The Status of Herons and Their Wetland Habitat in Southeastern Australia, 2000-2010

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The Status of Herons and Their Wetland Habitat in Southeastern Australia, 2000-2010 Copyright © 2011. Maddock, M. 2011. The status of herons and their wetland habitat in southeastern Australia, 2000-2010. Journal of Heron Biology and Conservation 1:7 [online] www.HeronConservation.org/JHBC/vol01/art07/ The status of herons and their wetland habitat in southeastern Australia, 2000-2010 Max Maddock 78 Ballydoyle Dr., Ashtonfield, NSW 2323 Australia; [email protected] Abstract This paper presents an update on the status of herons in southeastern Australia from 2000 to 2010, with emphasis on the situation in the Murray-Darling Basin river system. During the period, four major stud- ies contributed to an enhanced understanding of heron biology and conservation of herons in Australia. In the Lower Hunter Region of New South Wales, Rufous Night Herons (Nycticorax caledonicus) have not been recorded as a breeding species following the destruction of their colony site in the 1980’s. Since 2000, there has been little action with regard to the conservation of the Australasian Bittern (Bo- taurus poiciloptilus), listed as Endangered by IUCN and as Critically Endangered by the Heron Special- ist Group. The federal government listed the species as nationally Endangered in 2011, but otherwise, little has been done to stop habitat destruction of specific sites. Two studies of the Cattle Egret, the Lockyer Valley Cattle Egret (Ardea ibis) study and the Project Egret Watch study of the two Lower Hunter colonies (Seaham and Shortland colonies) provide considerable information on the changing sta- tus of this species. Nesting populations in the Lower Hunter Valley decreased precipitously as critically important wetland sites became adversely affected by development pressures. The Murray-Darling river system traditionally provided major support of nesting and year round activities of the four species of egrets, three of bitterns and three of other herons, as well as other waterbirds. Drought and bad water management created water shortages and adversely affected heron numbers through 2006. Thereafter, overall favorable conditions for breeding and foraging returned and threats from water management were substantially reduced. Despite nesting success in response to floods and recent moves by some rur- al property owners to be proactively supportive of the water birds, the overall assessment is of a bleak future for Australian herons due to lack of governmental and popular support for sound environmental policies. The situation is still volatile due to continued political conflict and a finding in a new study re- leased as this report was going to press that previous estimations of flooding extent in the basin had been over estimated. Key words: Ardea; Botaurus; conservation; egrets; Egretta; Murray-Darling; New South Wales; Nyctico- rax; populations; wetlands. Journal of Heron Biology and Conservation 1:7, page !2 Introduction ticipated. Maddock (2000) summarized the status of herons in Australia as part of a global assessment of Results and Discussion heron conservation (Kushlan and Hafner 2000). The purpose of the present paper is to provide an Significant studies. Since 2000, four major stud- update of the breeding populations of key species ies have expanded the knowledge of heron biolo- through the end of the first decade of the 21st gy and conservation. century. This update discusses the current status of the populations, the habitat on which they de- McKilligan (2001) studied Cattle Egret nesting in pend, and the complex socio-economic and polit- the Lockyer Valley, Queensland. Cattle Egrets ical influences that have affected them. started nesting in the area in the 1974/75 season. The study encompassed the 20 years from 1979 Maddock (2000) concluded that there was a de- to 1998 and is an important example of the value creasing trend in breeding numbers of Eastern of long-term research in understanding processes Great (Ardea modesta), Intermediate (Ardea in- at work in controlling fluctuations in numbers of termedia), Little (Egretta garzetta) and Cattle nests and breeding success. (Ardea ibis) egrets in coastal New South Wales (NSW) colonies and recommended that conser- McKilligan (2005) filled a gap in Australian lit- vation status of the Great, Intermediate and Little erature. This was the first book to deal exclusive- Egrets should be raised to vulnerable. He sug- ly with the 14 Australian species of Ardeidae, gested that the erratic nature of breeding of the covering distribution, movements, feeding, breed- Rufous (Nankeen) Night Heron (Nycticorax ing, population dynamics and conservation. The caledonicus) in its major nesting areas in the publisher’s description of the book on the back Murray-Darling Basin and the continued overall cover described the chapter on population and decline of the water regime of the basin could conservation as a useful summary of the status of have long term consequences for its population. the species, some thriving and others in a very He also noted that very little was known at that precarious position, with northern Australia ac- time about the Australasian Bittern (Botaurus commodating large numbers of certain species, poiciloptilus). He pointed out the serious plight but the southern half of the continent having of the water regime of the Murray-Darling Basin, some species which had become very scarce and historically a major breeding area for herons and were at risk of local extinction. other waterbirds, and discussed its associated controversies and the resultant decline in water- Maddock (2008a) provided a comprehensive his- bird nesting. torical review of the growth of the Seaham and Shortland nesting sites from their establishment The present contribution documents that the situ- in the late 1970’s onwards until 2008. The report ation has worsened since that 2000 paper. The details the record of the rise of the Great, Inter- precipitous decline in the egret nesting popula- mediate, Little, and Cattle egrets until 1989, fol- tion in the Hunter Region of NSW is continuing lowed by a short, rapid downward plunge be- as part of a general pattern of ecological degrada- tween 1989-1995, and then a fluctuating but tion of wetlands. The further catastrophic col- overall declining trend thereafter (a warning lapse of the Murray-Darling ecosystem due to trend that the tipping point to local extinction political and sociological antagonism is to be an- may have been imminent). It includes a mapping Journal of Heron Biology and Conservation 1:7, page !3 of the changes over time of nest locations within area from that time through the 1980’s. Limited the two colonies and an analysis of the possible data available suggests a moderate recovery in impacts on the declining egret nesting popula- numbers at the Wetlands Centre, but not to the tions by a steadily increasing White Ibis nesting levels prior to 1972. No nesting has been record- population which began at Shortland in 2004. It ed anywhere in the Lower Hunter Region since also reviews the changes in the Straw-necked the demise of the original Kooragang colony. The (Threskiornis spinnicolis) and White Ibis (Thres- results from regular monitoring of Rufous Night kiornis aethiopicus) populations, which share the Heron numbers at Wallbridge Reserve, Raymond same wetland habitat with the egrets. Terrace since 2003, taken in conjunction with records of the herons present in the Shortland Maddock (2008b) provides a comprehensive his- egret colony during the nesting seasons, pointed torical review of the literature and monitoring to an annual departure of the birds from the re- data on the conservation issues involved in the gion to an unknown breeding site or sites else- continuous decline in ecological characteristics where. The Murray-Darling system would have of Lower Hunter (NSW) regional wetlands for to be a prime candidate as their destination. more than 200 years. Natural estuarine shorelines and floodplain wetlands have been altered, de- Despite regular monitoring for the presence of stroyed, drained, filled and severely degraded for Rufous Night Herons during the Shortland egret industrial and urban development to the detri- nesting season (nest counting 1981/82-2009/10 ment of flora and fauna, a process which acceler- and the annual program of wing-tagging egrets ated from the 1970’s onwards. The degradation 1995-2004), no nests were discovered, although occurred in both protected reserves and unpro- the species was regularly seen and recorded in tected areas alike. It resulted in negative impacts evening observations during winter, often in large on key, highly threatened species which require numbers. In the 2009/10 nesting season, 7 nests essential interactive ecological processes across a were located in tall trees on a property adjacent wide range of sites and disrupted critical conser- to the Shortland colony, reported as “the first vation management effort. In recent years, failed confirmed nesting for several decades” (Stuart and ecologically inappropriate compensatory off- 2009, p. 27). However, no nesting was located in set projects have become the norm. Case studies the 2010/11 season. include the Australasian Bittern as well as other waterbirds and demonstrate the vital role of The weekly monitoring program was maintained maintenance of the wider wetland ecological sys- during 2001-2010 at the Rufous Night Heron day tem for all species and all phases of the life cycle roost site at the Wallbridge Reserve, a local of these birds. Photographic evidence illustrated council reserve at Raymond Terrace near the the progressive degradation of the ecological junction of the Hunter and Williams Rivers. It characteristics of both the Seaham and Shortland revealed that numbers fluctuate year to year but wetlands up until 2008. in general show a pattern of low numbers in Jan- uary-April increases over the winter months, Rufous Night Heron. Maddock (2008a) con- June-August, and then a declines again to the end cluded that the status of the Rufous (Nankeen) of the year. The highest maximum number on Night Heron in the study area was somewhat ob- record was 85 in November 2004, the next high- scure.
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