Data

Flora and Soil Surveys for Senior Secondary Biology and Geography

Terrestrial Ecosystem Research Network
Terrestrial Ecosystem Research Network
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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/e35b48f3-2cf4-4d2e-9744-3c6bb90aa7ce&rft.title=Flora and Soil Surveys for Senior Secondary Biology and Geography&rft.identifier=http://geonetwork.tern.org.au/geonetwork/srv/eng/catalog.search#/metadata/e35b48f3-2cf4-4d2e-9744-3c6bb90aa7ce&rft.publisher=Terrestrial Ecosystem Research Network&rft.description=This dataset contains flora, vegetation structure and soil survey data collected by senior secondary school students as part of ecological monitoring activities aligned with the Australian senior secondary Biology and Geography curricula. Data are collected across Australia from disturbed and undisturbed ecosystems, or from contrasting ecosystem types, using field methods adapted from TERN's ecological monitoring protocols.Parameters may include plant composition and abundance, species diversity, canopy cover, leaf litter cover and depth, seedling abundance, basal area, slope, soil characteristics, disturbance history.Introduction Data were collected using a modified version of widely adopted ecological monitoring and fieldwork techniques, including those outlined in TERN's Ecological Field Monitoring Protocols (EMSA), which provide standardised methods for monitoring Australia's environment at the continental scale (Laws, 2023b) to compare either: • A disturbed and undisturbed ecosystem, or • Two ecosystems that can be easily differentiated based on vegetation structure Data types include: • Vegetation structure • Species diversity • Soil characteristics   Site Selection At each site, two subsites were selected to compare species diversity using measures such as species richness and the Simpson's Diversity Index, e.g.: • An undisturbed reference ecosystem vs a disturbed ecosystem of the same type, undergoing recovery. • Two regional ecosystem of different types, e.g., dry sclerophyll forest vs e.g., rainforest or wet sclerophyll forest.   Data Collection At each subsite, data were collected across multiple 5x5 m plots. Ideally a minimum of 10 plots were sampled at each subsite. The 5 x 5 m plots were delimited using transect tape. At each plot the following data were collected: 1. General observations: a. The canopy cover was estimated using a camera, PVC tube and canopy cover chart. The iPad was placed on the ground and held horizontally with the camera pointing towards the sky. The PVC tube was placed over the camera and an image was taken. This kept the field of view captured by the camera consistent across plots. b. The percentage of leaf litter cover was assessed by eye across the entire plot (value out of 100) and measure the depth (cm) was measured using a ruler. c. The number of seedlings (i.e. young trees and shrubs less than 0.5 m tall) was counted in each plot. This will provide insight into the rehabilitation or recovery stage. d. The slope of the site was measured using a clinometer. e. The diameter at breast height (DBH) was measured for all the plants within the 5 x 5 m plot that met these criteria: • trees and tall shrubs >2 m in height with a DBH of ≥10 cm • mallee and mulga >2 m in height with a DBH of ≥5 cm. f. Mean DBH and basal area for each plot were derived from the individual DBH measurements. 2. Plant composition and diversity a. Each plant within the plot was assigned a field species name and, where possible, a scientific name. Species identification was done with the help of the iNaturalist project (https://www.inaturalist.org ). If the plant could not be identified at the species level, it was assigned a descriptive term or a number. For instance: • Flowering herb - purple • Grass - tall, feathery • Shrub - spiky leaves • Eucalypt - smooth bark • Eucalypt – rough bark • Fern - large fronds • Other tree - red berries b. The number of individuals for each species was counted. These data were used to calculate species richness and the Simpson's Diversity Index for each plot. 3. Soil assessment a. For each plot a soil sample was obtained using an auger or hand trowel. b. Soil pH was measured using a soil pH test kit at a depth of 20 cm.Progress Code: onGoingMaintenance and Update Frequency: asNeeded&rft.creator=Terrestrial Ecosystem Research Network &rft.date=2026&rft.edition=1&rft.relation=https://zenodo.org/records/15171698&rft.relation=https://zenodo.org/records/15171679&rft.relation=https://zenodo.org/records/15171782&rft.relation=https://zenodo.org/records/15171952&rft.relation=https://zenodo.org/records/15178732&rft.coverage=Long Pocket, Brisbane, QLD, Australia.&rft.coverage=northlimit=-27.508277; southlimit=-27.510702; westlimit=152.995158; eastLimit=152.997519; projection=EPSG:4326&rft_rights=Creative Commons Attribution 4.0 International&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=biota&rft_subject=CANOPY CHARACTERISTICS&rft_subject=EARTH SCIENCE&rft_subject=BIOSPHERE&rft_subject=VEGETATION&rft_subject=CANOPY STRUCTURE&rft_subject=SOIL PH&rft_subject=SPECIES DISTRIBUTION&rft_subject=ECOLOGY&rft_subject=BIOLOGICAL SCIENCES&rft_subject=Terrestrial Ecosystem Research Network&rft_subject=Flora Survey&rft_subject=Site Survey&rft_subject=field species name&rft_subject=Unitless&rft_subject=soil pH&rft_subject=seedling count&rft_subject=Number&rft_subject=canopy cover&rft_subject=Percent&rft_subject=basal area&rft_subject=Hectare&rft_subject=ground slope angle&rft_subject=Degree&rft_subject=leaf litter depth&rft_subject=Centimetre&rft_subject=disturbance type&rft_subject=leaf litter cover area&rft_subject=soil colour&rft_subject=soil texture&rft_subject=soil moisture status&rft_subject=diameter at breast height&rft_subject=species richness&rft_subject=Simpson's diversity index&rft_subject=scientific name&rft_subject=plant growth form&rft_subject=plant growth stage&rft_subject=plant mortality&rft_subject=plant count&rft_subject=1 meter - < 30 meters&rft_subject=irregular&rft.type=dataset&rft.language=English Access the data

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Creative Commons Attribution 4.0 International

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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Contact Information

Street Address:
Terrestrial Ecosystem Research Network
80 Meiers Road, Indooroopilly, Queensland, 4068, Australia
Queensland 4068
Australia
Ph: +61 7 3365 9097

[email protected]

Brief description

This dataset contains flora, vegetation structure and soil survey data collected by senior secondary school students as part of ecological monitoring activities aligned with the Australian senior secondary Biology and Geography curricula. Data are collected across Australia from disturbed and undisturbed ecosystems, or from contrasting ecosystem types, using field methods adapted from TERN's ecological monitoring protocols.


Parameters may include plant composition and abundance, species diversity, canopy cover, leaf litter cover and depth, seedling abundance, basal area, slope, soil characteristics, disturbance history.

Notes

Supplemental Information

Schools are encouraged to contribute data collected through this module to support a growing national dataset of student collected citizen science ecosystem observations. Please submit your datasets to Eleanor Velasquez ([email protected]).

Lineage

Introduction

Data were collected using a modified version of widely adopted ecological monitoring and fieldwork techniques, including those outlined in TERN's Ecological Field Monitoring Protocols (EMSA), which provide standardised methods for monitoring Australia's environment at the continental scale (Laws, 2023b) to compare either:

• A disturbed and undisturbed ecosystem, or

• Two ecosystems that can be easily differentiated based on vegetation structure

Data types include:

• Vegetation structure

• Species diversity

• Soil characteristics

 

Site Selection

At each site, two subsites were selected to compare species diversity using measures such as species richness and the Simpson's Diversity Index, e.g.:

• An undisturbed reference ecosystem vs a disturbed ecosystem of the same type, undergoing recovery.

• Two regional ecosystem of different types, e.g., dry sclerophyll forest vs e.g., rainforest or wet sclerophyll forest.

 

Data Collection

At each subsite, data were collected across multiple 5x5 m plots. Ideally a minimum of 10 plots were sampled at each subsite. The 5 x 5 m plots were delimited using transect tape. At each plot the following data were collected:

1. General observations:

a. The canopy cover was estimated using a camera, PVC tube and canopy cover chart. The iPad was placed on the ground and held horizontally with the camera pointing towards the sky. The PVC tube was placed over the camera and an image was taken. This kept the field of view captured by the camera consistent across plots.

b. The percentage of leaf litter cover was assessed by eye across the entire plot (value out of 100) and measure the depth (cm) was measured using a ruler.

c. The number of seedlings (i.e. young trees and shrubs less than 0.5 m tall) was counted in each plot. This will provide insight into the rehabilitation or recovery stage.

d. The slope of the site was measured using a clinometer.

e. The diameter at breast height (DBH) was measured for all the plants within the 5 x 5 m plot that met these criteria:

• trees and tall shrubs >2 m in height with a DBH of ≥10 cm

• mallee and mulga >2 m in height with a DBH of ≥5 cm.

f. Mean DBH and basal area for each plot were derived from the individual DBH measurements.

2. Plant composition and diversity

a. Each plant within the plot was assigned a field species name and, where possible, a scientific name. Species identification was done with the help of the iNaturalist project (https://www.inaturalist.org ). If the plant could not be identified at the species level, it was assigned a descriptive term or a number. For instance:

• Flowering herb - purple

• Grass - tall, feathery

• Shrub - spiky leaves

• Eucalypt - smooth bark

• Eucalypt – rough bark

• Fern - large fronds

• Other tree - red berries

b. The number of individuals for each species was counted.

These data were used to calculate species richness and the Simpson's Diversity Index for each plot.

3. Soil assessment

a. For each plot a soil sample was obtained using an auger or hand trowel.

b. Soil pH was measured using a soil pH test kit at a depth of 20 cm.

Progress Code: onGoing
Maintenance and Update Frequency: asNeeded

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

The purpose of the dataset is:

•To compare species diversity and ecosystem characteristics between a disturbed and undisturbed site (or two different ecosystem types) aligned where possible with TERN protocols

•To analyse the effects of disturbance or environmental difference on ecosystem diversity and how this relates to ecosystem structure and function



Data Quality Information

Data Quality Assessment Scope
local : dataset
<p>This dataset has been collected by TERN Australia staff, University of Queensland students, senior secondary school students, and their teachers as part of educational, training, and citizen science activities. Data collection methods are based on standardised ecological monitoring approaches adapted from TERN's Ecological Monitoring System Australia (EMSA) protocols.</p> <p>Data quality may vary between contributors due to differences in experience, site conditions, equipment availability, and taxonomic expertise. To support consistency, participants are provided with standardised field methods, data collection worksheets, guidance materials, and where possible, supporting photographic records through platforms such as iNaturalist.</p> <p>Species identifications may vary in taxonomic resolution, with some observations recorded to species level and others recorded as broader taxonomic or functional groups. Users should consider these limitations when interpreting the data. Despite these constraints, the dataset provides valuable information on biodiversity, vegetation structure, soil characteristics, and ecosystem condition across a range of Australian environments and contributes to environmental literacy, ecological monitoring, and citizen science engagement.</p>

Created: 2026-04-15

Issued: 2026-07-06

Modified: 2026-07-06

Data time period: 2026-04-15

This dataset is part of a larger collection

Click to explore relationships graph

152.99752,-27.50828 152.99752,-27.5107 152.99516,-27.5107 152.99516,-27.50828 152.99752,-27.50828

152.9963385,-27.5094895

text: Long Pocket, Brisbane, QLD, Australia.

ACN 633 798 857