Cunninghamia : A Journal of Plant Ecology for Eastern Australia, Volume 8, Issue 3 (2004)
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A checklist of the mosses (Bryophyta) of the Wet Tropics bioregion, north-east Queensland is presented. Included is an update on the taxonomy of species, listing a total of 408 taxa. The habitat and distribution patterns of species within the area and in Australia, together with information on the phytogeographical affinities of these taxa in related areas beyond Australia, are discussed.
Floristic patterns along an east–west gradient in grassy box woodlands of Central New South Wales
(2004)
Temperate grassy box woodlands are the predominant native vegetation of the "wheat-sheep" belt of south-eastern Australia. In New South Wales, a number of different eucalypt species form the overstorey of these woodlands, with changes in dominance from Eucalyptus melliodora (Yellow Box) and Eucalyptus albens (White Box) in the east to Eucalyptus microcarpa (Grey Box) and Eucalyptus populnea (Poplar Box) in the west. Most grassy Box woodlands have now been cleared or modified for agriculture, and their conservation is dependent on adequate knowledge of the distribution, ecology and management needs of remaining woodlands. In this study we describe the understorey flora of high quality remnants of grassy Box woodlands along an east-west gradient in central New South Wales, comparing sites with a history of minimal livestock grazing (cemeteries) with sites with a history of intermittent livestock grazing (travelling stock reserves). With some important exceptions relating to Eucalyptus melliodora, dominant overstorey eucalypts were good indicators of understorey changes along the east-west gradient. A particular disjunction, involving changes in the dominant grasses from Themeda australis and Poa sieberiana to Austrostipa scabra, Austrodanthonia and Enteropogon species, distinguishes "eastern" (Eucalyptus melliodora, Eucalyptus albens) from "western" (Eucalyptus microcarpa, Eucalyptus populnea) Box woodlands, and has significant implications for understorey management. Notable changes in subsidiary species included changes in the main genera of shrubs and daisies, and a number of trends at the family level. Families such as Dilleniaceae, Haloragaceae, Epacridaceae and Ranunculaceae were more frequent or diverse in eastern Box woodlands, and gave way to species of the families Malvaceae, Chenopodiaceae, Myoporaceae, Amaranthaceae and Brassicaceae in the west. Intermittent grazing influenced understorey composition in all box woodlands sampled, although influences in western Box woodlands were less pronounced. Effects of grazing included a decline in shrub abundance and loss of a range of native perennials across all woodlands, changes to the dominant grasses and a considerable increase in exotic annuals in the east, and a decline in native grass diversity and increase in native annuals in the west.
Subalpine shrubs on rocky slopes on the Bogong High Plains, Victoria (36° 53’ S, 147° 19’ E), were observed to be severely desiccated over the summer of 2002/03 after a 50 day period when only 1.2 mm of rainfall was recorded. Moderate to severe canopy dieback was noted in shrubs growing on rocky north- and west-facing slopes. Four shrubs were assessed for their drought tolerance on west-facing slopes at Basalt Hill. Soils were rocky and uniformly shallow across the site (mean depth = 11.32 ± 0.69 cm). Prostanthera cuneata was the most drought tolerant species (as evidenced by the least amount of canopy dieback observed) followed by Hovea montana, Pimelea axiflora var. alpina and Epacris glacialis. All Epacris glacialis plants (n = 16) had died at the study location whereas no Prostanthera cuneata plants (n = 45) had canopy dieback that exceeded 60%. The amount of dieback observed was not significantly associated with either local soil depth or shrub canopy area. Hence, very small plants were not more susceptible to drought nor were shrubs found on the shallowest of the soils at the site. This suggests that drought effects are possibly dependent on local influences such as topography, drainage and competition intensity. Drought has only rarely been considered a major factor affecting the abundance and distribution of subalpine shrub species in Australia but this study suggests that it should be added to the list of abiotic factors governing the local dynamics of subalpine vegetation. In particular, the high mortality of Epacris glacialis observed in the study area suggests that non-equilibrium dynamics are likely to be the "norm" for some shrubs in subalpine areas.
In fire-prone grassy woodlands, fire response and time to reach reproductive maturity are two traits that can be used to provide an indication of the minimum interval between fires needed to maintain biodiversity. This study examined the effects of fire intensity and adult size on shrub mortality together with the primary and secondary juvenile periods of shrub species in the New England Tableland (NET) Bioregion. Most shrub species resprouted via basal lignotubers following fire, irrespective of fire intensity and shrub size. The primary juvenile period of most species was found to be greater than four years and the secondary juvenile period for most resprouting species was less than four years. These results suggest that a minimal interval between fires of eight years may be needed to maintain shrub species in grassy woodlands in the NET Bioregion, and that repeated fires at intervals of less than 8 years should be avoided. The time taken for shrubs in the grassy woodlands of the NET Bioregion to reach reproductive maturity appears to be longer than conspecifics in other Bioregions. Caution is needed when using data collected from outside a Bioregion to determine minimum fire frequency thresholds.
Montagu Island (36°15’S; 150°14’E) is situated about 10 km east of Narooma on the New South Wales South Coast. The paper presents evidence about the changes in the terrestrial vegetation of the island since it was first seen by Europeans, provides a floristic inventory and gives a perspective on the effects of introduced species.
Flinders (1814) mentions that the island "produced small trees." This is the only record of what grew on the island until in 1880 annotations on a map, made at the time of the construction of the lighthouse, mentioned the presence of scrub, trees and rank grass. This is confirmed by photographic evidence, but by 1932, when the botanist F. A. Rodway visited the island, the trees had disappeared. In 1973, during a land use survey of the South Coast, a team of CSIRO described the vegetation as a distinct series of dune communities belonging to the Lomandra longifolia – Pteridium esculentum – Phragmites australis complex. Vegetation mapping in the late 1980s confirmed the prevalence of these species, except that Pennisetum clandestinum then covered a large area along the west side of the island.
Excluding taxa used for ornamental or culinary purposes, nearly 200 species of vascular plants have been recorded since 1932 of which about 140 were still present in the late 1990s. There are ten species of ferns e.g. Pteridium esculentum, widespread and sometimes codominant with Lomandra longifolia, and Asplenium obtusatum, frequently found among the rocks along the east side of the island. The only taxon unique to Montagu Island is a hybrid of this species and Asplenium australasicum. Among the flowering plants there are about 110 native species and about 70 species naturalised in Australia. About 85 and 40, respectively, are still present today. Many of these have a wide distribution in Australia and only about 25 have a more restricted coastal distribution. The species that have disappeared include many that were weeds in the vegetable gardens or around the chicken sheds. Several naturalised species still present are notorious for their capacity to overrun existing vegetation. Foremost among these is Pennisetum clandestinum, which now covers about one-third of the island; Acetosa sagittata is a close second. Other contenders are Dipogon lignosus and Delairea odorata. It is now apparent that these species were kept in check by the feral goats that roamed the island before it was declared a Nature Reserve in December 1987.
Downey (1998) collated an inventory of mistletoe host species based on herbaria records for every aerial mistletoe species (families Loranthaceae and Viscaceae) in Australia. In this paper the representative nature of those host lists is examined in an extensive field survey of mistletoes and their host species in south-eastern New South Wales (including Australian Capital Territory). Four new host species not in the 1998 inventory, and eight new mistletoe-host combinations (i.e. a previously recorded host but not for that particular mistletoe species) were collected. These new records were distributed throughout the survey area. Interestingly, these new host-mistletoe combinations were for mistletoe species that were well represented in the national inventory (i.e. with many herbarium collections and numerous host species). The initial inventory was incomplete, at least for south-eastern New South Wales, indicating the need for (i) more targeted surveys similar to this one, and/or (ii) regular updates of the host inventory based on voucher specimens. A possible reasons why information on host-mistletoe combinations is incomplete may be that such combinations may be dynamic (i.e. mistletoe species may be expanding their suite of potential hosts, either fortuitously or as result of evolutionary pressures).
A study was undertaken of the floristic patterns in coastal rainforest (low closed forest) of Shoalwater Bay, central Queensland. The site encompasses 60 km of coastline, extending from latitude 22° 08’ 30’’ to 22° 30’ 0” and longitude 150° 02’ 00” to 150° 24’ 30”. The rainforest grows on coastal Holocene sand dunes, swales and sand flats, distributed as a series of 27 discrete patches greater than one hectare along 60 kilometres of coastline. Mean patch size was 10.7 hectares (maximum 150 hectares). The flora was predominantly woody, and lacked the complex growth forms of Webb (1968). Floristic links with central and north Queensland were strong, with some species distributions extending into Malesia and the Pacific. Three physical strata, emergent (composed of trees), canopy (composed of trees, vines and epiphytes) and sub-canopy (trees, vines and herbs) were recognised. The herb layer was very poorly developed. Eighty-one species were recorded, representing 42 families and 72 genera.
Sixty three quadrats were sampled across the rainforest patches to measure abundance of all vascular taxa using frequency score. Five floristic groups were defined from agglomerative classification analysis, one representing mixed forest, two representing low microphyll vine forest (LMVF) and two representing microphyll vine thicket (MVT). The vegetation at the study site was predominantly MVT. Five species groups were defined, one correlated with the mixed forest, one with the LMVF and one with the MVT. The remaining species groups represented ubiquitous and widespread species. Floristic patterns were found to be strongly influenced by three environmental variables using canonical correspondence analysis. The strongest variable was drainage, which separated the mixed forest from the vine forest/thicket. The LMVF/MVT vegetation forms a continuum along an environmental gradient, influenced by exposure to onshore-winds and landform height. The mesic/protected extreme was represented by the tallest LMVF situated in swales, whilst at the exposure/ elevation extreme was represented by wind-sheared MVT located on foredunes.
Werakata National Park (32° 50 S, 151° 25 E), near Cessnock in the Hunter Valley of New South Wales, conserves 2145 ha of mostly open forest vegetation, which was formerly widespread in the lower Hunter Valley. Six vegetation communities are delineated; Lower Hunter Spotted Gum – Ironbark Forest occupies most of the Park. All communities present are considered to be poorly conserved in the region and Werakata plays a critical role in the protection of these vegetation types. Two vegetation communities, Kurri Sand Swamp Woodland and Hunter Lowlands Redgum Forest, are listed as Endangered Ecological Communities under the NSW Threatened Species Conservation Act 1995, while others may warrant future listing. Considerable variation in the floristic composition of the Kurri Sand Swamp Woodland is apparent in the area and the implications are discussed. Populations of four vulnerable plant taxa — Callistemon linearifolius, Eucalyptus parramattensis subsp. decadens, Eucalyptus glaucina, Grevillea parviflora subsp. parviflora, and two rare plant taxa — Grevillea montana, Macrozamia flexuosa, together with several other regionally significant species occur within Werakata.
Recommendations are made on the conservation of plant taxa and vegetation communities in the Cessnock area, and on general reserve management. It is suggested that further areas be added to the reserve to consolidate and expand upon that which is already contained, particularly in regard to threatened species, and endangered and poorly conserved ecological communities.