Data

Kidman Springs Long Term Exclosure Study - Vegetation Changes 1973-2002

Terrestrial Ecosystem Research Network
Liedloff, Adam ; Cowley, Robyn ; Bastin, Gary ; Ludwig, John
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ctx_ver=Z39.88-2004&rft_val_fmt=info%3Aofi%2Ffmt%3Akev%3Amtx%3Adc&rfr_id=info%3Asid%2FANDS&rft_id=http://geonetwork.tern.org.au/geonetwork/srv/eng/catalog.search#/metadata/d8a667e6-e5da-4a0b-9bd2-f44acacae3a8&rft.title=Kidman Springs Long Term Exclosure Study - Vegetation Changes 1973-2002&rft.identifier=http://geonetwork.tern.org.au/geonetwork/srv/eng/catalog.search#/metadata/d8a667e6-e5da-4a0b-9bd2-f44acacae3a8&rft.publisher=Terrestrial Ecosystem Research Network&rft.description=The data are herbage biomass (dry weight, gram per square metre) and density of trees and shrubs (number per transect) measured inside cattle-proof exclosures and on adjacent grazed areas on two sites of different soils at Kidman Springs, Northern Territory between 1973 and 2002.The use of destocking as a means of promoting pasture recovery was evaluated on two important rangeland types of the semi-arid tropics of north west Australia. Fenced areas approximately 500-m square were established in 1973 on Victoria River Research Station, Kidman Springs, Northern Territory. One site, called Black Soil, was located on a cracking clay soil with shrubs (mainly Carissa lanceolate, conkerberry) and trees (Lysiphyllum cunninghamii, bauhinia and Terminalia volucris, rosewood) on the margins. The herbage layer was dominated by Chrysopogon fallax (ribbon grass) and Iseilema fragile (Flinders grass). This site was minimally affected by past grazing and was deemed in good condition. Two exclosures were constructed on red calcareous soils; one site eroded (Red Soil, eroded) and the other not (Red Soil, not eroded). When data collection commenced, the red-soil sites had an open tree and shrub layer of Eucalyptus pruinose (silver leaf gum), E. terminalis (bloodwood) and C. lanceolata. The herbage layer at the good site was dominated by biennial Enneapogon spp. (limestone grass) with sparse Brachyachne convergens (native couch), Sporobolus australasicus (fairy grass) and Aristida spp. (wire grasses) present in the degraded state. Six permanent plots (45 m by 30 m) were randomly located inside and outside of each of the three exclosures. Herbage biomass was measured by clipping individual species. Species were harvested within five randomly placed 1-m square quadrats at each plot. Samples were oven dried to obtain dry weight. Additional biomass data were obtained in two years (1989 and 1994) by estimating yield and composition using BOTANAL (Tothill et al. 1992) within 15 randomly placed 1-m square quadrats at each of the six permanently marked sampling locations. Trees and shrubs, categorised by lifeform (juvenile or mature), were counted within fixed 0.14-ha areas at each of the permanent sampling locations used to collect herbage biomass data. These numbers were multiplied by 7.14 to give the number per hectare (i.e. density). For analysis, the dry-weight biomass of individual species was sequentially grouped into functional groups: annual or perennial grasses and forbs, total grass and forb, and total herbage biomass. The data are provided by functional group and the biomass of dominant species for each soil type. Similarly, the densities of tree and shrub species by lifeform were aggregated to juvenile trees or shrubs and mature trees or shrubs and, from there, total trees or total shrubs. Data are provided by species with the user to aggregate to lifeform and age groups if required. Two separate analyses were conducted based on time since exclosure. In the first (Foran et al. 1985), analysis of variance was conducted on the herbage biomass and woody density data to examine the effect of destocking and year (essentially, prior wet-season rainfall). Stepwise multiple linear regression analysis was used to define the influence of different factors such as rainfall, stocking rate and shrub density on the levels of standing biomass in the grazed treatments. For the red-soil sites in their second reporting period (Bastin et al. 2003), repeated-measures analysis of variance was used to explore whether there was a significant change (slope) across time (years since exclosure) and, if so, whether changes across time differed for inside and outside the exclosures (treatments). If changes across time appeared to be non-linear, quadratic and cubic polynomials were explored.Progress Code: completedMaintenance and Update Frequency: notPlanned&rft.creator=Liedloff, Adam &rft.creator=Cowley, Robyn &rft.creator=Bastin, Gary &rft.creator=Ludwig, John &rft.date=2024&rft.edition=1&rft.coverage=Victoria River Research Station, Kidman Springs, Northern Territory.&rft.coverage=northlimit=-16.06; southlimit=-16.118; westlimit=130.945; eastLimit=130.962; projection=EPSG:4326&rft_rights=Creative Commons Attribution 4.0 International Licence http://creativecommons.org/licenses/by/4.0&rft_rights=TERN services are provided on an as-is and as available basis. Users use any TERN services at their discretion and risk. They will be solely responsible for any damage or loss whatsoever that results from such use including use of any data obtained through TERN and any analysis performed using the TERN infrastructure. <br />Web links to and from external, third party websites should not be construed as implying any relationships with and/or endorsement of the external site or its content by TERN. <br /><br />Please advise any work or publications that use this data via the online form at https://www.tern.org.au/research-publications/#reporting&rft_rights=Please cite this dataset as {Author} ({PublicationYear}). {Title}. {Version, as appropriate}. Terrestrial Ecosystem Research Network. Dataset. {Identifier}.&rft_subject=environment&rft_subject=RECLAMATION/REVEGETATION/RESTORATION&rft_subject=GRAZING DYNAMICS / PLANT ECOLOGY&rft_subject=EARTH SCIENCE&rft_subject=BIOSPHERE&rft_subject=ECOLOGICAL DYNAMICS&rft_subject=COMMUNITY DYNAMICS&rft_subject=RANGELAND&rft_subject=Terrestrial Ecology&rft_subject=BIOLOGICAL SCIENCES&rft_subject=ECOLOGY&rft_subject=Conservation and Biodiversity&rft_subject=ENVIRONMENTAL SCIENCES&rft_subject=ENVIRONMENTAL SCIENCE AND MANAGEMENT&rft_subject=Kidman Springs Red & Black Soil Exclosures&rft_subject=tree count (Number)&rft_subject=Number&rft_subject=shrub count (Number)&rft_subject=grazing present (Unitless)&rft_subject=Unitless&rft_subject=erosion present (Unitless)&rft_subject=above-ground herbage biomass (Gram per Square Metre)&rft_subject=Gram per Square Metre&rft_subject=30 meters - < 100 meters&rft_subject=irregular&rft_subject=Brachyachne convergens (F.Muell.) Stapf&rft_subject=Enneapogon polyphyllus (Domin) N.T.Burb.&rft_subject=Heteropogon contortus (L.) P.Beauv. ex Roem. & Schult.&rft_subject=Dichanthium P.Willemet&rft_subject=Iseilema Andersson&rft_subject=Chrysopogon fallax S.T.Blake&rft_subject=Acacia bidwillii Benth.&rft_subject=Acacia sp.&rft_subject=Atalaya hemiglauca (F.Muell.) F.Muell. ex Benth.&rft_subject=Cochlospermum fraseri Planch.&rft_subject=Ehretia saligna R.Br.&rft_subject=Eucalyptus confertiflora Kippist&rft_subject=Eucalyptus pruinosa Schauer&rft_subject=Eucalyptus microtheca F.Muell.&rft_subject=Eucalyptus terminalis F.Muell.&rft_subject=Eucalyptus sp.&rft_subject=Gyrocarpus americanus Jacq.&rft_subject=Hakea arborescens R.Br.&rft_subject=Lysiphyllum cunninghamii (Benth.) de Wit&rft_subject=Premna acuminata R.Br.&rft_subject=Terminalia arostrata Ewart & O.B.Davies&rft_subject=Terminalia volucris R.Br. ex Benth.&rft_subject=Ventilago viminalis Hook.&rft_subject=Acacia colei Maslin & L.A.J.Thomson&rft_subject=Acacia farnesiana (L.) Willd.&rft_subject=Calotropis procera (Aiton) R.Br. ex W.T.Aiton&rft_subject=Carissa lanceolata R.Br.&rft_subject=Senna oligoclada (F.Muell.) Randell&rft_subject=Grewia retusifolia Kurz&rft.type=dataset&rft.language=English Access the data

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TERN services are provided on an "as-is" and "as available" basis. Users use any TERN services at their discretion and risk. They will be solely responsible for any damage or loss whatsoever that results from such use including use of any data obtained through TERN and any analysis performed using the TERN infrastructure.
Web links to and from external, third party websites should not be construed as implying any relationships with and/or endorsement of the external site or its content by TERN.

Please advise any work or publications that use this data via the online form at https://www.tern.org.au/research-publications/#reporting

Please cite this dataset as {Author} ({PublicationYear}). {Title}. {Version, as appropriate}. Terrestrial Ecosystem Research Network. Dataset. {Identifier}.

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Brief description

The data are herbage biomass (dry weight, gram per square metre) and density of trees and shrubs (number per transect) measured inside cattle-proof exclosures and on adjacent grazed areas on two sites of different soils at Kidman Springs, Northern Territory between 1973 and 2002.

Lineage

The use of destocking as a means of promoting pasture recovery was evaluated on two important rangeland types of the semi-arid tropics of north west Australia.

Fenced areas approximately 500-m square were established in 1973 on Victoria River Research Station, Kidman Springs, Northern Territory. One site, called Black Soil, was located on a cracking clay soil with shrubs (mainly Carissa lanceolate, conkerberry) and trees (Lysiphyllum cunninghamii, bauhinia and Terminalia volucris, rosewood) on the margins. The herbage layer was dominated by Chrysopogon fallax (ribbon grass) and Iseilema fragile (Flinders grass). This site was minimally affected by past grazing and was deemed in good condition. Two exclosures were constructed on red calcareous soils; one site eroded (Red Soil, eroded) and the other not (Red Soil, not eroded). When data collection commenced, the red-soil sites had an open tree and shrub layer of Eucalyptus pruinose (silver leaf gum), E. terminalis (bloodwood) and C. lanceolata. The herbage layer at the good site was dominated by biennial Enneapogon spp. (limestone grass) with sparse Brachyachne convergens (native couch), Sporobolus australasicus (fairy grass) and Aristida spp. (wire grasses) present in the degraded state.

Six permanent plots (45 m by 30 m) were randomly located inside and outside of each of the three exclosures.

Herbage biomass was measured by clipping individual species. Species were harvested within five randomly placed 1-m square quadrats at each plot. Samples were oven dried to obtain dry weight. Additional biomass data were obtained in two years (1989 and 1994) by estimating yield and composition using BOTANAL (Tothill et al. 1992) within 15 randomly placed 1-m square quadrats at each of the six permanently marked sampling locations.

Trees and shrubs, categorised by lifeform (juvenile or mature), were counted within fixed 0.14-ha areas at each of the permanent sampling locations used to collect herbage biomass data. These numbers were multiplied by 7.14 to give the number per hectare (i.e. density).

For analysis, the dry-weight biomass of individual species was sequentially grouped into functional groups: annual or perennial grasses and forbs, total grass and forb, and total herbage biomass. The data are provided by functional group and the biomass of dominant species for each soil type. Similarly, the densities of tree and shrub species by lifeform were aggregated to juvenile trees or shrubs and mature trees or shrubs and, from there, total trees or total shrubs. Data are provided by species with the user to aggregate to lifeform and age groups if required.

Two separate analyses were conducted based on time since exclosure. In the first (Foran et al. 1985), analysis of variance was conducted on the herbage biomass and woody density data to examine the effect of destocking and year (essentially, prior wet-season rainfall). Stepwise multiple linear regression analysis was used to define the influence of different factors such as rainfall, stocking rate and shrub density on the levels of standing biomass in the grazed treatments. For the red-soil sites in their second reporting period (Bastin et al. 2003), repeated-measures analysis of variance was used to explore whether there was a significant change (slope) across time (years since exclosure) and, if so, whether changes across time differed for inside and outside the exclosures (treatments). If changes across time appeared to be non-linear, quadratic and cubic polynomials were explored.

Progress Code: completed
Maintenance and Update Frequency: notPlanned

Notes

Credit
We at TERN acknowledge the Traditional Owners and Custodians throughout Australia, New Zealand and all nations. We honour their profound connections to land, water, biodiversity and culture and pay our respects to their Elders past, present and emerging.
Purpose
Initially, in the 1970s and 1980s, to test the effectiveness of destocking, using exclosures, as a means of promoting pasture recovery on two important rangeland types of the semi-arid tropics of north west Australia. Subsequently, to determine the longer-term (30+ years) dynamics of these red-soil and black-soil vegetation communities.

Created: 1973-04-11

Issued: 2024-12-04

Modified: 2026-03-02

Data time period: 1973-04-11 to 2002-06-30

This dataset is part of a larger collection

Click to explore relationships graph

130.962,-16.06 130.962,-16.118 130.945,-16.118 130.945,-16.06 130.962,-16.06

130.9535,-16.089

text: Victoria River Research Station, Kidman Springs, Northern Territory.

Subjects
30 meters - < 100 meters | Acacia bidwillii Benth. | Acacia colei Maslin & L.A.J.Thomson | Acacia farnesiana (L.) Willd. | Acacia sp. | Atalaya hemiglauca (F.Muell.) F.Muell. ex Benth. | Biological Sciences | BIOSPHERE | Brachyachne convergens (F.Muell.) Stapf | COMMUNITY DYNAMICS | Calotropis procera (Aiton) R.Br. ex W.T.Aiton | Carissa lanceolata R.Br. | Chrysopogon fallax S.T.Blake | Cochlospermum fraseri Planch. | Conservation and Biodiversity | Dichanthium P.Willemet | EARTH SCIENCE | ECOLOGICAL DYNAMICS | Ecology | Environmental Science and Management | Environmental Sciences | Ehretia saligna R.Br. | Enneapogon polyphyllus (Domin) N.T.Burb. | Eucalyptus confertiflora Kippist | Eucalyptus microtheca F.Muell. | Eucalyptus pruinosa Schauer | Eucalyptus sp. | Eucalyptus terminalis F.Muell. | GRAZING DYNAMICS / PLANT ECOLOGY | Gram per Square Metre | Grewia retusifolia Kurz | Gyrocarpus americanus Jacq. | Hakea arborescens R.Br. | Heteropogon contortus (L.) P.Beauv. ex Roem. & Schult. | Iseilema Andersson | Kidman Springs Red & Black Soil Exclosures | Lysiphyllum cunninghamii (Benth.) de Wit | Number | Premna acuminata R.Br. | RANGELAND | RECLAMATION/REVEGETATION/RESTORATION | Senna oligoclada (F.Muell.) Randell | Terminalia arostrata Ewart & O.B.Davies | Terminalia volucris R.Br. ex Benth. | Terrestrial Ecology | Unitless | Ventilago viminalis Hook. | above-ground herbage biomass (Gram per Square Metre) | environment | erosion present (Unitless) | grazing present (Unitless) | irregular | shrub count (Number) | tree count (Number) |

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Other Information
Point-of-truth metadata URL

uri : https://geonetwork.tern.org.au/geonetwork/srv/eng/catalog.search#/metadata/d8a667e6-e5da-4a0b-9bd2-f44acacae3a8

Foran, B., Bastin, G., & Hill, B. (1985). The pasture dynamics and management of two rangeland communities in the Victoria River District of the Northern Territory. The Rangeland Journal, 7(2), 107.

doi : https://doi.org/10.1071/RJ9850107

Bastin, G. N., Ludwig, J. A., Eager, R. W., Liedloff, A. C., Andison, R. T., & Cobiac, M. D. (2003). Vegetation changes in a semiarid tropical savanna, northern Australia: 1973–2002. Rangeland Journal, 25(1), 3–19.

doi : https://doi.org/10.1071/RJ03001

Tothill, J.C.; Hargreaves, J.N.G.; Jones, R.M.; McDonals, C.K. (1992). BOTANAL - A Comprehensive Sampling and Computing Procedure for Estimating Pasture Yield and Composition. 1. Field Sampling . St Lucia, Qld.: CSIRO Division of Tropical Crops and Pastures; 1992.

doi : https://doi.org/10.4225/08/58712e506e989