Data

Norfolk Island soil permeability DSM attribute

Commonwealth Scientific and Industrial Research Organisation
Petheram, Cuan ; Philip, Seonaid ; Bui, Elisabeth ; Wilson, Peter ; Fitzpatrick, Rob
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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=info:doi10.25919/3nzw-xa76&rft.title=Norfolk Island soil permeability DSM attribute&rft.identifier=10.25919/3nzw-xa76&rft.publisher=Commonwealth Scientific and Industrial Research Organisation (CSIRO)&rft.description=Soil permeability is one of nine soil attributes analysed as one component of a digital soil mapping exercise undertaken as part of the Norfolk Island Water Resource Assessment (NIWRA). It was selected due to its importance to groundwater recharge, surface water storage and managed aquifer recharge. Soil permeability indicates the rate of water movement into and through the soil and is described as defined by the National Committee on Soil and Terrain 2009 (NCST) soil permeability descriptions. This raster data represents a modelled dataset of soil permeability and is derived from field measured site data and environmental covariates. Data values are: 1 Moderately permeable, 2 Highly permeable. A companion dataset presenting reliability of this data is also provided and can be found described in the lineage section of this metadata record. Processing was carried out in the ranger package inside R and attributes were modelled using a Random Forest approach. Further soil permeability information can be found in the NIWRA technical report (Petheram et al., 2020). The DSM process is described in Appendix E of the NIWRA technical report.This soil permeability dataset has been generated from a range of inputs and processing steps. The following is an overview of the methods detailed in Petheram et al. 2020. 1. Collated existing data (relating to: soils, climate, topography, natural resources, remotely sensed, of various formats: reports, spatial vector, spatial raster). 2. Selection of additional soil and land attribute site data locations by a conditioned Latin hypercube statistical sampling method applied across the covariate data space. 3. Fieldwork was carried out to collect new attribute data, soil samples for analysis and build an understanding of geomorphology and landscape processes. 4. Database analysis was performed to extract the data to specific selection criteria required for the attribute to be modelled. 5. The R statistical programming environment was used for the attribute computing. Models were built from selected input data and covariate data using predictive learning from a Random Forest approach implemented in the ranger R package. 6. Created soil permeability Digital Soil Mapping (DSM) attribute raster dataset. DSM data is a geo-referenced dataset, generated from field observations coupled with environmental covariate data through quantitative relationships. It applies pedometrics - the use of mathematical and statistical models that combine information from soil observations with information contained in correlated environmental variables and remote sensing images. 7. Companion predicted reliability data was produced from the 500 individual Random Forest attribute models created. 8. QA Quality assessment of this DSM attribute data was conducted by three methods. Method 1: Statistical (quantitative) method of the model and input data. Testing the quality of the DSM models was carried out using data withheld from model computations and expressed as OOB and R squared results, giving an estimate of the reliability of the model predictions. Method 2: Statistical (quantitative) assessment of the spatial attribute output data presented as a raster of the attributes “reliability”. This used the 500 individual trees of the attributes RF models to generate 500 datasets of the attribute to estimate model reliability for each attribute. For categorical attributes the method for estimating reliability is the Confusion Index. This data is supplied. Method 3: On-ground expert (qualitative) examination of outputs.&rft.creator=Petheram, Cuan &rft.creator=Philip, Seonaid &rft.creator=Bui, Elisabeth &rft.creator=Wilson, Peter &rft.creator=Fitzpatrick, Rob &rft.date=2021&rft.edition=v1&rft.coverage=northlimit=-28.99; southlimit=-29.0675; westlimit=167.91; eastLimit=168.0; uplimit=320.0; downlimit=0.0; projection=WGS84&rft_rights=All Rights (including copyright) CSIRO 2020.&rft_rights=Creative Commons Attribution https://creativecommons.org/licenses/by/4.0/&rft_subject=Norfolk Island&rft_subject=soil permeability&rft_subject=soil&rft_subject=digital soil mapping&rft_subject=soil infiltration&rft_subject=groundwater recharge&rft_subject=Hydrogeology&rft_subject=EARTH SCIENCES&rft_subject=PHYSICAL GEOGRAPHY AND ENVIRONMENTAL GEOSCIENCE&rft_subject=Soil Sciences not elsewhere classified&rft_subject=ENVIRONMENTAL SCIENCES&rft_subject=SOIL SCIENCES&rft_subject=Environmental Management&rft_subject=ENVIRONMENTAL SCIENCE AND MANAGEMENT&rft_subject=Surfacewater Hydrology&rft_subject=Land Use and Environmental Planning&rft_subject=BUILT ENVIRONMENT AND DESIGN&rft_subject=URBAN AND REGIONAL PLANNING&rft.type=dataset&rft.language=English Access the data

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All Rights (including copyright) CSIRO 2020.

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Brief description

Soil permeability is one of nine soil attributes analysed as one component of a digital soil mapping exercise undertaken as part of the Norfolk Island Water Resource Assessment (NIWRA). It was selected due to its importance to groundwater recharge, surface water storage and managed aquifer recharge. Soil permeability indicates the rate of water movement into and through the soil and is described as defined by the National Committee on Soil and Terrain 2009 (NCST) soil permeability descriptions. This raster data represents a modelled dataset of soil permeability and is derived from field measured site data and environmental covariates. Data values are: 1 Moderately permeable, 2 Highly permeable. A companion dataset presenting reliability of this data is also provided and can be found described in the lineage section of this metadata record. Processing was carried out in the ranger package inside R and attributes were modelled using a Random Forest approach. Further soil permeability information can be found in the NIWRA technical report (Petheram et al., 2020). The DSM process is described in Appendix E of the NIWRA technical report.

Lineage

This soil permeability dataset has been generated from a range of inputs and processing steps. The following is an overview of the methods detailed in Petheram et al. 2020. 1. Collated existing data (relating to: soils, climate, topography, natural resources, remotely sensed, of various formats: reports, spatial vector, spatial raster). 2. Selection of additional soil and land attribute site data locations by a conditioned Latin hypercube statistical sampling method applied across the covariate data space. 3. Fieldwork was carried out to collect new attribute data, soil samples for analysis and build an understanding of geomorphology and landscape processes. 4. Database analysis was performed to extract the data to specific selection criteria required for the attribute to be modelled. 5. The R statistical programming environment was used for the attribute computing. Models were built from selected input data and covariate data using predictive learning from a Random Forest approach implemented in the ranger R package. 6. Created soil permeability Digital Soil Mapping (DSM) attribute raster dataset. DSM data is a geo-referenced dataset, generated from field observations coupled with environmental covariate data through quantitative relationships. It applies pedometrics - the use of mathematical and statistical models that combine information from soil observations with information contained in correlated environmental variables and remote sensing images. 7. Companion predicted reliability data was produced from the 500 individual Random Forest attribute models created. 8. QA Quality assessment of this DSM attribute data was conducted by three methods. Method 1: Statistical (quantitative) method of the model and input data. Testing the quality of the DSM models was carried out using data withheld from model computations and expressed as OOB and R squared results, giving an estimate of the reliability of the model predictions. Method 2: Statistical (quantitative) assessment of the spatial attribute output data presented as a raster of the attributes “reliability”. This used the 500 individual trees of the attributes RF models to generate 500 datasets of the attribute to estimate model reliability for each attribute. For categorical attributes the method for estimating reliability is the Confusion Index. This data is supplied. Method 3: On-ground expert (qualitative) examination of outputs.

Data time period: 2019-07-01 to 2020-06-30

This dataset is part of a larger collection

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168,-28.99 168,-29.0675 167.91,-29.0675 167.91,-28.99 168,-28.99

167.955,-29.02875

Identifiers