Abstract

Open-cut coal mining began in central Queensland’s Bowen Basin approximately 50 years ago. Over this period of time, mine rehabilitators have used a variety of tree, shrub, and groundcover species to create ‘novel ecosystems’ to stabilise soils and provide vegetative cover for pre-supposed final end-land uses. We examine post-mining rehabilitation from multiple soil and vegetation monitoring activities in the Bowen Basin to assess the similarity of landforms, plant composition, and trends in plant diversity compared to unmined reference communities. Rehabilitated spoil dumps and reference sites were assessed using soil and vegetation data contained in compliance monitoring reports from Goonyella Riverside, Moura, Oaky Creek, Rolleston, and Blackwater mines. Slopes, soil chemistry, and plant species mixes of rehabilitation aged from 2 to 22 years were compared to selected reference communities. Mines in this region have generally proposed one of two post-rehabilitation end-land uses: either pasture for cattle grazing or reconstructed native communities which potentially provide native fauna habitat. Landform data from a selection of these mine sites suggest that when their rehabilitation was compared to nearby reference sites median slope values were between 2.5 and 7 times steeper and soil pH, electrical conductivity, and phosphorus levels were significantly higher. The steeply sloped landforms, poor soil characteristics, depauperate native species pool, and uniform presence of exotic pasture grasses in the rehabilitation indicate that most of these newly created ecosystems should not be used for cattle grazing and also have few natural values. Legislative and community expectations have changed progressively over time and, although much of the rehabilitation is currently dominated by an assemblage of exotic buffel grass (Cenchrus ciliaris) and Acacia spp., recent environmental authorities suggest these ‘novel ecosystems’ will be judged against native reference sites. Upon completion of mining activities the resilience of these new ecosystems to drought, fire, and grazing will need to be demonstrated prior to lease relinquishment.

Highlights

  • Open-cut coal mining began in central Queensland’s Bowen Basin approximately 50 years ago

  • If mines continue to use topsoil with seed banks dominated by aggressive and opportunistic exotic species and add fertiliser, very few native species will survive over the longer term due to an altered competitive equilibrium

  • A larger question remains: should society accept the current rehabilitated landforms and vegetation types as new novel regional ecosystems or demand that mining companies achieve higher quality ecosystems with more native species that are both resilient and functional into the distant future? Unless the ecosystems created can demonstrate some utility to future land users, public perception will remain that mining companies need to manage their leases in perpetuity

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Summary

Introduction

Open-cut coal mining began in central Queensland’s Bowen Basin approximately 50 years ago Over this period of time, mine rehabilitators have used a variety of tree, shrub, and groundcover species to create ‘novel ecosystems’ to stabilise soils and provide vegetative cover for pre-supposed final end-land uses. The 80,000 km Bowen Basin geological formation contains Australia’s largest and most lucrative coal reserves Coal in this area was formed during the Early Permian to Middle Triassic (Geoscience Australia 2013) with coal seams up to 16 m thick. Across the region a number of buffel grass (Cenchrus ciliaris) varieties were subsequently introduced to improve pasture yields and this invasive grass species is a common feature in the landscape (Marshall et al 2012) These activities represent unmistakable large-scale drivers of change toward the ecological form and function of the entire biogeographic region

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