Upload
richard-thackway
View
67
Download
0
Embed Size (px)
Citation preview
Managing vegetation for multiple benefit outcomes –
Diagnosis and Prognosis
Richard Thackway
Presentation to Murray Darling Basin Authority22 September 2016
MDBA has identified two development areas for native vegetation:
1. Analysis framework for evaluation of extent and condition of woody vegetation communities
2. Developing scenarios for future landscape transformation
Definitions
• Change in a plant community (type) due to effects of land management practices:
– Structure
– Composition
– Regenerative capacity• Resilience = the capacity of an plant community to recover to
a reference state following a change/s in land management
• Transformation = changes to vegetation condition over time• Condition, resilience and transformation are assessed relative
to fully natural a reference state
Vegetation condition
VAST = Vegetation Assets States and TransitionsNVIS = National Vegetation Information System
VIVIVIIIIII0
Native vegetationcover
Non-native vegetationcover
Increasing modification caused by use and management
Transitions = trend
Vegetation thresholds
Reference for each veg type (NVIS)
A framework for assessing modification of native vegetation extent and condition
Condition states
Residual or unmodified
Naturally bare
Modified Transformed Replaced -Adventive
Replaced - managed
Replaced - removed
Thackway & Lesslie (2008)
Diagnostic attributes of VAST (classes):• Vegetation structure• Species composition• Regenerative capacity
VAST-2 criteria and indicators Change & Trend
NVIS
1925
Occupation
Relaxation
Anthropogenic change
Net benefit
time
1900 2025 1950
Reference
chan
ge in
veg
etati
on in
dica
tor o
r ind
ex
1850 1875 1975 2000
Model of ecosystem change (causes & effects)
Baseline
Accounting for changes in native veg type, extent and condition
Land managers use LMP to influence ecological function at sites and across landscapes by changing:• Vegetation structure• Species composition and • Regenerative capacity
LMP deliberately &/or unintentionally do this by:• Modifying • Removing and replacing• Enhancing• Restoring• Maintaining• Improving
*
* Natural disturbances
Function
Structure & Composition
LMP = land management practices
Goal is to develop whole of landscape monitoring of criteria and indicators relative to reference states
0
20
40
60
80
100
1985 1990 1995 2000 2005 2010
Year
FPC
Source: Tim Danaher and Phil Tickle
Site and landscape scales
1925
Occupation
Relaxation
Anthropogenic change
Net benefit
time
1900 2025 1950
Reference
chan
ge in
veg
etati
on in
dica
tor o
r ind
ex
1850 1875 1975 2000
VAST classes
Evaluation of ecosystem change thatrely on remote sensing metrics however …
Hyperspatial, hypertemoral &
hyperspectral remote sensing
Aerial photos and digital
imagery
Aerial photos
Quantitative
Baseline
Time before remote sensing
Caution - remote sensing change is relative to a baseline - it is only half the answer – NEED REFERENCE STATE
Zero/constant baseline (e.g. environmental planting = reveg)
Resp
onse
va
riabl
e/s
Time
Start ofactivity/
intervention
Time
Varying baseline (e.g. environmental watering)
Resp
onse
va
riabl
e/s
Single intervention & climatic variability
BaselineResponse to activity/ intervention
Indicator 13: Overstorey height
Indicator 4: ground water
Photo by Peter Coyne
1740
1906
Phillip Island, South Pacific – extent and condition
Photo State Library NSW: JW Beattie
1860 already denuded
year
scor
e %
Pine – Hardwood Subtropical Rainforest, Phillip Island, Sth Pac
Pigs released
Uninhabited island
Pigs died out
Goats, rabbit and fowl released
Goats died out
Rabbits eradicated
Rabbit control
commenced
Commenced passive & active
restoration. Minimal ecological
monitoring
Phase 1 Phase 2 Phase 3 Phase 4
Evaluation framework
• Has been extensively used to evaluate condition outcomes – Diagnosing and reporting condition (i.e. status and trend) of veget
ation types – Evaluating examples of restoration and regeneration
Tran
sfor
mat
ion
scor
e
Years
1800
2016
Reference
Developing scenarios for future landscape transformation
Modified
Transformed
Replaced/ managed
Residual
Replaced/adventive
VAST Classes
1850 19501900 2000 2050 2100Replaced/ removed
Baseline
Classes can be modelled as extent and condition
Extent native
NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Reference pre-European: Sydney Blue Gum High Forest
Commenced managing area for recreation. Weed control. Arboretum abandoned
Cleared & sown to improved pasture for grazing & orchard
Commenced grazing native pastures
Indigenous people manage the area
Grazed area gazetted as State Forest, commenced planting arboretum
Area logged for building houses and fences
Commenced managing area as a future production forest. Weed control
Explorers traverse the area and site selected
Ceased grazing. Area purchased as a future working forest
Modified
Transformed
Replaced/ managed or removed
Residual
Replaced /adventive
VAST
Before developing any scenarios it is critical to assess where, when and how landscapes were/are transformed relative to a reference
Spp compVeg structure
LU = Land Use, LMP = Land Management Practices
VAST Diagnostic attributes
LU & LMPYear
Time
Regen cap
/Function
Bioregion: Mulga Lands
Reference state: Extent of pre-clearing Regional Ecosystem (RE) 6.3.13Atriplex spp., Sclerolaena spp., species of Asteraceae and/or short grasses open-herbland on alluvial plains
Source: Daniel Ferguson, Queensland Herbarium
Need to assess which of the 10 key criteria are affected and by how much i.e. Condition
Soil
Vegetation
Regenerative capacity/ function
Vegetation structure & Species composition
1. Soil hydrological status2. Soil physical status3. Soil chemical status4. Soil biological status5. Fire regime6. Reproductive potential7. Overstorey structure8. Understorey structure9. Overstorey composition10. Understorey composition
NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Function – Regenerative capacity
Criteria #1 Criteria #2
Criteria #3 Criteria #4
Disturbance regime
NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Function – Regenerative capacity
Criteria #5 Criteria #6
NSW, SB Bioregion, Cumberland SF, ex-comp 3a, 7a, 7b, 7c Vegetation structure
Indicators:#13: Height#14: Foliage cover#15: Age structure
Indicators:#16: Height#17: Foliage cover#18: Age structure
Criteria #7
Criteria #8
NSW, SB Bioregion, Cumberland SF, Transect 2 (ex-comp 3a, 7a, 7b, 7c)Species composition
Criteria #9
Criteria #10
Conclusions
• Vegetation types are kept in various extents and condition states depending on social and economic ideals, values, goals and drivers
• Conversions to non-vegetated, non-native and highly modified native commenced at European settlement; the reference state
• Conventional mapping and monitoring of vegetation type, extent and condition using remote sensing is only started around 70 years ago
• Transformations are changes in condition and extent relative to a reference state: function, structure & composition
• Net gains in condition and extent(spatially and temporally) can be accounted for as changes in function, structure and composition
• To achieve long term lasting changes in extent and condition we must engage land managers using language of public and private benefits
• Scenarios that aim to transform extent and condition must be informed locally by evidence of previous land management practices
Thank you
Supplementary Information
Dynamics
Rainfall is assumed the main driver of natural system dynamicsIt is a key dataset used in developing chronologies of effects of land management on vegetation condition:• Period 1900 – current1
• Average seasonal rainfall (summer, autumn, …) is highly correlated to LMP2 and their effects on function, structure and composition
• Rainfall anomaly is calculated above and below the mean• Two year running trend line is fitted to give insights into El Niño and La
Niña events3
1. Bureau of Meteorology: modelled monthly rainfall 5km resolution national dataset 2. LMP – Land management practices3. El Niño events are associated with prolonged periods of below average rainfall and at times, devastating droughts. A rapid onset of a La Niña event, following a severe El Niño event, have been associated with major soil erosion events and major cycles of regeneration and germination
Differentiating natural disturbance events and land management practices
Photos by Garry Dowling and Richard Thackway
2006 20132009
Low intensity grazing - cell grazing sheep
Severe dust storm Low intensity grazing - cell grazing sheep
Reference state: Pre-clearing Regional ecosystem 6.3.13 Atriplex spp., Sclerolaena spp., species of Asteraceae and/or short grasses open-herbland on alluvial plains
Illustrates a baseline but not the Reference state
Photo: Melinda Laidlaw
High intensity cattle grazing -Continuous or set stocking
Source: https://publications.qld.gov.au/storage/f/2014-09-18T23%3A49%3A36.560Z/re-seq-landzones.pdf
A Framework for Program Evaluation
Source: http://sphweb.bumc.bu.edu/otlt/mph-modules/ProgramEvaluation/ProgramEvaluation2.html
Need continuous social learning linked to adaptive management
Yapp, Walker and Thackway (2010)
VAST 1 Residual/unmodified*
VAST II1 Transformed
* Reference state
Multiple benefits (ecosystem services) and condition states