The distribution and biology of the genus Coptotermes (Isoptera) in Western Australia.

1956 ◽  
Vol 4 (1) ◽  
pp. 19 ◽  
Author(s):  
JH Calaby ◽  
FJ Gay

Knowledge of the distribution and biology in Western Australia of species of Coptotermes has been very incomplete and in some respects erroneous, due partly to a lack of collecting and partly to the fact that the genus is notoriously difficult taxonomically. This genus, which includes the most destructive Australian termites, is represented in the State by four species and one subspecies. The form raffrayi previously thought to be a good species occurring sympatrically with acinaciformis is shown to be a subspecies of the latter form intergrading with it through a wide zone of intermediate forms and replacing it geographically in the wetter south-western corner of the State. C. michaelseni is restricted to south-western Australia and previous records from South Australia, Victoria, and Queensland are shown or considered to be misidentifications of C. frenchi. C. frenchi is definitely recorded from Western Australia for the first time. The separation of these two species by microscopical measurements is discussed. The fourth species is the recently discovered and described C. brunneus. The known Western Australian distributions of all species except C. brunneus are given. New biological data for all species are recorded, particularly on tree species attacked, dispersal of alates, and construction of mounds. C. acinaciformis builds symmetrical domed mounds in parts of southern Western Australia. Mound nests had not previously been recorded in 'the State and they differ considerably in construction from those recorded from the Northern Territory and north Queensland. C. frenchi is here definitely recorded as a mound builder. The mound-building habit erroneously attributed in the literature to C. michaelseni is shown to be due to the confusion of this species with frenchi. Photographs of mounds of C. acinaciformis raffrayi, C. frenchi, and C. brunneus are published for the first time.


1989 ◽  
Vol 29 (1) ◽  
pp. 72
Author(s):  
D.J. Gately

On 12 May 1988 amendments to the Queensland Petroleum Act of 1923 came into force. These empower the Governor- in- Council to appoint a Pipelines Tribunal to inquire into the operations of any existing or proposed pipeline. The Act now affirms the existence of the Secretary of Mines as a Corporation which can undertake all the aspects of an oil company from exploration to distribution of refined products. In particular, this corporation now has the sole right to construct and operate any pipeline in Queensland which extends beyond the boundaries of a lease. There was little or no dialogue with industry prior to the proclamation of these amendments.In comparison with the Petroleum Acts of South Australia, Western Australia and the Northern Territory, the Queensland Petroleum Act contains many areas subject to ministerial discretion or which are no longer relevant to present- day administrative practices. The Queensland Government's proposal to issue a green paper discussing amendments to the Act, based on submissions from interested parties, is welcomed since it is in the interests of management of the exploratory oil industry to strive for uniformity of administration in each state.



2016 ◽  
Vol 38 (2) ◽  
pp. 135 ◽  
Author(s):  
Donna Digby ◽  
Liz Bird ◽  
Lyndee Severin ◽  
Paul O'Leary ◽  
Mac Jensen ◽  
...  

Feral camels occur over almost 3.3 million km2 of the Australian rangelands, including parts of the Northern Territory, Queensland, South Australia and Western Australia. Within this range, pastoral land encompasses an area of 1.39 million km2 (1189 properties). The pastoral industry was identified as one of the key stakeholder groups to work with under the Australian Feral Camel Management Project. The impacts of feral camels fall into three main categories: economic, environmental and social/cultural. It should be noted that not all pastoralists were impacted by feral camels. Under the Australian Feral Camel Management Project, multiple approaches were used to engage the pastoral industry through their involvement in developing partnerships, operational planning, implementation and communication. Critical to the success of the project was the commitment to effectively consult with landholders, build partnerships, respect landholder values, establish effective project governance and adopt a flexible management approach.



Zootaxa ◽  
2020 ◽  
Vol 4832 (1) ◽  
pp. 1-75
Author(s):  
SVATOPLUK BÍLÝ ◽  
MARK HANLON

Taxonomic revision of the genus Bubastes Laporte & Gory, 1836. Thirteen new species are described: Bubastes barkeri sp. nov. (New South Wales, Queensland, Victoria), B. deserta sp. nov. (South Australia), B. dichroa sp. nov. (Western Australia), B. flavocaerulea sp. nov. (New South Wales, Queensland), B. hasenpuschi sp. nov. (Queensland), B. iridiventris sp. nov. (Western Australia), B. iris sp. nov. (Western Australia), B. macmillani sp. nov. (Western Australia), B. magnifica sp. nov. (Queensland, New South Wales), B. michaelpowelli sp. nov. (Western Australia), B. pilbarensis sp. nov. (Western Australia), B. remota sp. nov. (Northern Territory) and B. viridiaurea sp. nov. (Western Australia). The following seventeen new synonyms are proposed: Bubastes thomsoni Obenberger, 1928, syn. nov. = B. australasiae Obenberger, 1922, B. olivina Obenberger, 1920, syn. nov. = Neraldus bostrychoides Théry 1910, B. boisduvali Obenberger, 1941, syn. nov. = B. erbeni Obenberger, 1941, B. borealis Obenberger, 1941, syn. nov. = B. globicollis Thomson, 1879, B. laticollis Blackburn, 1888, syn. nov. = B. globicollis Thomson, 1879, B. simillima Obenberger, 1922, syn. nov. = B. globicollis Thomson, 1879, B. obscura Obenberger, 1922, syn. nov. = B. inconsistans Thomson, 1879, B. septentrionalis Obenberger, 1941, syn. nov. = B. inconsistans Thomson, 1879, B. viridicupraea Obenberger, 1922, syn. nov. = B. inconsistans Thomson, 1879, B. blackburni Obenberger, 1941, syn. nov. = B. kirbyi Obenberger, 1928, B. chapmani Obenberger, 1941, syn. nov. = B. kirbyi Obenberger, 1928, B. aenea Obenberger, 1922, syn. nov. = B. niveiventris Obenberger, 1922, B. saundersi Obenberger, 1928, syn. nov. = B. odewahni Obenberger, 1928, B. occidentalis Blackburn, 1891, syn. nov. = B. sphaenoida Laporte & Gory, 1836, B. persplendens Obenberger, 1920, syn. nov. = B. sphaenoida Laporte & Gory, 1836, B. splendens Blackburn, 1891, syn. nov. = B. sphaenoida Laporte & Gory, 1836 and B. strandi Obenberger, 1920, syn. nov. = B. suturalis Carter, 1915. Neotype is designated and redescribed for Bubastes cylindrica W. J. Macleay, 1888 and lectotypes are designated for Bubastes thomsoni Obenberger, 1928 and B. leai Carter, 1924. Morphological characters of the genus are presented and all species are illustrated (incl. historical types) and a key is provided for all species of the genus. 



Zootaxa ◽  
2006 ◽  
Vol 1304 (1) ◽  
pp. 31 ◽  
Author(s):  
ADRIAN M. PINDER ◽  
S. M. EBERHARD ◽  
WILLIAM F. HUMPHREYS

Four species of phallodriline tubificids (Clitellata: Tubificidae) from karst aquifers and caves along the west coast of the state of Western Australia are the first records of this subfamily from nonmarine waters in the southern hemisphere. Aktedrilus parvithecatus (Erséus 1978) and Pectinodrilus ningaloo n. sp. occur in anchialine groundwater of Cape Range, along with other taxa of marine affinity. Aktedrilus leeuwinensis n. sp. and Aktedrilus podeilema n. sp. occur in caves of the Leeuwin-Naturaliste Ridge and Perth Basin respectively and are the first taxa of marine lineage to have been collected from these systems.



Zootaxa ◽  
2009 ◽  
Vol 2029 (1) ◽  
pp. 1-70 ◽  
Author(s):  
DANNY TANG ◽  
BRENTON KNOTT

The Gnangara Mound is a 2,200 km 2 unconfined aquifer located in the Swan Coastal Plain of Western Australia. This aquifer is one of the most important ground water resources for the Perth Region and supports a number of groundwaterdependent ecosystems, such as the springs of Ellen Brook and root mat communities of the Yanchep Caves. Although freshwater copepods have been documented previously from those caves and springs, their specific identity were hitherto unknown. The current work formally identifies copepod samples collected from 23 sites (12 cave, three bore, five spring and three surface water localities) within the Gnangara Mound region. Fifteen species were documented in this study: the cyclopoids Australoeucyclops sp., Eucyclops edytae sp. nov., Macrocyclops albidus (Jurine, 1820), Mesocyclops brooksi Pesce, De Laurentiis & Humphreys, 1996, Metacyclops arnaudi (G. O. Sars, 1908), Mixocyclops mortoni sp. nov., Paracyclops chiltoni (Thomson, 1882), Paracyclops intermedius sp. nov. and Tropocyclops confinis (Kiefer, 1930), and the harpacticoids Attheyella (Chappuisiella) hirsuta Chappuis, 1951, Australocamptus hamondi Karanovic, 2004, Elaphoidella bidens (Schmeil, 1894), Kinnecaris eberhardi (Karanovic, 2005), Nitocra lacustris pacifica Yeatman, 1983 and Paranitocrella bastiani gen. et sp. nov. Tropocyclops confinis is recorded from Australia for the first time and A. (Ch.) hirsuta and E. bidens are newly recorded for Western Australia. The only copepod taxa endemic to the Gnangara Mound region are E. edytae sp. nov. (occurs primarily in springs and rarely in the Yanchep National Park Caves) and P. bastiani gen. et sp. nov. (confined to the Yanchep National Park Caves containing tuart root mats). Paracyclops chiltoni was the most common species, whilst T. confinis and N. l. pacifica were rarely encountered. Metacyclops arnaudi was the only taxon absent from ground waters. The copepod fauna recorded in the caves and springs of the Gnangara Mound region are comparable, with respect to species richness, endemicity and the varying degrees of dependency on ground water, to those reported from similar habitats in South Australia and Western Australia. Restoring the root mats and maintaining permanent water flow within the Yanchep Caves, as well as minimising urban development near the Ellen Brook Springs, are essential to protect the copepod species, particularly the endemic P. bastiani gen. et sp. nov. and E. edytae sp. nov., inhabiting these unique ground water environments.



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