda arvensis 63 months – but I am sure they are always present
on the Plain – they just don’t sing for a few months each year, and are hard to
identify when grounded.)
Rare birds
As shown above there are 10
species with a COG status of rare. 9 of
the species have been recorded only on the Plain – an interesting fact which
requires some further thought.
Three of these (Scarlet
Honeyeater Myzomela sanguinolenta,
Black-eared Cuckoo Chalcites osculans
and Scaly-breasted Lorikeet Trichoglossus
chlorolepidotus) have only been reported from the ‘neck’ site on the Plain. The Lorikeet was considered an escapee.
Plumed Whistling Ducks (Dendrocygna eytoni) have become regular
at sites in Bungendore but have only been recorded once – very recently in 2015
- on the Plain.
The appearance of Banded Lapwing
(Vanellus tricolor), Australian Painted
Snipe (Rostratula australis) and
Painted Honeyeater (Grantiella picta)
all coincided with a year of increased sightings of these species elsewhere in
the COG Area of Interest (AOI). The
Banded Lapwings (2012- 13) invaded a Lucerne crop with up to 45 birds present:
despite continued growing of Lucerne the species has not reappeared. In 2013 it was becoming ‘usual’ to see
Painted Snipe in Kelly’s Swamp but to flush two birds from a paddock full of Herefords
was truly surreal.
Figure 5
Australian Painted Snipe on the Hoskinstown Plain (image by Garry Moffit)
The Painted Honeyeaters bred in
a GBS site at Hoskinstown in 2013-14 but have not returned.
Two other species are simply
rare in both Carwoola and the AOI. Horsfield’s Bushlark
(Mirafra javanica) may well be not recorded due to its preference for rank
grass on the roadsides of the Plain where it is overlooked, especially as the
quiet song is mainly sung early in the morning. The single flock of Zebra
Finches (Taeniopygia guttata) were seen in a period of strong westerly
wind.
The final species, Masked
Woodswallow (Artamus personatus), could
be considered as at the margin for a status of rare in the AOI, although they
are less frequently seen in both areas than White-browed Woodswallows (Artamus superciliosus).
Case studies
The Swamp on the Plain [1]
I have referred above to an ephemeral swap on the
Plain. The presence of water - and
waterbirds – in the swamp was noticed in about March 2012 following 2 months of
very heavy rain. At its greatest extent the
water covered about 10Ha.
While the water was present the swamp was notable for
the presence of a number of species in larger than usual numbers and several
others which are not common in Carwoola.
As noted above, White-necked Heron are frequently
reported as individual birds but for a period there were up to 20 birds present
in this swamp, with a similar number of White-faced herons (Egretta novaehollandiae). Similarly Black-winged Stilt (Himantopus himantopus) are seen
irregularly, but not in numbers such as the 35 seen in this location on 29
October 2012! Eurasian Coot (Fulica atra) numbers peaked at an
estimated 100 birds
Hoary-headed Grebes (Poliocephalus poliocephalus) were added
to the area list here, with up to 20 birds.
2 Glossy Ibis (Plegadis
falcinellus) were the first (and so far only) reports for the area. Single Eastern Great Egret and Yellow-billed
Spoonbill seen in this event were also the first for the area.
Figure 6
A selection of birds on the Swamp
Of course, commoner species
were also present including 100 each of Pacific Black Ducks (Anas superciliosa) and Grey Teal (Anas gracilis), 10 Australasian Shoveler
(Anas rhynchotis), 20 Hardhead (Aythya australis) and a family of 5
Black Swans (Cygnus atratus). Although Australian Wood Duck (Chenonetta jubata) are common in the
area generally, this habitat was not favoured by them: they were recorded
infrequently and in small numbers.
The water had more or less
completely gone by mid 2013, leave a mass of reeds and other vegetation. While doubtless still enjoyed by the resident
Tiger Snakes (Notechis scutatus) the
birds had all departed.
Raptors
Carwoola has very good
diversity of both diurnal and nocturnal raptors. Following a sighting of a Black Kite (Milvus migrans) in 2014, all diurnal
raptors (except Eastern Osprey Pandion
cristatus) listed in the most recent Annual Bird Report have been sighted
in the area. All four Owls listed in the
report, and Tawny Frogmouth (Podargus
strigoides) and Australian Owlet-nightjar (Aegotheles cristatus) have been sighted (or, more frequently
in the latter case, heard).
Six species in this group have
been recorded breeding in the area.
Highlights of records of this group have been:
- · Frequent sightings of 1-3 Spotted Harriers (Circus assimilis) on the Plain, especially in wetter periods. The group of 3 included one apparently juvenile bird, but no nest site has been located;
- · Spotted Harrier hunting with Black Falcon (Falco subniger) possibly cooperatively, although one observer described the Falcon as ‘bullying’ the Harrier;
- · Large numbers of Black-shouldered Kite (Elanus axillaris up to 16 birds[2] in a single tree –all checked carefully to ensure it was this species) and Brown Falcon (Falco berigora possibly 20 individuals perched on and hunting from fence posts around one paddock) were seen during a mouse plague on the Plain in 2011
Figure 7
Flock of Black-shouldered Kites, Carwoola 2011
- · Up to 4 Eastern Barn Owls (Tyto javanica) were seen hunting along Plains Rd in one drive following the end of a mouse plague ‘further West’. The Hawthorns along that road provided convenient roost sites for the owls.
Eastern Yellow Robin
The basic situation of Eastern
Yellow Robin (Eopsaltria australis) is
stated by Wilson 1999 “The stronghold of this species is the moist forest of
the western ranges but it occurs in smaller numbers wherever there is dense
vegetation in wet gullies and along watercourses.” A prime example of the latter habitat is
given by the Australian National Botanical Gardens (ANBG): it is almost
impossible for an alert birder to visit ANBG without seeing or hearing this
species.
However references to “moist
gullies” do not immediately conjure up an image of the Grassy Box woodland (at
best) of Carwoola. For the first three
years of the project it was hardly recorded, and I think the few sightings made
were in the more densely vegetated areas of Yanununbeyan SCA.
Then starting in September 2010
a member of the species was reported from a property in Widgiewa Rd (about 1km up
Whiskers Creek from our property). In
December 2010 I recorded a single bird in a clump of dense Cypress at our
house. I have recorded 1 or 2 birds most
months since then (there is no discernible pattern in the missing months).
Table 7 Eastern Yellow Robin Number of months
recorded x year
year
|
# months
|
2007
|
1
|
2008
|
2
|
2009
|
2
|
2010
|
4
|
2011
|
10
|
2012
|
10
|
2013
|
10
|
2014
|
11
|
2015
|
3
|
In December 2013 I observed a
bird carrying food, and in December 2014 4 birds were present in the Cypress,
but no exchange of food was seen.
However I am confident that they are now breeding in the dense foliage
of the Cypresses.
I am not sure whether it is
possible to extrapolate from this observation and generalise about the benefits
of small islands of habitat-type as a basis for range expansion.
Tawny Frogmouth
I have reported several times
(eg Butterfield 2011) on my observations of a pair of Tawny Frogmouths which reside
and breed in our garden and a summary of observations follows. (In passing, I have no way of knowing if they
are the same birds but as they use the same daytime roosts year after year it
seems sensible that at least one of the pair is the same bird.) I have also sighted other members of this
species on more distant parts of our property, and several other observers in
other parts of the study area have reported sightings of the species from time
to time.
As I have become more familiar
with their habits I have had greater success in locating the birds – Typically
I find the male on about 75% of days on which I am home and of these about 25%
are when he is brooding (and thus guaranteed to be on the nest). The female tends to be a little more of a
free spirit although on 90% of the days when located (outside the breeding
period) the two birds are snuggled together.
When they have had ‘a domestic’ and are roosting separately I have found
them up to 70m apart.
They have been very successful
in breeding raising 2 chicks to independence 6 years out of 7. In the other year one chick fell out of the
nest and died before it was discovered.
I have now found them using 33
different daytime roost sites within my GBS site. They have roosted in ornamental Hazels and
Elms and Acacia dealbata. The two nest sites have been Eucalyptus meliodora (5 years) and E. macrorhyncha (2 years) and those
species have been their preferred daytime roosts with occasional visits to E. mannifera.
While not an extensive survey,
such as those reported by Kaplan 2007 or blogged by Stuart Rae, hopefully the
daily observations, made possible by my being retired, contribute somewhat to
an understanding of the species.
Introduced
species.
I have used this heading to
refer to a group of 6 species native to Europe or Asia found in the ACT and
Carwoola. In terms of their perception
by many birders they could be described as “pest species’. Notes on each species follow.
Spotted Dove This
species is becoming increasingly common in the ACT, but has only been reported 3
times in Carwoola. It is unclear to me
why the species is not recorded more often in the study area as:
- · Crested Pigeons have spread here as readily as elsewhere in the COG AOI; and
- · I believe the Spotted Dove has self-introduced to the ACT and must therefore have bridged over the gap to other populations.
House sparrow (Passer domesticus): A species in
world-wide decline, which is still in the top 10 in terms of abundance in the
GBS. While reported in 94/97 months most
observations are very close to housing, usually properties with fed stock such
as horses.
Common Myna (Sturnus tristis): The species continues
to decline in the Canberra area (GBS rank in the high teens) and has not thus
far become established in the Carwoola area.
It has only been recorded in 17/97 months and again mainly associated
with fed livestock.
Common Starling (Sturnus vulgaris): Numbers are declining in Canberra, but still
very common in Carwoola (seen every month), but more so on the Plain than in
the wooded areas (although an area of very old Eucalyptus mannifera on the edge of the Plain provides many nest
hollows well used by this and other species).
Often sighted in huge flocks especially when the Hawthorns are in fruit.
Common Blackbird (Turdus merula): Quite common, being seen
in 82 months. It seems to prefer areas
close to houses with dense garden plantings.
European Goldfinch (Carduelis carduelis): Quite common,
being seen in 87 months. The species appeared to be in decline in the area,
only being reported in 8 months in 2010.
That may have been a response to the drought as it has since recovered
and is reported nearly every month. A
broadly similar pattern is evident for the COGAOI (although the current
reporting rate is still well below the levels achieved in the “Atlas years” of
the late 1980s.)
Summary
This review of my records has
shown considerable similarity between the avifauna of the Carwoola area and
rest of the COG AOI. Given the small
number of observers and the relatively brief time frame of this project I
believe that having at least one record for 188 species is a good result. Noting those constraints and the lack of some
habitats in the area, recording approximately 150 species per year compares
satisfactorily with the record of 241 species recorded in the COGAOI in 2012-13 (COG 2014).
Most of the noticeable differences
can be attributed to differences in habitat including absence of forested areas. Within the Carwoola data there is an apparent
relationship to weather, especially for the waterbirds group, reflecting the
ephemeral nature of larger waterbodies.
As might be expected in
compiling the report I have gained insights to what has been recorded over the
period. In particular the analysis has
emphasised the number of species for which the grassland, both native and
introduced, of the Hoskinstown Plain is an important location. Another important factor has been the fact
that many people in the area spend a relatively high proportion of their time
“out on the block” and report on the birds seen. In contrast some parts of the AOI get no
visits in a year (at least not from people prepared to put in a record of the
birds seen).
It would be good to have more
data so as to be able to analyse the birds of the area more rigorously (for
example to compare the birds seen in reserves with those on the rural
residential blocks with those on the commercial properties). That isn’t the case and so it is hoped this
overview has given a summary of the situation as it has been observed.
To provide a level of
privacy for observers I do not attribute
names in my reports. However I offer my
thanks for the contributions to this project by
the observers and landholders in
Captains Flat Rd Hoskinstown (Plain and
village); Knox Close, Pony Place, Radcliffe Circuit, Walga Close, Wanna Wanna
Rd and Widgiewa Rd.
References
Butterfield M. 2011 Tawny
Frogmouth and Pied Currawong nesting at Carwoola 2011, Canberra Bird Notes v36, No.3
COG 2014 Canberra Bird Notes:
Annual Bird Report 1 July 2012 to 30 June 2013
Kaplan G 2007 Tawny Frogmouth
Marchant S and P J Higgins
(eds) 1990 Handbook of Australian, New Zealand and Atarctic Birds Vol 1
Ratities to Ducks, pt B
Wilson S 1999 Birds of the ACT
Two Centuries of Change
Appendix 1: Complete list of species recorded in
Carwoola;
February 2007
– April 2015
The species marked with a hash (#) are those recorded in
every month.
Emu
|
Stubble
Quail
|
Brown
quail
|
Plumed
Whistling Duck
|
Musk
duck
|
Freckled
Duck
|
Black
Swan
|
Australian
Shelduck
|
# Australian
Wood Duck
|
Pink-eared
duck
|
Australasian
Shoveler
|
Grey
Teal
|
Chestnut
Teal
|
Pacific
Black Duck
|
Hardhead
|
Australasian
Grebe
|
Hoary-headed
Grebe
|
Rock
Dove
|
Spotted
Dove
|
Common
Bronzewing
|
Crested
Pigeon
|
Wonga
Pigeon
|
Tawny
Frogmouth
|
Australian
owlet-nightjar
|
White-throated
Needletail
|
Fork
tailed swift
|
Darter
|
Little
Pied Cormorant
|
Great
Cormorant
|
Little
Black Cormorant
|
Australian
Pelican
|
White-necked
Heron
|
Great
Egret
|
Intermediate
Egret
|
Cattle
Egret
|
White-faced
Heron
|
Nankeen
Night Heron
|
Glossy
Ibis
|
Australian
White Ibis
|
Straw-necked
Ibis
|
Royal
Spoonbill
|
Yellow-billed
Spoonbill
|
Black-shouldered
kite
|
White-bellied
Sea-eagle
|
Whistling
Kite
|
Black
Kite
|
Brown
Goshawk
|
Collared
Sparrowhawk
|
Grey
Goshawk
|
Spotted
Harrier
|
Swamp
Harrier
|
Wedge-tailed
Eagle
|
Little
eagle
|
Nankeen
kestrel
|
Brown
Falcon
|
Australian
Hobby
|
Black
Falcon
|
Peregrine
falcon
|
Purple
swamphen
|
Australian
Spotted Crake
|
Spotless
Crake
|
Dusky
Moorhen
|
Eurasian
Coot
|
Black-winged
Stilt
|
Black-fronted
dotterel
|
Red-kneed
Dotterel
|
Banded
Lapwing
|
Masked
Lapwing
|
Painted
Snipe
|
Latham's
Snipe
|
Painted
button-quail
|
Whiskered
tern
|
Silver
Gull
|
Glossy
Black-Cockatoo
|
Yellow-tailed
Black-cockatoo
|
Gang-gang
cockatoo
|
# Galah
|
Little
Corella
|
# Sulphur-crested
cockatoo
|
Scaly-breasted
Lorikeet
|
Australian
King-parrot
|
Superb
Parrot
|
# Crimson
Rosella
|
# Eastern
Rosella
|
Red-rumped
parrot
|
Australian
Koel
|
Channel-billed
Cuckoo
|
Horsfield's
Bronze-Cuckoo
|
Black-eared
Cuckoo
|
Shining
Bronze-cuckoo
|
Pallid
Cuckoo
|
Fan-tailed
Cuckoo
|
Brush
Cuckoo
|
powerful
owl
|
Barking
Owl
|
Southern
boobook
|
Eastern
Barn Owl
|
# Laughing
Kookaburra
|
Sacred
Kingfisher
|
Rainbow
Bee-eater
|
Dollarbird
|
Superb
lyrebird
|
# White-throated
treecreeper
|
Brown
Treecreeper
|
Satin
bowerbird
|
Superb
Fairy-wren
|
White-browed
scrubwren
|
Chestnut-rumped
Heathwren
|
Speckled
warbler
|
Weebill
|
Western
gerygone
|
White-throated
gerygone
|
Striated
thornbill
|
Yellow
thornbill
|
# Yellow-rumped
thornbill
|
Buff-rumped
thornbill
|
Brown
thornbill
|
Southern
whiteface
|
Spotted
pardalote
|
Striated
pardalote
|
Eastern
spinebill
|
Yellow-faced
honeyeater
|
# White-eared
Honeyeater
|
Yellow-tufted
honeyeater
|
Fuscous
Honeyeater
|
White-plumed
Honeyeater
|
# Noisy
Miner
|
Red
wattlebird
|
Scarlet
Honeyeater
|
Crescent
Honeyeater
|
New
Holland Honeyeater
|
Brown-headed
honeyeater
|
White-naped
honeyeater
|
Noisy
friarbird
|
Painted
Honeyeater
|
Spotted
quail-thrush
|
Varied
Sittella
|
Black-faced
cuckoo-shrike
|
White-winged
triller
|
Golden
whistler
|
Rufous
whistler
|
Grey
shrike-thrush
|
Olive-backed
oriole
|
Masked
Woodswallow
|
White-browed
woodswallow
|
Dusky
woodswallow
|
# Grey
butcherbird
|
# Australian
Magpie
|
# Pied
Currawong
|
Grey
currawong
|
Rufous
Fantail
|
Grey
fantail
|
# Willie
wagtail
|
# Australian
Raven
|
# Little
Raven
|
Leaden
flycatcher
|
Satin
Flycatcher
|
Restless
Flycatcher
|
# Magpie-lark
|
White-winged
chough
|
Jacky
Winter
|
Scarlet
robin
|
Red-capped
Robin
|
Flame
robin
|
Rose
Robin
|
Hooded
Robin
|
Eastern
Yellow Robin
|
Horsfields
Bushlark
|
Skylark
|
Golden-headed
Cisticola
|
Australian
Reed-warbler
|
Rufous
songlark
|
Brown
Songlark
|
Silvereye
|
# Welcome
swallow
|
Fairy
Martin
|
Tree
Martin
|
Common
blackbird
|
# Common
starling
|
Common
Myna
|
Mistletoebird
|
Zebra
Finch
|
Double-barred
finch
|
Red-browed
finch
|
Diamond
Firetail
|
House
sparrow
|
Australasian
pipit
|
European
goldfinch
|
[1] For additional commentary see http://carwoolabirds.blogspot.com.au/2013/01/glossy-ibis-on-plain.html and http://carwoolabirds.blogspot.com.au/2012/10/a-swampy-day.html
[2]
http://franmart.blogspot.com.au/2011/09/large-flock-of-black-shouldered-kites.html