11 research outputs found
Local peoples’ scores of clean water availability during the last 10–20 years (from high to low satisfaction ± SD).
<p>Changes in satisfaction with clean water availability during the periods when the selected major land-use changes occurred as part of the adaptation strategies to hazards (L1–4).</p
Mean number of tree species per land use (± SD) that were changed by local people as part of their adaptation strategies to hazards (L1–4).
<p>Mean number of tree species per land use (± SD) that were changed by local people as part of their adaptation strategies to hazards (L1–4).</p
Mean values of harvested products from the land (USD/ha/y ± 10% uncertainties).
<p>Land uses that were changed by local people as part of their adaptation strategies to hazards (L1–4).</p
Map of the study sites.
<p>Land cover in the studied landscapes (L) in the Indonesian provinces of West Kalimantan (L1, L2) and Central Java (L3, L4) in 2014.</p
Description of the major land-use changes (L1–4) that the local people undertook to adapt and maintain well-being under the impacts of drivers of change (source: Focus group discussions).
<p>Description of the major land-use changes (L1–4) that the local people undertook to adapt and maintain well-being under the impacts of drivers of change (source: Focus group discussions).</p
Overview of the indicators and methods used to assess land-use changes and their impact on ecosystem services.
<p>Overview of the indicators and methods used to assess land-use changes and their impact on ecosystem services.</p
The modified ecosystem services cascade framework.
<p>Drivers of change affect the state of social and ecological systems. Changes in landscape properties or societal values influence land-use decisions and the supply of ecosystem services. A change at one point in the system triggers further changes because of the reinforcing loop of ecosystem services flows, whereby benefits derived from particular land uses lead to more changes by local people to those land-uses to ensure supply of more services.</p
Changes in ecosystem services (land products, carbon sequestration, water purification and regulation) and biodiversity before and after selected land-use changes as per people’s adaptation strategies.
<p>The value of each indicator is normalized from 0 (minimum possible value at the center of the spider plot) to 5 (maximum observed value on the outermost circle).</p
Ecosystem services 2015-12-01
Semi-quantitative changes in bundles of ecosystem services and adaptation services under scenarios of ‘Without development’ ‘Current’, and ‘Climate change’. Potential ecosystem services that may be of value for adaptation were determined based on increase between ‘Current’ and ‘Climate Change
Changes in frequency and volume of floods 2015-12-01
. Estimated percentage and ranked changes in the period between floods and flood volumes from current development, 1895-2006 climate to current development, 2030 climate for major floodplains and wetlands in the Murray-Darling Basin. Overall rank change in flood regimes of for wetlands is mapped in Figure 3d. No data was available for the Eastern Mt. Lofty Ranges Catchment. Data on changes in flood return period and volume is from Table 7.2 of each of the CSIRO MDBSY regional reports, http://www.csiro.au/en/Research/LWF/Areas/Water-resources/Assessing-water-resources/Sustainable-yields/MurrayDarlingBasin/Report