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FIGURE 12 in A new dasyurid marsupial from Kroombit Tops, south-east Queensland, Australia: the Silver-headed Antechinus, Antechinus argentus sp. nov. (Marsupialia: Dasyuridae)
FIGURE 12. Scatterplot of posterior palatal vacuity length (PPV) versus skull width level with the junction of the second and third upper molar (R-LM2) measures for male A. argentus (closed circles) and A. stuartii (open triangles).
FIGURE 2 in First Report of Sabella spallanzanii (Gmelin, 1791) (Annelida: Polychaeta) from Botany Bay, New South Wales, a northern range extension for the invasive species within Australia
FIGURE 2. Diagnostic features of Sabella spallanzanii. A, branchial crown emerging from tube, showing colour pattern. Live specimen from Botany Bay (one from AM W43464), photo by S. Humphreys. B, branchial crown showing asymmetric lobes. Preserved specimen (AM W24270, from North Haven, South Australia), photo by E. Wong. C, junction of thorax and abdomen showing: a, thoracic companion chaetae; b, spiralled fascicle of abdominal chaetae. Live specimen from Botany Bay (one from AM W43464), photo by S. Humphreys.
FIGURE 1 in First Report of Sabella spallanzanii (Gmelin, 1791) (Annelida: Polychaeta) from Botany Bay, New South Wales, a northern range extension for the invasive species within Australia
FIGURE 1. Map showing collecting location of Sabella spallanzanii in Botany Bay. Inset: recorded locations of S. spallanzanii populations in Australia. = Botany Bay. X = Port Adelaide. = Port Phillip Bay. A = Devonport. □ = Eden Harbour (Twofold Bay). ● = Esperance. Ο = Bunbury. ♢ = Albany. ♦ = Spencer Gulf. ̝= Cockburn Sound and Fremantle.
Subspecies and Distribution. S. s. scrofa Linnaeus, 1758 — W Europe, from Denmark, Germany, Poland, and Czech Republic to N Italy and N Iberian Peninsula; possibly also Albania. The taxonomic status of animals in Austria, Switzerland, Slovenia, and Slovakia is unclear but presumably these populations are included in scrofa, as are the populations of Sweden, Finland, and the Baltic states. However, restocking of once depleted populations, for example in Italy, has likely involved the introduction and mixing of this subspecies with other subspecies, such as attila. S. s. affinis Gray, 1847 — S India and Sri Lanka. S. s. algirus Loche, 1867 — Tunisia, Algeria, and Morocco, on the coastal side of the mountains or in the low montane areas. S. s. attila Thomas, 1912 — Hungary, Ukraine, C & S Belarus, Romania, Moldova, and S Russia towards the N flank of the Caucasus, but not including the Transcaucasian countries of Georgia, Armenia, and Azerbaijan. The range possibly extends as far S as the Mesopotamian Delta in Iraq, in which case it would likely include W & SW Iran, and possibly E Turkey and Syria, where it borders with lybicus. Such a range could not be easily reconciled with a statement by Groves that "the difference between pigs from N and S of the Caucasus is quite striking; Transcaucasian boars are certainly not attila." This subspecies may also extend into C Asia and include Kazakhstan, Uzbekistan, and Turkmenistan, but no data exist to support this. S. s. baeticus Thomas, 1912 — originally described from Coto Donana, S Spain, and later merged with meridionalis; also S Portugal. Unless evidence is found that these Italian and Iberian populations are the relics of a much larger formerly contiguous range, this subspecies should be kept as distinct. S. s. coreanus Heude, 1897 — Korean Peninsula. S. s. eristatus Wagner, 1839 — Himalayas S to C India and E to Indochina (N of the Kra Isthmus). S. s. davidi Groves, 1981 — the arid zone from E Iran to Gujarat, including Pakistan and NW India, and perhaps N to Tajikistan. S. s. leucomystax Temminck, 1842 — main Is ofJapan (Honshu, Shikoku, Kyushu, Nakadori, Hiburijima, Tojima, Kushima, and other smaller Is). S. s. lybicus Gray, 1868 — Bulgaria, Greece, Turkey, Syria, Jordan, Israel, Palestine, in the past also in Lybia, and Egypt. The former Yugoslavia was included in its range, which would suggest that now Slovenia, Serbia, Croatia, Bosnia and Herzegovina, Montenegro, and Kosovo are within the range of this subspecies, although the exact boundaries are unclear. Pigs from Albania have been assigned to S. s. scrofa. S. s. majori De Beaux & Festa, 1927 — C & S Italian Peninsula. S. s. menidionalis Forsyth Major, 1882 — Corsica and Sardinia, with the proviso that the two populations are very likely to be introduced or feral. S. s. moupinensis Milne-Edwards, 1871 — China, S to Vietnam and W to Sichuan. S. s. nigripes Blanford, 1875 — the flanks of the Tianshan mountains in Kyrgyzstan and NW China (Xinjiang). An animal photographed in NE Iran (Golestan) looked like this subspecies. S. s. nukiuanus Kuroda, 1924 — Iriomote, Ishigaki, Okinawa, Tokunoshima, Amamioshima, and Kakerome Is in the Ryukyu chain in extreme S Japan, though some of these populations have hybridized with introduced domesticates. S. s. sibiricus Staffe, 1922 — Mongolia and Transbaikal (S & E of Lake Baikal). S. s. tawvanus Swinhoe, 1863 — Taiwan. S. s. ussuricus Heude, 1888 — far E Russia and the Manchurian region (China). Korean populations were previously included in this subspecies, but based on new evidence, the Korean taxon seems more similar to moupinensis. S. s. vittatus Boie, 1828 — Malay Peninsula, S of the Isthmus of Kra, the offshore islands of Terutai and Langkawi, Sumatra, Riau Archipelago, Java, Bali, and a range of smaller islands around these, including Babi, Bakong, Batam, Bawean, Bengkalis, Bintan, Bulan, Bunguran, Cuyo, Deli, Durian, Enggano, Galang, Jambongan, Karimon (Riau Is), Kundur, Lagong, Laut, Lingga, Lingung, Mapor, Moro Kecil, North Pagai, Nias, Panaitan, Payong, Penang, Pinie, Rupat, Siantan, Siberut, Simeulue, Singkep, Sugi, Sugi Bawa, Telibon, Tinggi, Tuangku, and the Tambelan Is. This species was originally present from the British Is in the extreme W, through Eurasia from S Scandinavia to S Siberia, extending as far E as Korea and Japan, and SE into some of the Sunda Is and Taiwan. In the S the species ranged along the Nile Valley to Khartoum, and N of the Sahara in Africa, more orless following the continental coasts of S, E, and SE Asia. Within this range it was absent only from extremely dry deserts, e.g. the driest regions of Mongolia and in China W of Sichuan; and alpine zones, such as the high altitudes of Pamir and Tien Shan. In recent centuries, the range of S. scrofa has changed dramatically because of hunting and changes in available habitat. The species disappeared from the British Is in the 17" century, from Denmark in the 19" century, and was greatly reduced in range and numbers in the 20" century from areas as distant as Tunisia, Sudan, Germany, and Russia. Following these severe declines, there were some slight population recoveries in Russia, Italy, Spain, and Germany in the mid-20™ century, and natural and assisted range expansions in Denmark and Sweden. The species has also been inadvertently reintroduced in various locations in the Great Britain via escapees of mixed origin from commercial farming enterprises. Ex-S. scrofa stocks also occur as introduced feral populations in various other parts of the world, including Australia, New Zealand, the eastern Malay Archipelago, and in North, Central, and South America. In all of these areas they are now generally recognized as a major pest. in Suidae
Subspecies and Distribution. S. s. scrofa Linnaeus, 1758 — W Europe, from Denmark, Germany, Poland, and Czech Republic to N Italy and N Iberian Peninsula; possibly also Albania. The taxonomic status of animals in Austria, Switzerland, Slovenia, and Slovakia is unclear but presumably these populations are included in scrofa, as are the populations of Sweden, Finland, and the Baltic states. However, restocking of once depleted populations, for example in Italy, has likely involved the introduction and mixing of this subspecies with other subspecies, such as attila. S. s. affinis Gray, 1847 — S India and Sri Lanka. S. s. algirus Loche, 1867 — Tunisia, Algeria, and Morocco, on the coastal side of the mountains or in the low montane areas. S. s. attila Thomas, 1912 — Hungary, Ukraine, C & S Belarus, Romania, Moldova, and S Russia towards the N flank of the Caucasus, but not including the Transcaucasian countries of Georgia, Armenia, and Azerbaijan. The range possibly extends as far S as the Mesopotamian Delta in Iraq, in which case it would likely include W & SW Iran, and possibly E Turkey and Syria, where it borders with lybicus. Such a range could not be easily reconciled with a statement by Groves that "the difference between pigs from N and S of the Caucasus is quite striking; Transcaucasian boars are certainly not attila." This subspecies may also extend into C Asia and include Kazakhstan, Uzbekistan, and Turkmenistan, but no data exist to support this. S. s. baeticus Thomas, 1912 — originally described from Coto Donana, S Spain, and later merged with meridionalis; also S Portugal. Unless evidence is found that these Italian and Iberian populations are the relics of a much larger formerly contiguous range, this subspecies should be kept as distinct. S. s. coreanus Heude, 1897 — Korean Peninsula. S. s. eristatus Wagner, 1839 — Himalayas S to C India and E to Indochina (N of the Kra Isthmus). S. s. davidi Groves, 1981 — the arid zone from E Iran to Gujarat, including Pakistan and NW India, and perhaps N to Tajikistan. S. s. leucomystax Temminck, 1842 — main Is ofJapan (Honshu, Shikoku, Kyushu, Nakadori, Hiburijima, Tojima, Kushima, and other smaller Is). S. s. lybicus Gray, 1868 — Bulgaria, Greece, Turkey, Syria, Jordan, Israel, Palestine, in the past also in Lybia, and Egypt. The former Yugoslavia was included in its range, which would suggest that now Slovenia, Serbia, Croatia, Bosnia and Herzegovina, Montenegro, and Kosovo are within the range of this subspecies, although the exact boundaries are unclear. Pigs from Albania have been assigned to S. s. scrofa. S. s. majori De Beaux & Festa, 1927 — C & S Italian Peninsula. S. s. menidionalis Forsyth Major, 1882 — Corsica and Sardinia, with the proviso that the two populations are very likely to be introduced or feral. S. s. moupinensis Milne-Edwards, 1871 — China, S to Vietnam and W to Sichuan. S. s. nigripes Blanford, 1875 — the flanks of the Tianshan mountains in Kyrgyzstan and NW China (Xinjiang). An animal photographed in NE Iran (Golestan) looked like this subspecies. S. s. nukiuanus Kuroda, 1924 — Iriomote, Ishigaki, Okinawa, Tokunoshima, Amamioshima, and Kakerome Is in the Ryukyu chain in extreme S Japan, though some of these populations have hybridized with introduced domesticates. S. s. sibiricus Staffe, 1922 — Mongolia and Transbaikal (S & E of Lake Baikal). S. s. tawvanus Swinhoe, 1863 — Taiwan. S. s. ussuricus Heude, 1888 — far E Russia and the Manchurian region (China). Korean populations were previously included in this subspecies, but based on new evidence, the Korean taxon seems more similar to moupinensis. S. s. vittatus Boie, 1828 — Malay Peninsula, S of the Isthmus of Kra, the offshore islands of Terutai and Langkawi, Sumatra, Riau Archipelago, Java, Bali, and a range of smaller islands around these, including Babi, Bakong, Batam, Bawean, Bengkalis, Bintan, Bulan, Bunguran, Cuyo, Deli, Durian, Enggano, Galang, Jambongan, Karimon (Riau Is), Kundur, Lagong, Laut, Lingga, Lingung, Mapor, Moro Kecil, North Pagai, Nias, Panaitan, Payong, Penang, Pinie, Rupat, Siantan, Siberut, Simeulue, Singkep, Sugi, Sugi Bawa, Telibon, Tinggi, Tuangku, and the Tambelan Is. This species was originally present from the British Is in the extreme W, through Eurasia from S Scandinavia to S Siberia, extending as far E as Korea and Japan, and SE into some of the Sunda Is and Taiwan. In the S the species ranged along the Nile Valley to Khartoum, and N of the Sahara in Africa, more orless following the continental coasts of S, E, and SE Asia. Within this range it was absent only from extremely dry deserts, e.g. the driest regions of Mongolia and in China W of Sichuan; and alpine zones, such as the high altitudes of Pamir and Tien Shan. In recent centuries, the range of S. scrofa has changed dramatically because of hunting and changes in available habitat. The species disappeared from the British Is in the 17" century, from Denmark in the 19" century, and was greatly reduced in range and numbers in the 20" century from areas as distant as Tunisia, Sudan, Germany, and Russia. Following these severe declines, there were some slight population recoveries in Russia, Italy, Spain, and Germany in the mid-20™ century, and natural and assisted range expansions in Denmark and Sweden. The species has also been inadvertently reintroduced in various locations in the Great Britain via escapees of mixed origin from commercial farming enterprises. Ex-S. scrofa stocks also occur as introduced feral populations in various other parts of the world, including Australia, New Zealand, the eastern Malay Archipelago, and in North, Central, and South America. In all of these areas they are now generally recognized as a major pest.
FIGURE 5 in True branching and phenotypic plasticity in the planktonic cyanobacterium Dolichospermum brachiatum sp. nov. (Nostocales, Aphanizomenonaceae), from south-eastern Australia
FIGURE 5. Phylogenetic tree based on partial 16S ribosomal RNA gene sequence (1518 base pairs) of 128 OTUs showing the phylogenetic position of Dolichospermum brachiatum. Numbers indicate bootstrap values (> 50%) from 1000 replicates of ML and NJ analyses respectively. GenBank accession numbers are shown in parentheses. Scale bar = 0.01 nucleotide substitutions per site.
FIGURE 2 in True branching and phenotypic plasticity in the planktonic cyanobacterium Dolichospermum brachiatum sp. nov. (Nostocales, Aphanizomenonaceae), from south-eastern Australia
FIGURE 2. Sequence of development of T-type true branching of Dolichospermum brachiatum from Waranga Basin. Scale bars = 20 μm.
FIGURE 7 in True branching and phenotypic plasticity in the planktonic cyanobacterium Dolichospermum brachiatum sp. nov. (Nostocales, Aphanizomenonaceae), from south-eastern Australia
FIGURE 7. Secondary structure of the ITS sequence in D. brachiatum and allied species. Circles and oblongs highlight the differences in the structures; (A–D) D1-D1′ helix (A) D. brachiatum strains WB20619.B1, WB20619.B3, WB20619.C1 and WB20619.C2, (B) D. planctonicum strains 1-3; 19-1; 23-10; NRERC-101; D. ucrainicum CHAB623, (C) D. affinis CHAB28, (D) D. lemmermanni BC Ana 0032. (E–H) Box B helix (E) D. brachiatum strains WB20619.B1, WB20619.B3, WB20619.C1 and WB20619.C2, (F) D. planctonicum strains 1-3; 19-1; 23-10; NRERC-101; D. ucrainicum CHAB623, (G) D. affinis CHAB28 and CHAB964; D. flos-aquae CHAB1652 and NIES 1669, (H) D. lemmermannii BC Ana 0032. (I–M) V3 helix (I) D. brachiatum strains WB20619.B1, WB20619.B3, WB20619.C1 and WB20619.C2, (J) D. planctonicum strain 1-3; 1-9; 19-1; 23-10; NRERC-101, (K) D. affinis CHAB28; D. flos-aquae CHAB1652 and NIES 1669, (L) D. ucrainicum CHAB623, (M) D. lemmermannii BC Ana 0032.
FIGURE 6 in True branching and phenotypic plasticity in the planktonic cyanobacterium Dolichospermum brachiatum sp. nov. (Nostocales, Aphanizomenonaceae), from south-eastern Australia
FIGURE 6. Phylogenetic tree based on the ITS sequence of the 16S–23S rRNA operon of 25 OTUs showing the phylogenetic position of Dolichospermum brachiatum. Numbers indicate bootstrap values> 50% from 1000 replicates of ML and NJ analyses respectively. GenBank accession numbers shown in parentheses. Scale bar = 0.05 nucleotide substitutions per site. Strains isolated and sequenced in this study shown in bold.
Predicting habitat suitability for wild deer in relation to threatened ecological communities in south-eastern New South Wales, Australia
<p><strong>Context.</strong> High density deer populations can cause ecological damage, yet their distribution and impacts are poorly known across much of Australia. As a result, land managers rely on anecdotal reports to make decisions about management and control measures.</p> <p><strong>Aims.</strong> We aimed to model habitat suitability for deer in the South Coast of New South Wales (NSW), Australia, to be used as a baseline for future management and identify which threatened ecological communities (TECs) in the region are at greatest current risk of being occupied by deer.</p> <p><strong>Methods.</strong> We compiled 678 presence-only records of wild deer from online databases, observations made by National Parks and Wildlife Service field staff and field-based surveys. We combined these observations with eight environmental variables to model and map habitat suitability for deer across our study area using maximum entropy. Three spatial models of habitat suitability across our study area were produced: one for all deer species; and two species-specific models for fallow and sambar deer. Key results. Our models indicate that suitable habitat for deer exists throughout much of the South Coast of NSW. Of the TECs examined, Coastal Saltmarsh, Themeda Grassland, and Swamp Sclerophyll Forest had the highest proportion of area likely to be extremely suitable for deer and thus should be prioritised for protection within our study area.</p> <p><strong>Conclusions. </strong>Further systematic field-based surveys are needed to improve the quality of models in this region. Implications. We recommend that areas having high habitat suitability but are not yet occupied by deer be identified as sites where deer occupancy could be prevented.</p>
Distribution. SE Australia, in SE Queensland, New South Wales, Victoria, and SE South Australia; also Flinders I and Tasmania. in Vespertilionidae
Distribution. SE Australia, in SE Queensland, New South Wales, Victoria, and SE South Australia; also Flinders I and Tasmania.
Distribution. SW Western Australia, E & SE Queensland (including Fraser I), C & E New South Wales, Victoria, and SE South Australia, SW & E Australia. A specimen is known from Fiji, but this is suspected to represent the New Caledonian Long-eared Bat (NV. nebulosus) or a mislabeled specimen. in Vespertilionidae
Distribution. SW Western Australia, E & SE Queensland (including Fraser I), C & E New South Wales, Victoria, and SE South Australia, SW & E Australia. A specimen is known from Fiji, but this is suspected to represent the New Caledonian Long-eared Bat (NV. nebulosus) or a mislabeled specimen.
Subspecies and Distribution. A.p.porcinusZimmermann,1780—Pakistan,NIndia,Nepal,Bhutan,Bangladesh,andMyanmar. A. p. annamiticus Heude, 1888 — S China (Yunnan), Thailand (reintroduced), and Cambodia; formerly also Laos and Vietnam but may be extinct there now. Tt was introduced some centuries ago in Sri Lanka, and more recently into Australia, and South Africa. in Cervidae
Subspecies and Distribution. A.p.porcinusZimmermann,1780—Pakistan,NIndia,Nepal,Bhutan,Bangladesh,andMyanmar. A. p. annamiticus Heude, 1888 — S China (Yunnan), Thailand (reintroduced), and Cambodia; formerly also Laos and Vietnam but may be extinct there now. Tt was introduced some centuries ago in Sri Lanka, and more recently into Australia, and South Africa.
Distribution. Formerly Anatolia, Turkey, then has been introduced into Europe from ancient times and later into many other countries in North and South America, South Africa, Australia, New Zealand, and Fiji Is. The distribution map includes both the native range in Anatolia and the European continent with its old introductions. in Cervidae
Distribution. Formerly Anatolia, Turkey, then has been introduced into Europe from ancient times and later into many other countries in North and South America, South Africa, Australia, New Zealand, and Fiji Is. The distribution map includes both the native range in Anatolia and the European continent with its old introductions.
Subspecies and Distribution. R.u.unicolorKerr,1792—India,Nepal,Bhutan,Bangladesh,andSriLanka. R.u.brooketHose,1893—Borneo. R.u.cambojensisGray,1861—mainlandSEAsia,fromSChina(includingHainanI)andMyanmartoMalayPeninsula. R.u.equinaG.Cuvier,1823—Sumatra,andseveralsmallerassociatedIs. R. u. swinhoer Sclater, 1862 — Taiwan. Introduced to Australia, New Zealand, South Africa, and USA. in Cervidae
Subspecies and Distribution. R.u.unicolorKerr,1792—India,Nepal,Bhutan,Bangladesh,andSriLanka. R.u.brooketHose,1893—Borneo. R.u.cambojensisGray,1861—mainlandSEAsia,fromSChina(includingHainanI)andMyanmartoMalayPeninsula. R.u.equinaG.Cuvier,1823—Sumatra,andseveralsmallerassociatedIs. R. u. swinhoer Sclater, 1862 — Taiwan. Introduced to Australia, New Zealand, South Africa, and USA.
Distribution. Restricted to arid areas of inland Australia S of Tropic of Capricorn, in SW Western Australia, S Northern Territory, South Australia, SW Queensland, W New South Wales, and NW Victoria; distribution is disjunct, with Western Australian population isolated from C & E population by treeless areas of Nullarbor Plain. in Molossidae
Distribution. Restricted to arid areas of inland Australia S of Tropic of Capricorn, in SW Western Australia, S Northern Territory, South Australia, SW Queensland, W New South Wales, and NW Victoria; distribution is disjunct, with Western Australian population isolated from C & E population by treeless areas of Nullarbor Plain.
Distribution. Sparse and patchy distribution in arid and semiarid regions of Australia, extending E from C Australia to Great Dividing Range in Queensland and N New South Wales. in Molossidae
Distribution. Sparse and patchy distribution in arid and semiarid regions of Australia, extending E from C Australia to Great Dividing Range in Queensland and N New South Wales.
Year-round at-sea movements of fairy prions from south-eastern Australia
<p>Effective conservation assessments require detailed information of species' ecological niches during the whole annual cycle. For seabirds, this implies investigating the at-sea distribution and foraging behaviour during both the breeding and non-breeding periods. However, until recently, collecting information about the smallest species has been precluded by the excessive size of the required devices. This lack of knowledge is exacerbated in the case of polytypic genera with species sharing very similar appearance and behaviour, such as the super-abundant prions (<em>Pachyptila</em> spp.). The present study investigates the year-round at-sea distribution and foraging ecology of the fairy prion (<em>Pachyptila turtur</em>) in south-eastern Australia. Using miniaturized GPS during the breeding season and geolocators (GLS) during the non-breeding period, the results highlight the importance of the continental shelf-edge waters for fairy prions throughout the year. In addition, contrary to previous assumptions, the GLS data revealed an unsuspected post-breeding migration to the waters south of Australia, during which individuals likely undergo a rapid moult of flight feathers. Understanding the at-sea distribution and ecology of prions during the whole annual cycle will be fundamental to their conservation as it can reveal species- or population-specific threats that have been overlooked because of their status of abundant species.</p>
Distribution. SE Australia in three isolated populations: New South Wales (Kosciuszko National Park) and Victoria (a population between Mt Bogong and Mt Higginbotham and another distinct population on Mt Buller). in Burramyidae
Distribution. SE Australia in three isolated populations: New South Wales (Kosciuszko National Park) and Victoria (a population between Mt Bogong and Mt Higginbotham and another distinct population on Mt Buller).
Distribution. SE Australia, from the McPherson and Border ranges in SE Queensland, S to Victoria and SE South Australia; it is absent from the coastal drainages of the Great Dividing Range, S at least to the Wallamba River, and W of the Great Dividing Range in New South Wales (but it probably occurs to the limit of tree growth on the Southern Tableland), and from the inland draining catchments of the Murray Basin in Victoria. in Acrobatidae
Distribution. SE Australia, from the McPherson and Border ranges in SE Queensland, S to Victoria and SE South Australia; it is absent from the coastal drainages of the Great Dividing Range, S at least to the Wallamba River, and W of the Great Dividing Range in New South Wales (but it probably occurs to the limit of tree growth on the Southern Tableland), and from the inland draining catchments of the Murray Basin in Victoria.
FIGURE 21 in Five new species of Yoyetta Moulds (Hemiptera: Cicadidae: Cicadettinae) from south-eastern Australia
FIGURE 21. Male calling song structure of Yoyetta robusta n. sp. illustrated in waveform plots, including: (A), a 6.0 s sample of the stationary clicking song with s sequence of triple syllables followed by an echeme; (B), a 0.8 s sample expanded from the plot above showing the detailed structure of three triple syllables; (C), a 0.4 s sample expanded from (A) above showing the detailed structure of one triple syllable followed by the echeme; (D), a power spectrum illustrating the song frequency of the syllables; and (E), a power spectrum illustrating the song frequency of the echeme. The specimen was recorded in the field by LWP in the Dundee district, New South Wales (29°36'19''S 151°56'17''E) using RS2 (see Methods and Terminology).
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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