The effects of contemporary and previous land management practices are reflected in the present-day condition of native vegetation. In order to properly manage land for productive use or to restore it to its 'natural' condition, it is important to know the changes that have taken place to the use of the land, and the cumulative effect of those changes. Assessing and reporting the resilience of native vegetation using metrics of structure, composition and function is discussed. The system, VAST-2, has been developed in the Australian context, where land management was relatively unchanged for some tens of thousands of years prior to European settlers who arrived some hundred years hence. This reference state provides a structure in which to compile, interpret and sequence data gathered in the past about changes in management practices and the effects of these practices on the condition of native plant communities. Early settlers and subsequent land managers have modified and fragmented the native vegetation thereby transforming many landscapes.
Assessing and reporting resilience of native vegetation using metrics of structure, composition and function
1. Assessing and reporting resilience of
native vegetation using metrics of
structure, composition and function
Richard Thackway
Macquarie University Biology Department Seminar
22 April 2015
2. Outline
⢠How the land use modifies native vegetation
⢠Links between management and ecosystem services
⢠VAST-2 methodology
â Detailed chronology of causes and effects
â Criteria and indicators of structure, composition and function
â Some concepts and definitions
â Analytical framework
⢠Case studies
⢠Lessons
⢠Where to from here
⢠Conclusions and more information
13. Historic goals of land managers over time
Values and decisions matrix:
⢠Social
⢠Economic
⢠Environmental
Intensification
Degradation?
Time
State @ t1
State @ t2
State @ t3
Development
14. Regulation of hydrological regime
Generation of food and fibre
Regulation of climate / microclimate
Generation of raw materials
Recycling of organic matter
Creating and regulating habitats
Controlling reproduction and dispersal
LMP are used to change ecological function to
derive multiple benefits (ecosystem services)
t1 t2 t3
Time
State@t1
State@t2
State@t3
15. Current & future goals of land managers
Values and decisions matrix:
⢠Social
⢠Economic
⢠Environmental
Extensification
Restoration
State @ t1
Regeneration
State @ t2
State @ t3
17. Concepts and definitions
⢠Resilience = the capacity of an plant community to recover
toward a reference state following a change/s in land
management
⢠Change in condition of a plant community (type) is due to
effects of land management practices:
â Structure
â Composition
â Regenerative capacity
⢠Transformation = changes in vegetation condition over time
⢠Condition, resilience and transformation are assessed relative
to a fully natural Reference state
Vegetation condition
18. Based on Cannon (1987)
Baseline for assessing resilience:
Indigenous peoples first contact with explorers
Based on Cannon (1987), Readers Digest.
Plotted using IBRA regions
19. How do land managers modify structure, composition &
function (i.e. resilience) over time?
LMP that focus on soil
LMP that focus on
native vegetation
Regenerative capacity/ function
Vegetation structure &
Species composition
1. Soil hydrological status
2. Soil physical status
3. Soil chemical status
4. Soil biological status
5. Fire regime
6. Reproductive potential
7. Overstorey structure
8. Understorey structure
9. Overstorey composition
10. Understorey composition
LMP = Land Management Practices
Focussing on 10 key criteria
20. Common interventions designed to influence
structure, composition & function i.e. resilience
Various interventions:
Land management practices (LMP) are used to influence
ecological building blocks at sites and landscapes by:
⢠Modifying âŚ
⢠Removing and replacing âŚ
⢠Enhancing âŚ
⢠Restoring âŚ
⢠Maintaining âŚ
⢠Improving âŚ
Various purposes:
To achieve the desired mix of ecosystem services (space & time)
21. VAST-2 is an accounting system for assessing the
transformation of native vegetation
LU = Land Use, LMP = Land Management Practices
VAST Diagnostic attributes
Time
22. Aim of VAST-2 at sites and landscapes
Indigenous
land
management
First
explorers
Grazing
Degreeof
resilience/condition
Logging
Cropping
Site 1
Site 2
Site 3
Time
Reference state
Long
term
rainfall
Long term
disturbance
e.g. wildfire,
cyclones
Revegetation
VAST
classes
Weeds
Ferals
23. How does VAST-2 use metrics
to assess and report
resilience/condition of native
vegetation?
24. Generate total indices for âtransformation siteâ for each year of the
historical record. Validate using Expert Knowledge
⢠Compile and collate effects of land
management on criteria (10) and
indicators (22) over time.
⢠Evaluate impacts on the plant
community over time
Transformation site
⢠Compile and collate effects of
land management on criteria
(10) and indicators (22)
Reference state/sites
Score all 22 indicators for âtransformation siteâ relative to the
âreference siteâ. 0 = major change; 1 = no change
Derive weighted indices for the âtransformation siteâ i.e. regenerative
capacity (55%), vegetation structure (27%) and species composition (18%)
by adding predefined indicators
General process for tracking change over time
using the VAST-2 system
25. Approximate
year
Source:
Year
LU & LMP Source:
LU & LMP
Effects of land use and
management on criteria and
indicators of vegetation
condition
Source:
Effects
1800
1840
2015
Establish a chronology of data and information of
causes and effects /observed & measured responses
Pre-contact
First contact
Current year
LU = Land Use, LMP = Land Management Practices NB: Accuracy of each observation and
measurement is important
26. Components
(3)
Criteria
(10)
Description of loss or gain relative to pre settlement indicator reference state
(22)Regenerativecapacity
Fire regime Change in the area /size of fire foot prints
Change in the number of fire starts
Soil hydrology Change in the soil surface water availability
Change in the ground water availability
Soil physical
state
Change in the depth of the A horizon
Change in soil structure.
Soil nutrient
state
Nutrient stress â rundown (deficiency) relative to soil fertility
Nutrient stress â excess (toxicity) relative to soil fertility
Soil biological
state
Change in the recyclers responsible for maintaining soil porosity and nutrient recycling
Change in surface organic matter, soil crusts
Reproductive
potential
Change in the reproductive potential of overstorey structuring species
Change in the reproductive potential of understorey structuring species
Vegetationstructure
Overstorey
structure
Change in the overstorey top height (mean) of the plant community
Change in the overstorey foliage projective cover (mean) of the plant community
Change in the overstorey structural diversity (i.e. a diversity of age classes) of the stand
Understorey
structure
Change in the understorey top height (mean) of the plant community
Change in the understorey ground cover (mean) of the plant community
Change in the understorey structural diversity (i.e. a diversity of age classes) of the plant
Species
Composition
Overstorey
composition
Change in the densities of overstorey species functional groups
Change in no.s of indigenous overstorey species relative to the number of exotic species
Understorey
composition
Change in the densities of understorey species functional groups
Change in no.s of indigenous understorey species relative to the number of exotic species
28. Importance of dynamics
Assume rainfall is main driver of natural system dynamics
⢠Period 1900 - 2014
⢠Average seasonal rainfall (summer, autumn, âŚ)
⢠Rainfall anomaly is calculated above and below the mean
⢠Two year running trend line fitted
30. ⢠Network of collaborators
⢠Ecologists, land managers, academics, research scientists,
environmental historians
⢠Inputs
⢠Reference state
⢠Historical record of land use & Land management practices
⢠Historical record of major natural events e.g. droughts, fires, floods,
cyclones, modelled average rainfall 1900-2014
⢠Observed interactions e.g. rabbits, sheep and drought
⢠Observations and quantitative measures of effects of LMP
⢠Include written, oral, artistic, photographic, long-term ecological
monitoring sites and remote sensing
Resources needed for each site
31. Certainty level standards used to compile
historic record
Certainty
level
standards
Spatial precision
(Scale)
Temporal precision
(Year of observation)
Attribute accuracy
(Land use, land
management practices,
effects on condition)
HIGH
"Definiteâ
Reliable direct
quantitative data.
Code: 1
Reliable direct
quantitative data.
Code: 4
Reliable direct
quantitative data.
Code: 7
MEDIUM
"Probable
"
Direct (with
qualifications) or strong
indirect data.
Code: 2
Direct (with
qualifications) or strong
indirect data.
Code: 5
Direct (with
qualifications) or strong
indirect data.
Code: 8
LOW
"Possible"
Limited qualitative and
possibly contradictory
observations. More
data needed.
Code: 3
Limited qualitative and
possibly contradictory
observations. More
data needed.
Code: 6
Limited qualitative and
possibly contradictory
observations. More
data needed.
Code: 9
32. Reliability levels of attribute sources
Quadrat or pixel
Land unit
Land system
Sub-bioregion
Bioregion
Certainty
levels
Coarse
Fine
Low
Low
Medium
Medium
High
Sources of
information
Granularity of
information
33. Assumptions
Changes in LU & LMP
â result in measurable and predictable changes in structure, floristics
& regen capacity
â can be consistently and reliably differentiated from natural events
â have or can be adequately and reliably documented over time
Sequential responses in veg structure, floristics & regen capacity can be
discovered, unpacked and scored over time
Ratings and weightings are ecologically meaningful
41. Predictions of mature forest
(Bunningâs Enquiry 1974)
Bridge Hill Ridge- post mining restoration
X = 2034
Y = 2054
Z = 2074
X Y Z
42. Predictions of mature forest
(Bunningâs Enquiry 1974)
Bridge Hill Ridge- post mining restoration
X = 2034
Y = 2054
Z = 2074
X Y Z
43. Components
(3)
Criteria
(10)
Description of loss or gain relative to pre settlement indicator reference state
(22)Regenerativecapacity
Fire regime Change in the area /size of fire foot prints
Change in the number of fire starts
Soil hydrology Change in the soil surface water availability
Change in the ground water availability
Soil physical
state
Change in the depth of the A horizon
Change in soil structure.
Soil nutrient
state
Nutrient stress â rundown (deficiency) relative to soil fertility
Nutrient stress â excess (toxicity) relative to soil fertility
Soil biological
state
Change in the recyclers responsible for maintaining soil porosity and nutrient recycling
Change in surface organic matter, soil crusts
Reproductive
potential
Change in the reproductive potential of overstorey structuring species
Change in the reproductive potential of understorey structuring species
Vegetationstructure
Overstorey
structure
Change in the overstorey top height (mean) of the plant community
Change in the overstorey foliage projective cover (mean) of the plant community
Change in the overstorey structural diversity (i.e. a diversity of age classes) of the stand
Understorey
structure
Change in the understorey top height (mean) of the plant community
Change in the understorey ground cover (mean) of the plant community
Change in the understorey structural diversity (i.e. a diversity of age classes) of the plant
Species
Composition
Overstorey
composition
Change in the densities of overstorey species functional groups
Change in no.s of indigenous overstorey species relative to the number of exotic species
Understorey
composition
Change in the densities of understorey species functional groups
Change in no.s of indigenous understorey species relative to the number of exotic species
44. Lessons site vs. landscape
1. Constrain assessments to soil landscape units because this
approximates land managerâs interventions
2. Must account for natural dynamics e.g. flood, fire, cyclone
3. Remote sensing is only part of the solution â
a) Some measures of remote sensing e.g. greenness of tree crowns may not
be directly related to vegetation condition
4. Tracking outcomes of management interventions using remote sensing
a) e.g. environmental plantings and environmental watering requires on-
ground collection of data to calibrate and validate spatial and multi-
temporal imagery
b) Only populate criteria and indicators once imagery has been validated
45. Conclusions
⢠VAST and VAST-2:
ď Provides an accounting tool for reporting change and trend in the
condition of plant communities
ď Helps with telling the resilience story in landscape transformation
ď Provides a system for synthesizing diverse source and types of
information (quantitative and qualitative)
ď Values equally land managers and ecologists because they both
contribute essential data and information
ď Enables decision-makers to better understand complex ecosystem
transformations such as degradation, restoration and regeneration.
46. âTelling the transformation storyâ
Residual/ unmodified
Modified
Transformed
Adventive
Replaced and
managed
Organ Pipes National Park, Vic â
ex cropping paddock
Pathways of
landscape
transformation
reflect choices
and drivers
VAST
classes
49. More info & Acknowledgements
More information
http://www.vasttransformations.com/
http://portal.tern.org.au/search
http://aceas-data.science.uq.edu.au/portal/
Acknowledgements
⢠University of Queensland, Department of Geography Planning and
Environmental Management for ongoing research support
⢠Many public and private land managers, land management agencies,
consultants and researchers have assisted in the development of VAST & VAST-2