Brief description
Experimental sites were established in the northern wheat-growing district of western Australia (Lat -29.66°, Long 116.18°) in August 2017, and monitored through to November 2019. We selected five planted old field sites with similar soil types and vegetation composition. Old fields were planted with York gum (Eucalyptus loxophleba Benth.) and dominant shrubs as understorey. At the time of sampling in 2017, vegetation age ranged from 8–13 years and distance from remnant measured 279 m (± 162 m).We established two control and two treatment plots, each measuring 5 m x 5 m, in the interrows of five planted old field sites. Both treatments were randomly assigned to plots within each site. Between August and early November 2017, we measured a total of 30 response variables at each of the control and treatment plots. Response variables included soil physical and chemical properties (bulk density, penetration resistance, soil moisture, nitrogen and carbon pools), microbial biomass, decomposition rate of roiboos and green tea as per the standardized Tea Bag Index (TBI) protocol, herbaceous vegetation cover and richness, and ant abundance and richness, as well as abundance and richness of ant functional groups.
Lineage
Experimental sites were established in the northern wheat-growing district of western Australia (Lat -29.66°, Long 116.18°) in August 2017, and monitored through to November 2019. We established two control and two treatment plots, each measuring 5 m x 5 m, in the interrows of five planted old field sites. Both treatments were randomly assigned to plots within each site. Between August and early November 2017, we measured a total of 30 response variables at each of the control and treatment plots. Response variables included soil physical and chemical properties (bulk density, penetration resistance, soil moisture, nitrogen and carbon pools), microbial biomass, decomposition rate of roiboos and green tea as per the standardized Tea Bag Index (TBI) protocol developed for comparison of litter decomposition rates across various ecosystems by Keuskamp, Dingemans, Lehtinen, Sarneel and Hefting (2013), herbaceous vegetation cover and richness, and ant abundance and richness, as well as abundance and richness of ant functional groups. Detailed sampling method descriptions are provided in the Supporting Information section. In November 2017, one treatment plot at each site was uniformly covered with 13 kg of freshly mulched York gum branches including leaves, and a second treatment plot with three York gum logs. The mulch and log application rate mimics leaf litter and fine and coarse woody debris cover of the intact York gum woodland remnants. York gum mulch was sourced from roadside tree lopping of a local shire and the logs were cut to size from recently fallen York gum branches. After two years, between August and November 2019, we re-measured all 30 response variables across the control and treatment plots
Progress Code: completed
Maintenance and Update Frequency: notPlanned
Notes
CreditWe 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
Ecological restoration of former agricultural land can improve soil condition, recover native vegetation, and provide fauna habitat. However, restoration benefits are often associated with time lags, as many attributes, such as leaf litter and coarse woody debris, need time to accumulate. Here we experimentally tested whether adding mulch and logs to restoration sites in semi-arid western Australia can accelerate restoration benefits. All sites had been cropped and then planted with native trees and shrubs (i.e., Eucalyptus, Melaleuca, Acacia spp.) 10 years prior to our experiment, to re-establish the original temperate eucalypt woodland vegetation community. We used a Multi-site Before-After / Control-Impact (MBACI) design to test the effects on 30 abiotic and biotic response variables over a period of two years.
Ecological restoration of former agricultural land can improve soil condition, recover native vegetation, and provide fauna habitat. However, restoration benefits are often associated with time lags, as many attributes, such as leaf litter and coarse woody debris, need time to accumulate. Here we experimentally tested whether adding mulch and logs to restoration sites in semi-arid western Australia can accelerate restoration benefits. All sites had been cropped and then planted with native trees and shrubs (i.e., Eucalyptus, Melaleuca, Acacia spp.) 10 years prior to our experiment, to re-establish the original temperate eucalypt woodland vegetation community. We used a Multi-site Before-After / Control-Impact (MBACI) design to test the effects on 30 abiotic and biotic response variables over a period of two years.
Data Quality Information
Data Quality Assessment Scope
local :
dataset
Abiotic data was processed and analysed by professional soil laboratories (CSBP and CSIRO). All biotic data (flora and fauna) was processed and determined by taxonomic experts. All data were curated for error prior to statistical analysis and data publication.
Created: 2019-12-01
Issued: 2022-06-10
Modified: 2014-07-14
Data time period: 2017-06-01 to 2019-11-30
Subjects
1 meter - < 30 meters |
Biological Sciences |
Ecology |
Environmental Sciences |
Environmental rehabilitation and restoration |
Eucalyptus loxophleba subsp. supralaevis L.A.S.Johnson & K.D.Hill |
FORMICIDAE |
Gram Per Cubic Centimetre |
Invertebrate Biology |
Milligram Per Kilogram |
Number |
Plant Biology |
Percent |
RECLAMATION/REVEGETATION/RESTORATION |
Soil Sciences |
Unitless |
Year |
Zoology |
ammonium in soil (Milligram Per Kilogram) |
biota |
environment |
ground cover - bare (Percent) |
ground cover - cwd (Percent) |
ground cover - litter (Percent) |
mass fraction of organic matter in soil (Percent) |
number of individual animals (Number) |
one off |
plant cover (Percent) |
relative species abundance (Number) |
soil bulk density (Gram Per Cubic Centimetre) |
soil dissolved organic carbon (Milligram Per Kilogram) |
soil free amino acids (Milligram Per Kilogram) |
soil gravimetric water content (Percent) |
soil microbial biomass carbon (Milligram Per Kilogram) |
soil nitrate (Milligram Per Kilogram) |
soil organic carbon (Percent) |
soil organic matter (Percent) |
soil volumetric water content (Percent) |
species richness (Number) |
tea bag index k facfor (Year) |
tea bag index s factor (Unitless) |
weed cover (Percent) |
User Contributed Tags
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Point-of-truth metadata URL Identifiers
- URI : geonetwork.tern.org.au/geonetwork/srv/eng/catalog.search#/metadata/a7a7573c-abd5-418f-b9bc-6449b8058b5c
- global : a7a7573c-abd5-418f-b9bc-6449b8058b5c
