LTERN Data Portal
Tropical Rainforest Plot Network: Rainforest Tree Demographic Data (Plot EP34), Northern Queensland, Australia, 2011-2013
- Citation
-
Metcalfe, D; Murphy, H; Bradford, M; Hogan, D; Ford, A (): Tropical Rainforest Plot Network: Rainforest Tree Demographic Data (Plot EP34), Northern Queensland, Australia, 2011-2013. Long Term Ecological Research Network. http://www.ltern.org.au/knb/metacat/ltern2.555.6/html
- Identifier
-
- docid
- ltern2.555.6
- Data Creators
-
- Individual
- Dr Daniel J. Metcalfe
- Position
- Senior Research Scientist
- Organization
- CSIRO Ecosystem Sciences
- Individual
- Dr Helen T. Murphy
- Position
- Research Scientist
- Organization
- CSIRO Ecosystem Sciences
- Individual
- Matt G. Bradford
- Position
- Senior Technical Officer
- Organization
- CSIRO Ecosystem Sciences
- Individual
- Dominic Hogan
- Position
- Data Librarian
- Organization
- CSIRO Information Management and Technology
- Individual
- Andrew J. Ford
- Position
- Research Projects Officer (Reference herbarium)
- Organization
- CSIRO Ecosystem Sciences
- Abstract
-
The LTERN Tropical Rainforest Plot Network Rainforest Tree Demographic Data contains stem measurement data for 1 of 20, 0.5 ha (100 m x 50 m) permanent rainforest plots in Northern Queensland, Australia from 2011 to 2013. This is part of a much larger dataset that spans from 1971 to 2013 that is managed by CSIRO. This data publication refers specifically to observations made at Plot EP34, and this data is accessible as a composite data package at the following location: Metcalfe, D; Murphy, H; Bradford, M; Hogan, D; Ford, A (2014): Tropical Rainforest Plot Network: Rainforest Tree Demographic Data, Northern Queensland, Australia, 2011-2013. Long Term Ecological Research Network. http://www.ltern.org.au/knb/metacat/ltern2.90.42/html The CSIRO permanent rainforest plots are located within 60 km of the north Queensland coast between Mackay (21.5ºS, 149ºE) and the Iron Range on Cape York Peninsula (12.5ºS, 143ºE). The plots have a rainfall range of 1200 to 3500 mm, represent eleven vegetation types, six parent materials, and range from 15 m to 1200 m above sea level. Except for minor disturbances associated with selective logging on two plots, the plots were established in old growth forest and all plots have thereafter been protected. Plots were regularly censused and at each census the diameter at breast height (DBH) of all stems ≥10 cm DBH is recorded. Due to the wide geographical range of the plots, no species dominate, although the families Lauraceae, Rutaceae and Myrtaceae contribute a large number of species. The data collected from the 20 plots provides an insight into the floristical composition, structure and long term forest dynamics of Australian tropical rainforests and allows direct comparisons to be made with long-term monitoring plots at a global scale (Bradford, M.G., Murphy, H.T., Ford, A.J., Hogan, D. and Metcalfe, D.J. (2014). Long term stem inventory data from tropical rainforest plots in Australia. Ecology 95:2362. http://www.rainforest-crc.jcu.edu.au/publications/permanent_plots1.pdf. This is part of a much larger dataset that spans from 2004 to 2014; a synopsis of related data packages which have been collected as part of the Tropical Rainforest Plot Network’s full program is provided at http://www.ltern.org.au/index.php/ltern-plot-networks/tropical-rainforest.
- Contacts for Questions on the Use and Interpretation of Data
-
- Individual
- Dr Daniel J. Metcalfe
- Position
- Senior Research Scientist
- Organization
- CSIRO Ecosystem Sciences
- Address
-
EcoSciences Precinct
41 Boggo Road
Dutton Park. Queensland 4102
Australia
- Phone
-
- voice
- 07 3833 5529,
- Email Address
- dan.metcalfe@csiro.au
- Individual
- Matt G. Bradford
- Position
- Senior Technical Officer
- Organization
- CSIRO Ecosystem Sciences
- Address
-
P.O. Box 780
Atherton. Queensland 4883
Australia
- Phone
-
- voice
- 61 740918800
- Email Address
- matt.bradford@csiro.au
- Project Information and Data Owners
-
- Title
- CSIRO Permanent Rainforest Plots
- Personnel
-
- Role
- Data Owner
- Organization
- CSIRO
- Role
- Principal Investigator
- Individual
- Dr Daniel J. Metcalfe
- Position
- EcoSciences Precinct
- Organization
- CSIRO Ecosystem Sciences
- Role
- Research Projects Officer
- Individual
- Matt G. Bradford
- Position
- Senior Technical Officer
- Organization
- CSIRO Ecosystem Sciences
- Funding
-
Commonwealth Forest and Timber Bureau (1971-1978), CSIRO internal funding (1978-1992), Tropical Rainforest Ecology and Management and the Rainforest Cooperative Research Centres (1992-2006), Earthwatch (2006). The most recent censuses have been supported by the Long-Term Ecological Research Network sub facility, part of the Australian Government’s Terrestrial Ecosystems Research Network (http://www.tern.org.au/Long-Term-Ecological-Research-Network-LTERN-pg17872.html).
- Methods and Sampling Information
-
- Methods
-
Method Step 1
- Description
-
Plot set-up
The 20 CSIRO permanent plots were opportunistically located ahead of logging operations or in areas of no or minor recent disturbance (EP9 and EP38 showed evidence of slight disturbance in a section of the plot due to selective logging at least 20 years prior to establishment). Where possible, plots were located to represent the major forests and geologies of North Queensland. All plots were surveyed to enclose a projected plan view area of 0.5 ha (100 m x 50 m) with plot boundary distances corrected for slope. Plot boundaries were surveyed with prismatic compasses, 50 m steel survey band and Abney level. The four plot corners were initially marked with treated wooden pegs and subsequently replaced with steel pickets. All plots were subdivided into 16 subplots, each 25 m x 12.5 m with permanent wooden subplot markers. A 20 m buffer area around each plot was established to exclude future human disturbance. A canopy tower was located adjacent to both EP4 and EP33 from establishment until 2005 and focussed on canopy sampling and photosynthetic studies. Data from the towers is not included in this data paper, however, publications resulting from data collected are included in the publications and results section. The plots were established between 1971 and 1980 and were initially censused every two years until 1991. Since 1991 census intervals have ranged between 2-15 years.
- Instrument
-
- Plot boundaries were surveyed with prismatic compasses, 50 m steel survey band and Abney level.
Method Step 2- Description
-
Census of stems ≥10 cm DBH
At each census, the diameter of all stems ≥10 cm DBH were measured with a diameter tape (Richter 2 m, Yamayo Million 10 m) to the nearest millimetre. Measurements made by the Commonwealth Forest and Timber Bureau at plot establishment followed protocols of Queensland Department of Forestry which are similar to the Smithsonian Institute methodology with two major exceptions, 1) for species known to exhibit buttressing on larger specimens, the point of measurement (POM) was pre-emptively elevated above the predicted buttressing influence. Prior to 1992 this was not always done as the buttressing nature of all species was not known. Subsequently, some point of measurement marks have been raised as buttresses moved their way up stems. In addition, some POM marks were lowered or raised due to deformations on the stem. In these cases only the newly raised or lowered DBH measurement was measured and DBH changed was recorded. 2) point of measurement lines approximately 25 mm wide and perpendicular to the trunk, and an alphanumeric stem code were painted on the stem. Rules of measurement are as follows:
1) Comments were recorded for unusual measurements that may affect the way the data is interpreted: 1 = raised or lowered point of measurement, 2 = broken top above POM, 3 = hollow stem, 4 = dead or damaged part of the stem, 5 = DBH estimated, 7 = sick stem, 8 = near dead stem, 9 = leaning >45°.
2) Stem diameters were measured in centimetres at breast height from the ground on the uphill side of the stem. Stems with DBH <10 cm were not included.
3) Stems leaning >45 degrees (comment 9) were measured 1.3 m along the stem along the underside of the stem.
4) Vines were pulled away from the stem or the diameter tape was slipped under the vines before measuring where possible. Where there was a reason why no measurement could be made, a visual estimation of the DBH was made (comment 5). This occurred when a stem had immovable vines, a strangler fig, or large and high buttresses.
5) Stems with a swelling or deformity that precludes taking a normal DBH measurement were measured above or below the deformity. If the deformity continued to <1 m above the ground then the measurement was taken above the deformity.
6) Stems with buttresses were measured at least 1 m above the highest buttress. Smaller specimens of particular species that were known to exhibit buttressing when they grow larger were measured at a higher POM to account for future buttressing. In this case the POM was decided on by the team leader.
7) Where the trunk was irregular, damaged, deformed or fluted at all heights, the POM was taken at 1.3 m. A comment of 3 or 4 was recorded for hollow or damaged stem.
8) Stems that forked above 1.3 m were measured below the fork where the stem was not swollen or deformed. Stems that forked below 1.3 m were measured as separate stems, at or close to 1.3 m.
9) Palms were included if the stem was ≥10 cm DBH below the lowest living leaf base.
10) Lianas were measured 1.3 m along the stem after they left the ground. The height of a liana was recorded as the estimated length of the stem and was generally higher than the host stem. Lianas were mapped where they were considered to originate.
11) The diameter of each individual stem (aerial root) of a strangler fig ≥10 cm DBH was measured separately. Over time when these roots merged with each other or the host stem, then the DBH was estimated (comment 5).
Lianas ≥10 cm DBH were not included in the census at establishment, were included selectively from 1987 onwards. Consequently, the 11 stems listed in Table 4 were most likely present as stems ≥10 cm before they were recorded in the database. All other lianas in the database (8 stems) were included in the database as they were recruited into the ≥10 cm DBH size class.
The positions of all stems ≥10 cm DBH were mapped to an accuracy of ±0.5 m. The X coordinate was taken as the projected plan distance in metres along the 100 m axis starting at the subplot A-D outside edge of the plot (Fig. 1). The Y coordinate was taken as the projected plan distance in metres along the 50 m axis starting at the subplot A-M outside edge. Where stems originated within 0.5 m of each other or in a multi-stemmed case, the same coordinates were shared within the same plot.
At establishment, the height of each stem ≥10 cm DBH was estimated. Height estimations were taken as the length of the stem from ground to upmost growing tip. Estimations were regularly validated for highly visible stems using the triangulation method (base distance and slope angle) with a clinometer and measuring tape. Height estimations were repeated in 1998 (2001 at EP37; not repeated at EP31) using the same method with the addition of a laser rangefinder (Newcon Optic 1200, Nikon Forestry 550) to aid in base distance, slope angle and direct height estimations where appropriate. Stems recruited at each census were given a height using the same method.
Stems were numbered using an alphanumeric code representing subplot (A to P) and sequential number within that subplot. This code was painted on the stem either below or above the POM line. Multi-stemmed individuals branching below the POM were numbered by placing a numeral in the ‘hundreds’ before the stem number. For example: in the same subplot, P005, P105 and P205 are separate trunks of the same individual branching at or below 1.3 m.
At each census following establishment, new stems recruiting into the ≥10 cm DBH size class were measured, mapped and assigned a height. All stems ≥10 cm DBH that had died since the last census were noted and no attempt was made to assign a cause of death. Stems that were dead or snapped below the painted POM line were considered dead. The nature and extent of major disturbances (e.g. cyclones, erosion) in each plot were noted and mapped.
- Instrument
-
- At each census, the diameter of all stems ≥10 cm DBH were measured with a diameter tape (Richter 2 m, Yamayo Million 10 m) to the nearest millimetre.
- Sampling
-
- Study Extent Description
-
The study was conducted in the rainforests of North Queensland, Australia between Mackay 21.5ºS, 149ºE and the Iron Range 12.5ºS, 143ºE. The plots span much of the geographical variation in environmental gradients across the study area and represent eleven moist humid tropical vegetation (Tracey, J. G. 1982. The vegetation of the humid tropical region of North Queensland. CSIRO Publishing, Melbourne.), six parent material types, and range from 15 m to 1200 m asl. The climate is tropical with mean annual rainfall ranging from 1200 mm to over 8000 mm on the higher coastal ranges. Seventeen of the plots are located within the Wet Tropics Bioregion which is broadly composed of closed canopy rainforest and open Eucalyptus forests and woodlands. Continuous areas of rainforest account for approximately 6300 km2 of the region (Tracey 1982 as above) and are found in the wetter and mountainous areas where the rainfall exceeds 1500 mm. Full site descriptions of each plot can be found at http://www.rainforest-crc.jcu.edu.au/publications/permanent_plots1.pdf
- Sampling Description
-
The 20 CSIRO permanent plots were opportunistically located ahead of logging operations or in areas of no or minor recent disturbance (EP9 and EP38 showed evidence of slight disturbance in a section of the plot due to selective logging at least 20 years prior to establishment). Where possible, plots were located to represent the major forests and geologies of North Queensland. All plots were surveyed to enclose a projected plan view area of 0.5 ha (100 m x 50 m) with plot boundary distances corrected for slope. The resulting plot areas are presented in Table 2. Plot boundaries were surveyed with prismatic compasses, 50 m steel survey band and Abney level. The four plot corners were initially marked with treated wooden pegs and subsequently replaced with steel pickets. All plots were subdivided into 16 subplots (A to P), each 25 m x 12.5 m with permanent wooden subplot markers. A 20 m buffer area around each plot was established to exclude future human disturbance. A canopy tower was located adjacent to both EP4 and EP33 from establishment until 2005 and focussed on canopy sampling and photosynthetic studies. Data from the towers is not included in this data package, but have been included in associated publications. The plots were established between 1971 and 1980 and were initially censused every two years until 1991, and at intervals of 2-15 years thereafter .
- Keywords and Subject Categories
-
- Keywords List
-
- rainforest
- mortality
- recruitment
- cyclone
- hurricane
- disturbance
- stem growth
- stem height
- permanent plot
- Australia
- biomass
- LTERN Monitoring Themes
-
- Vegetation structure
- Plant species composition
- Plant species abundance
- Individual plants
- ANZSRC-FOR Codes
-
- 0501 Ecological Applications
- 0602 Ecology
- GCMD Science Keywords
-
- Biological Classification > Plants
- Geographic Coverage
-
- Geographic Description
- The CSIRO permanent rainforest plots are located within 60 km of the north Queensland coast between Mackay (21.5ºS, 149ºE) and the Iron Range on Cape York Peninsula (12.5ºS, 143ºE). North-eastern Australia is topographically diverse, and the plots span much of the geographical variation in environmental gradients across the study area. The climate is tropical with mean annual rainfall ranging from 1200 mm to over 8000 mm on the higher coastal ranges. Seventeen of the plots are located within the Wet Tropics Bioregion (sensu Department of Environment 2013) between 19.4ºS, 146.5ºE and 15.7ºS, 145.3ºE.
- Bounding Coordinates
-
- West
- 143.25092 degrees
- East
- 148.54295 degrees
- North
- -12.74273 degrees
- South
- -21.25266 degrees
- Temporal Coverage
-
- Date Begin
- 2011
- Date End
- 2013
- Taxonomic Coverage and Classification
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- Classification
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- Species
- Acacia celsa
-
- Species
- Acacia hylonoma
-
- Species
- Aceratium concinnum
-
- Species
- Aceratium doggrellii
-
- Species
- Acmena divaricata
-
- Species
- Acmena resa
-
- Species
- Acmenosperma claviflorum
-
- Species
- Acronychia acidula
-
- Species
- Acronychia acronychioides
-
- Species
- Acronychia laevis
-
- Species
- Agathis atropurpurea
-
- Species
- Agathis robusta
-
- Species
- Aglaia australiensis
-
- Species
- Aglaia sapindina
-
- Species
- Aglaia tomentosa
-
- Species
- Aleurites rockinghamensis
-
- Species
- Alloxylon wickhamii
-
- Species
- Alphitonia petriei
-
- Species
- Alphitonia whitei
-
- Species
- Alstonia muelleriana
-
- Species
- Alstonia scholaris
-
- Species
- Anthocarapa nitidula
-
- Species
- Antidesma bunius
-
- Species
- Antidesma erostre
-
- Species
- Antirhea tenuiflora
-
- Species
- Apodytes brachystylis
-
- Species
- Archidendron grandiflorum
-
- Species
- Archidendron vaillantii
-
- Species
- Archontophoenix cunninghamii
-
- Species
- Argyrodendron peralatum
-
- Species
- Argyrodendron polyandrum
-
- Species
- Argyrodendron trifoliolatum
-
- Species
- Arytera divaricata
-
- Species
- Auranticarpa papyracea
-
- Species
- Austrobuxus megacarpus
-
- Species
- Austromuellera trinervia
-
- Species
- Austrosteenisia blackii
-
- Species
- Backhousia bancroftii
-
- Species
- Backhousia hughesii
-
- Species
- Balanops australiana
-
- Species
- Baloghia parviflora
-
- Species
- Barongia lophandra
-
- Species
- Barringtonia calyptrata
-
- Species
- Beilschmiedia bancroftii
-
- Species
- Beilschmiedia collina
-
- Species
- Beilschmiedia obtusifolia
-
- Species
- Beilschmiedia recurva
-
- Species
- Beilschmiedia tooram
-
- Species
- Beilschmiedia volckii
-
- Species
- Blepharocarya involucrigera
-
- Species
- Bobea myrtoides
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- Species
- Brachychiton acerifolius
-
- Species
- Brackenridgea australiana
-
- Species
- Brombya platynema
-
- Species
- Bubbia semecarpoides
-
- Species
- Buckinghamia celsissima
-
- Species
- Calophyllum sil
-
- Species
- Cananga odorata
-
- Species
- Canarium australasicum
-
- Species
- Canarium muelleri
-
- Species
- Carallia brachiata
-
- Species
- Cardwellia sublimis
-
- Species
- Casearia costulata
-
- Species
- Casearia dallachii
-
- Species
- Castanospermum australe
-
- Species
- Castanospora alphandii
-
- Species
- Catalepidia heyana
-
- Species
- Celtis paniculata
-
- Species
- Ceratopetalum succirubrum
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- Species
- Cerbera inflata
-
- Species
- Chionanthus axillaris
-
- Species
- Chrysophyllum roxburghii
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- Species
- Cinnamomum laubatii
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- Species
- Cissus hypoglauca
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- Species
- Cissus penninervis
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- Species
- Cissus repens
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- Species
- Citronella smythii
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- Species
- Claoxylon tenerifolium
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- Species
- Cleidion javanicum
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- Species
- Cleistanthus apodus
-
- Species
- Cleistanthus myrianthus
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- Species
- Cleistanthus semiopacus
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- Species
- Cnesmocarpon dasyantha
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- Species
- Commersonia bartramia
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- Species
- Cordia dichotoma
-
- Species
- Corynocarpus cribbianus
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- Species
- Croton insularis
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- Species
- Croton triacros
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- Species
- Cryptocarya angulata
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- Species
- Cryptocarya bellendenkerana
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- Species
- Cryptocarya burckiana
-
- Species
- Cryptocarya cocosoides
-
- Species
- Cryptocarya corrugata
-
- Species
- Cryptocarya cunninghamii
-
- Species
- Cryptocarya densiflora
-
- Species
- Cryptocarya endiandrifolia
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- Species
- Cryptocarya glaucocarpa
-
- Species
- Cryptocarya grandis
-
- Species
- Cryptocarya hypospodia
-
- Species
- Cryptocarya leucophylla
-
- Species
- Cryptocarya lividula
-
- Species
- Cryptocarya mackinnoniana
-
- Species
- Cryptocarya melanocarpa
-
- Species
- Cryptocarya murrayi
-
- Species
- Cryptocarya oblata
-
- Species
- Cryptocarya onoprienkoana
-
- Species
- Cryptocarya pleurosperma
-
- Species
- Cryptocarya putida
-
- Species
- Cryptocarya saccharata
-
- Species
- Cryptocarya smaragdina
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- Species
- Cryptocarya vulgaris
-
- Species
- Cupaniopsis foveolata
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- Species
- Cyathea cooperi
-
- Species
- Cyclophyllum coprosmoides
-
- Species
- Cyclophyllum protractum
-
- Species
- Daphnandra repandula
-
- Species
- Darlingia darlingiana
-
- Species
- Davidsonia pruriens
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- Species
- Decaspermum humile
-
- Species
- Dendrocnide corallodesme
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- Species
- Dendrocnide photinophylla
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- Species
- Denhamia celastroides
-
- Species
- Denhamia viridissima
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- Species
- Dinosperma erythrococcum
-
- Species
- Dinosperma melanophloium
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- Species
- Diospyros cupulosa
-
- Species
- Diospyros hebecarpa
-
- Species
- Diospyros pentamera
-
- Species
- Diploglottis bracteata
-
- Species
- Diploglottis diphyllostegia
-
- Species
- Doryphora aromatica
-
- Species
- Drypetes acuminata
-
- Species
- Dysoxylum alliaceum
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- Species
- Dysoxylum arborescens
-
- Species
- Dysoxylum gaudichaudianum
-
- Species
- Dysoxylum oppositifolium
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- Species
- Dysoxylum papuanum
-
- Species
- Dysoxylum parasiticum
-
- Species
- Dysoxylum pettigrewianum
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- Species
- Dysoxylum pumilum
-
- Species
- Dysoxylum rufum
-
- Species
- Elaeocarpus bancroftii
-
- Species
- Elaeocarpus carolinae
-
- Species
- Elaeocarpus coorangooloo
-
- Species
- Elaeocarpus elliffii
-
- Species
- Elaeocarpus eumundii
-
- Species
- Elaeocarpus ferruginiflorus
-
- Species
- Elaeocarpus foveolatus
-
- Species
- Elaeocarpus grandis
-
- Species
- Elaeocarpus ruminatus
-
- Species
- Elaeocarpus sericopetalus
-
- Species
- Elaeodendron melanocarpum
-
- Species
- Elattostachys megalantha
-
- Species
- Emmenosperma cunninghamii
-
- Species
- Endiandra acuminata
-
- Species
- Endiandra bessaphila
-
- Species
- Endiandra compressa
-
- Species
- Endiandra cowleyana
-
- Species
- Endiandra dichrophylla
-
- Species
- Endiandra dielsiana
-
- Species
- Endiandra globosa
-
- Species
- Endiandra hypotephra
-
- Species
- Endiandra impressicosta
-
- Species
- Endiandra insignis
-
- Species
- Endiandra leptodendron
-
- Species
- Endiandra longipedicellata
-
- Species
- Endiandra microneura
-
- Species
- Endiandra montana
-
- Species
- Endiandra palmerstonii
-
- Species
- Endiandra phaeocarpa
-
- Species
- Endiandra sankeyana
-
- Species
- Endiandra wolfei
-
- Species
- Entada phaseoloides
-
- Species
- Erythroxylum australe
-
- Species
- Euodia hylandii
-
- Species
- Eupomatia laurina
-
- Species
- Euroschinus falcatus
-
- Species
- Fagraea cambagei
-
- Species
- Fagraea fagraeacea
-
- Species
- Faradaya splendida
-
- Species
- Ficus crassipes
-
- Species
- Ficus destruens
-
- Species
- Ficus leptoclada
-
- Species
- Ficus obliqua
-
- Species
- Ficus septica
-
- Species
- Ficus triradiata
-
- Species
- Ficus watkinsiana
-
- Species
- Firmiana papuana
-
- Species
- Flindersia acuminata
-
- Species
- Flindersia bourjotiana
-
- Species
- Flindersia brayleyana
-
- Species
- Flindersia ifflana
-
- Species
- Flindersia laevicarpa
-
- Species
- Flindersia pimenteliana
-
- Species
- Flindersia schottiana
-
- Species
- Fontainea picrosperma
-
- Species
- Franciscodendron laurifolium
-
- Species
- Galbulimima baccata
-
- Species
- Garcinia gibbsiae
-
- Species
- Garcinia warrenii
-
- Species
- Gardenia ovularis
-
- Species
- Geissois biagiana
-
- Species
- Gevuina bleasdalei
-
- Species
- Gillbeea adenopetala
-
- Species
- Gillbeea whypallana
-
- Species
- Glochidion sumatranum
-
- Species
- Gmelina fasciculiflora
-
- Species
- Gomphandra australiana
-
- Species
- Goniothalamus australis
-
- Species
- Gossia bidwillii
-
- Species
- Gossia grayi
-
- Species
- Gossia hillii
-
- Species
- Gossia lewisensis
-
- Species
- Gossia myrsinocarpa
-
- Species
- Gossia shepherdii
-
- Species
- Grevillea baileyana
-
- Species
- Guioa lasioneura
-
- Species
- Guioa montana
-
- Species
- Gynochthodes oresbia
-
- Species
- Halfordia kendack
-
- Species
- Hedycarya loxocarya
-
- Species
- Helicia australasica
-
- Species
- Helicia lamingtoniana
-
- Species
- Helicia nortoniana
-
- Species
- Hollandaea sayeriana
-
- Species
- Homalium circumpinnatum
-
- Species
- Hylandia dockrillii
-
- Species
- Idiospermum australiense
-
- Species
- Irvingbaileya australis
-
- Species
- Ixora oreogena
-
- Species
- Lepidopetalum fructoglabrum
-
- Species
- Lepidozamia hopei
-
- Species
- Lethedon setosa
-
- Species
- Levieria acuminata
-
- Species
- Lindsayomyrtus racemoides
-
- Species
- Litsea bindoniana
-
- Species
- Litsea connorsii
-
- Species
- Litsea fawcettiana
-
- Species
- Litsea leefeana
-
- Species
- Lomatia fraxinifolia
-
- Species
- Macaranga inamoena
-
- Species
- Macaranga subdentata
-
- Species
- Mallotus mollissimus
-
- Species
- Mallotus philippensis
-
- Species
- Mallotus polyadenos
-
- Species
- Margaritaria indica
-
- Species
- Maytenus disperma
-
- Species
- Medicosma fareana
-
- Species
- Melicope elleryana
-
- Species
- Melicope jonesii
-
- Species
- Melicope vitiflora
-
- Species
- Miliusa horsfieldii
-
- Species
- Millettia pinnata
-
- Species
- Mischarytera lautereriana
-
- Species
- Mischocarpus grandissimus
-
- Species
- Mischocarpus lachnocarpus
-
- Species
- Mischocarpus macrocarpus
-
- Species
- Mischocarpus stipitatus
-
- Species
- Mitrephora diversifolia
-
- Species
- Morinda citrifolia
-
- Species
- Musa banksii
-
- Species
- Musgravea heterophylla
-
- Species
- Musgravea stenostachya
-
- Species
- Myristica insipida
-
- Species
- Myrsine achradifolia
-
- Species
- Myrsine porosa
-
- Species
- Nauclea orientalis
-
- Species
- Neisosperma poweri
-
- Species
- Neolitsea dealbata
-
- Species
- Neorites kevedianus
-
- Species
- Niemeyera prunifera
-
- Species
- Normanbya normanbyi
-
- Species
- Olea paniculata
-
- Species
- Opisthiolepis heterophylla
-
- Species
- Oraniopsis appendiculata
-
- Species
- Ormosia ormondii
-
- Species
- Palaquium galactoxylon
-
- Species
- Parsonsia latifolia
-
- Species
- Petraeovitex multiflora
-
- Species
- Pilidiostigma tropicum
-
- Species
- Pisonia umbellifera
-
- Species
- Pitaviaster haplophyllus
-
- Species
- Pittosporum wingii
-
- Species
- Placospermum coriaceum
-
- Species
- Podocarpus grayae
-
- Species
- Polyalthia michaelii
-
- Species
- Polyalthia nitidissima
-
- Species
- Polyosma alangiacea
-
- Species
- Polyosma hirsuta
-
- Species
- Polyosma rhytophloia
-
- Species
- Polyscias australiana
-
- Species
- Polyscias elegans
-
- Species
- Polyscias murrayi
-
- Species
- Pouteria brownlessiana
-
- Species
- Pouteria castanosperma
-
- Species
- Pouteria chartacea
-
- Species
- Pouteria euphlebia
-
- Species
- Pouteria myrsinifolia
-
- Species
- Pouteria myrsinodendron
-
- Species
- Pouteria papyracea
-
- Species
- Pouteria pearsoniorum
-
- Species
- Pouteria xerocarpa
-
- Species
- Prumnopitys ladei
-
- Species
- Prunus turneriana
-
- Species
- Pseudoweinmannia lachnocarpa
-
- Species
- Pseuduvaria froggattii
-
- Species
- Psydrax lamprophylla
-
- Species
- Psydrax montigena
-
- Species
- Psydrax tropica
-
- Species
- Pullea stutzeri
-
- Species
- Quassia baileyana
-
- Species
- Rhamnella vitiensis
-
- Species
- Rhodamnia blairiana
-
- Species
- Rhodamnia costata
-
- Species
- Rhodamnia sessiliflora
-
- Species
- Rhodamnia spongiosa
-
- Species
- Rhodomyrtus macrocarpa
-
- Species
- Rhodomyrtus pervagata
-
- Species
- Ristantia pachysperma
-
- Species
- Rockinghamia angustifolia
-
- Species
- Ryparosa javanica
-
- Species
- Sarcopteryx montana
-
- Species
- Sarcopteryx reticulata
-
- Species
- Sarcotoechia cuneata
-
- Species
- Sarcotoechia lanceolata
-
- Species
- Sarcotoechia protracta
-
- Species
- Schefflera actinophylla
-
- Species
- Scolopia braunii
-
- Species
- Siphonodon membranaceus
-
- Species
- Sloanea langii
-
- Species
- Sloanea macbrydei
-
- Species
- Sphalmium racemosum
-
- Species
- Sphenostemon lobosporus
-
- Species
- Steganthera macooraia
-
- Species
- Stenocarpus davallioides
-
- Species
- Stenocarpus reticulatus
-
- Species
- Stenocarpus sinuatus
-
- Species
- Storckiella australiensis
-
- Species
- Streblus brunonianus
-
- Species
- Sundacarpus amarus
-
- Species
- Symplocos gittinsii
-
- Species
- Symplocos paucistaminea
-
- Species
- Synima cordierorum
-
- Species
- Syzygium apodophyllum
-
- Species
- Syzygium cormiflorum
-
- Species
- Syzygium cryptophlebium
-
- Species
- Syzygium dansiei
-
- Species
- Syzygium endophloium
-
- Species
- Syzygium erythrocalyx
-
- Species
- Syzygium gustavioides
-
- Species
- Syzygium johnsonii
-
- Species
- Syzygium kuranda
-
- Species
- Syzygium luehmannii
-
- Species
- Syzygium malaccense
-
- Species
- Syzygium maraca
-
- Species
- Syzygium monospermum
-
- Species
- Syzygium papyraceum
-
- Species
- Syzygium pseudofastigiatum
-
- Species
- Syzygium puberulum
-
- Species
- Syzygium sayeri
-
- Species
- Syzygium trachyphloium
-
- Species
- Syzygium wesa
-
- Species
- Tapeinosperma pseudojambosa
-
- Species
- Terminalia complanata
-
- Species
- Terminalia sericocarpa
-
- Species
- Ternstroemia cherryi
-
- Species
- Tetrameles nudiflora
-
- Species
- Tetrasynandra laxiflora
-
- Species
- Toechima erythrocarpum
-
- Species
- Toechima monticola
-
- Species
- Toona ciliata
-
- Species
- Vavaea amicorum
-
- Species
- Viticipremna queenslandica
-
- Species
- Waterhousea unipunctata
-
- Species
- Wilkiea macrophylla
-
- Species
- Wilkiea wardellii
-
- Species
- Wrightia laevis
-
- Species
- Xanthophyllum octandrum
-
- Species
- Xanthostemon whitei
-
- Species
- Xylopia maccreae
-
- Species
- Zanthoxylum ovalifolium
-
- Species
- Zanthoxylum veneficum
-
- Intellectual Rights, Licence and Usage Conditions
-
CC-BY-4_0 Special Conditions: None
- Data Table
-
- Name
- mtrf_rainforest_tree_demographic_data_2011_2013_ep34_pp399t667.csv
- Description
- mtrf Rainforest Tree Demographic Data_
- Attribute Information
-
epnumber
- Name
- epnumber
- Definition
- CSIRO experimental plot number
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
stemnumber- Name
- stemnumber
- Definition
- Alphanumeric character assigned to each stem
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
family- Name
- family
- Definition
- Taxonomic family
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
genus- Name
- genus
- Definition
- Taxonomic genus
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
taxon- Name
- taxon
- Definition
- Full taxonomic name
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
taxonauth- Name
- taxonauth
- Definition
- Full taxonomic name with author
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
ala_apni_taxon_lsid- Name
- ala_apni_taxon_lsid
- Definition
- Life Science Identifier (LSID) sourced from the Australian Plant Name Index http://www.anbg.gov.au/apni/
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
ala_apni_taxon_uri- Name
- ala_apni_taxon_uri
- Definition
- Australian Plant Name Index URI
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
wettropicsendemic- Name
- wettropicsendemic
- Definition
- Endemic to the Wet Tropic Bioregion of Australia
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
wettropicsendemic_label- Name
- wettropicsendemic_label
- Definition
- wettropicsendemic_label
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- wettropicsendemic_label
coordinates_x_metres- Name
- coordinates_x_metres
- Definition
- Stem position along the 100 m axis
- Measurement Type
- interval
- Measurement Domain
-
- Standard Unit
- meter
- Number Type
- whole
coordinates_y_metres- Name
- coordinates_y_metres
- Definition
- Stem position along the 50 m axis
- Measurement Type
- interval
- Measurement Domain
-
- Standard Unit
- meter
- Number Type
- whole
year- Name
- year
- Definition
- Year of census
- Measurement Type
- dateTime
- Measurement Domain
-
- Format
- yyyy
dbh_centimetres- Name
- dbh_centimetres
- Definition
- Diameter of the stem (cm) at breast height (1.3 m) or otherwise as stated in the methods description
- Measurement Type
- ratio
- Measurement Domain
-
- Standard Unit
- centimeter
- Number Type
- real
height_metres- Name
- height_metres
- Definition
- Height of any stem (m) estimated post-establishment
- Measurement Type
- ratio
- Measurement Domain
-
- Standard Unit
- meter
- Number Type
- whole
status- Name
- status
- Definition
- Dead or Alive at the census shown in variable ‘year’
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
comment- Name
- comment
- Definition
- Comment on the health of the stem or status of the measurement
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
comment_label- Name
- comment_label
- Definition
- comment_label
- Measurement Type
- nominal
- Measurement Domain
-
- Text Domain
-
- Definition
- Text
- Number Of Records
- 7925
- Physical Structure Description
-
- Object Name
- mtrf_rainforest_tree_demographic_data_2011_2013_ep34_pp399t667.csv
- Size
- 1872567 byte
- Text Format
-
- Number of Header Lines
- 1
- Record Delimiter
- #x0A
- Attribute Orientation
- column
- Simple Delimited
-
- Field Delimiter
- ,
- Distribution
-
Online
- URL
- ltern2.556.1
- Access
-
- Access Control
-
- Auth System
- knb
- Order
- allowFirst
- Allow:
-
Permission Principal [read] cn=allusers,o=unaffiliated,dc=ecoinformatics,dc=org [all] cn=submitters,o=unaffiliated,dc=ecoinformatics,dc=org
- Additional Metadata Links
-
additionalLinksAdditional Metadata : additionalLinks
- Metadata
-
- additionalLinks
-
- url
-
- @name
- The Tropical Rainforest Plot Network homepage
- Access
-
- Access Control
-
- Auth System
- knb
- Order
- allowFirst
- Allow:
-
Permission Principal [read] public [read] uid=metcalfe,o=unaffiliated,dc=ecoinformatics,dc=org [read] uid=bradford,o=unaffiliated,dc=ecoinformatics,dc=org [all] cn=submitters,o=unaffiliated,dc=ecoinformatics,dc=org
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