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generalised example from North Central CMA

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Victorian Dept. of Primary Industries, University of Melbourne ... Site 3 1.5 ha Valley Grassy Forest. Site 2 1.8 ha Valley Grassy Forest. Landholder's name & code ... – PowerPoint PPT presentation

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Title: generalised example from North Central CMA


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Guiding Principles
SUSTAINABILITY the rate and consequences of
natural resource use are understood and
addressed guilt free
EFFICIENCY better outcomes for a given level of
effort or investment waste free
EQUITY fairness from both investor and landholder
perspectives envy free
3
Key Drivers for Trial
  • to contribute to broader based efforts to better
    quantify biodiversity priorities and outcomes
  • to improve targeted participation in conservation
    management on private land in a demonstrably
    cost-effective manner

4
Why try a new approach to public investment in
private land native vegetation ?
  • Victoria has mature support programs
  • (e.g. Land for Wildlife, Trust for Nature),
    however
  • many existing participants have practical
    limits
  • we are not engaging some important landholders
  • we need to more convincingly demonstrate
  • the return on investment

gt we need better resolution of cost-sharing
given a diverse range of views on public
/ private benefit gt we need better ways to
align individual actions with complex
regional NRM priorities
5
Why an auction approach?
  • Asymmetric (hidden) information between buyers
    and sellers is a key impediment to creating
    effective markets
  • landholder best knows opportunity and service
    costs
  • community governance groups (agency / regional
    authority) best placed to express public
    preferences and identify appropriate actions
  • Auctions are a mechanism we can employ to
    reveal hidden information and make
    mutually-acceptable, cost-effective deals with
    landholders to better manage natural resources.
  • Auctions require effective sharing of
    information

6
Traditional information relationships
vegetation / habitat condition ?
7
Required characteristics of an assessment
approach to Native Vegetation Quality
  • provide a sufficiently reliable and repeatable
    measure that can be a surrogate for naturalness
  • indicate direction, nature and amount of
    potential change
  • allow comparison between different vegn types
  • combine quality and quantity to calculate net
    outcomes
  • can be undertaken relatively easily and quickly
  • can enable exchange of information in an easily
    understood way

8
Vegetation / Habitat Condition
  • one Habitat Hectare
  • one hectare of native vegetation which
    retains the average characteristics of a mature
    and apparently long-undisturbed stand of the same
    vegetation type
  • Requires a reference point or benchmark for
    mature, natural condition for each
    vegetation type
  • Offers a common currency for quality /
    quantity with each assessment providing a
    baseline and guidance on what is lacking / what
    could be improved

9
Habitat Score Components/Weightings

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A pragmatic balance
  • Ignored
  • Intuitive (personal knowledge)
  • Generic Habitat Index (hab
    ha)
  • Individual habitat
    attributes
  • Use of
    habitat by species

on-ground decisions
scientific research
11
BushTender information relationships
THREATS
CONDITION current habitat service
BIODIVERSITY SIGNIFICANCE endangered, vulnerable,
depleted, rare
BIODIVERSITY SIGNIFICANCE conservation
status landscape priority
MGT. OUTCOME action to secure and/or improve
habitat service
MANAGEMENT
BIODIVERSITY BENEFIT (significance X mgt.
outcome) / cost
COST
12
Scoring estimated level of habitat service
secured and/or improved
13
Biodiversity Significance Score
14
BushTender Trial parameters
  • Trial focused on biodiversity values (multiple
    benefits options being considered in current MBI
    pilot)
  • Landholders tender bids for
  • management services that maintain or improve
    native vegetation beyond the level required by
    duty of care and currently permitted uses
  • Scope of trial
  • 2001/02 Northern Victoria (2 areas)
  • 400 000 for landholder payments - 3 yr
    agreements
  • 2002/03 Gippsland (3 areas)
  • 800 000 - 3 or 6 yr agr. /- on-going protection

15
  • Landholders experience
  • Site Visit
  • advised on significance of vegetation types /
    species / locations
  • can witness an assessment of quality
  • discuss quality issues / mgt. options relative
    importance (score) of outcomes
  • agree on proposed mgt. commitments
  • Following visit, receive by mail
  • map of sites
  • summary of significant values
  • draft mgt. plan agreement
  • Return a sealed bid (total ) by mail
  • If successful, receive by mail
  • agreement to sign and return
  • reporting / payments monitoring
  • If unsuccessful, receive by mail
  • advice on how close other options

16
Biodiversity Benefits Index
current Biodiversity Significance Score
Habitat Services Score /
  • Index used for objective discrimination between
    bidders based on conservation preference,
    price and habitat services being offered - a
    value for money measure

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BushTender Results2001/02 Northern Victoria
  • Site
  • assessments Auction Successful
  • 115 properties 98 bidders 73 bidders
    74
  • 148 bids 97
    bids 66
  • 223 sites 186 sites 131 sites
    70
  • area 3840 ha 3160 ha
    82
  • Broadly similar result for 2002/03 Gippsland.

20
Bid Diagram for Northern Victoria Gippsland
trial areas
21
Agreement Types - Gippsland trial
  • Successful contract type
  • Three years 2.5
  • Three years plus 10 years protection 0
  • Three years plus permanent protection 0
  • Six years 49
  • Six years plus ten years protection 28
  • Six years plus permanent protection
    20.5

22
Some observations on the Trial
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An engaging process
  • easier to get participation than some expected
  • participants were reasonably representative
  • similar on-farm income
  • more likely to be a member of a landcare group
  • ( but 18 were not currently members of
    any group )
  • more likely to have participated in other
    environment programs ( but 35 had no involvement
    in previous 3 yrs )
  • similar for successful
    unsuccessful bidders
  • landholders appreciated the process / opportunity
  • of participants, over 80 rated the site
    assessment process as good or very good
  • of non-participants, 78 rated the approach as a
    good idea

24
An efficient cost-effective process
In comparison to a fixed price approach, 25
more biodiversity improvement for the given
budget - also some landholders with
services of interest unlikely to have accepted
lower price
Very reasonable transaction costs, primarily due
to efficient assessment high conversion
rate e.g. 1 site ass./day, 74 lead to offers,
95 accepted Direct comparisons to other
approaches are difficult (outcomes of other
approaches not as well quantified) but appear
favourable
25
Finding the balance? biodiversity
scientific detail AND practical simple
delivery to landholder
limited scientific understanding AND
inclusion of important concepts
investing in avoidance of damage to existing
assets AND active improvement of the
condition of existing assets
AND creation of new assets (i.e.
revegetation)
26
Finding the balance? economics
desire for a strong focus on landholder
accountability for outcomes AND the
variable degree of control that is possible over
natural resource outcomes (opted to score service
according to estimated outcomes but base
management agreements on inputs)
allowing flexibility in pricing (for
landholders) AND control of overall
expenditure (by investor)
27
Finding the balance? engagement
supporting building on existing engagement
AND engaging new landholders
investment based on the best biodiversity
outcomes AND investment based on
attitudinal change
matching landholder commitments AND
apparent capabilities
28
Opportunities for learning
  • During assessment
  • landholders learn about the nature and condition
    of their assets and the relative priorities of
    actions
  • Government gains some new information about
    distribution and condition of assets
  • End of auction round
  • landholders learn about place in market
  • Government learns about market behaviour
    including amount of participation, relative costs

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Opportunities for learning cont.
  • Between rounds
  • non-participants could learn about the nature and
    benefits of the mechanism
  • unsuccessful bidders could reconsider their bids
  • Government could refine methods of preferencing
    (e.g. science - more sophisticated models
    measures economics - accommodation of any
    inherently different costing scenarios for
    particular assets)
  • During management agreements
  • landholders learn about results of actions
  • Government learns about compliance and about how
    appropriate were the estimates of outcomes

30
Guiding Principles
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