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Biodiversity Offsets in Canada Conference
Biodiversity offsetting in Victoria

Michael Crowe

February 2014
Native Vegetation Controls

Year: 1788 to 2012
Evolution of Offsetting in Victoria
1989 – Initial regulation of native vegetation clearing
• an end to large scale clearing

However offsetting was sporadic and not codified
1998 - Biodiversity mapping
• Extant vegetation, 1750 vegetation, bioregions, threatened species

Provided state-wide information base
2002 - Policy - the Native Vegetation Management Framework
• No net loss, like-for-like, metrics …..

However developers found it hard to find their offsets
2007 – Offset market based on credit trading
• Third party suppliers, brokers, credit register

2013 – Some policy amendments and technical improvements
The Regulation
Regulation of native vegetation clearing:
• A planning permit required to clear native vegetation
• Assessment of permit applications based on the biodiversity
significance of the impact
• Applications must demonstrate ‘avoid’ and ‘minimise’ steps
of the mitigation hierarchy
• The permit (if granted) requires an offset
Offset policy in Victoria - 2002
The nature and size of the offset was set by Native Vegetation
Management Framework policy (statutory document):
– Avoid, minimise, offset
– No Net Loss
– Quality/area metric - habitat hectares
– Offsets to be secure and ongoing
– Additionality
– Like for like rules
– Biodiversity importance
No net loss – quality is important
Measuring site quality – 10 attributes in habitat hectares

reduced cover
of trees

reduced
recruitment

reduced
understorey
diversity

increased cover
of weeds

Habitat score = 0.50
Increased quality at the offset site

tree
canopy
cover

size & connectivity
of the patch

large
old
trees

understorey
diversity
recruitment of
young trees
logs & organic litter

Habitat score = 0.90
Estimating Gain
Total gain = area x quality increment/ha

• Improvement gain
Increments in quality attribute scores resulting from
restoration actions (eg revegetation)

• Management gain
Increments in quality attribute scores resulting from actions to
control threatening processes (eg pest & weed control)

• Security gain
Increments in overall quality score depending on the changes
in land use (eg establish protected areas)
• Gain scoring includes rules for additionality
Secure and ongoing
• The landowner agreement – private land
− permanent statutory contract
− binds future landowners – on title
− actions and commitments in the management plan
− reporting and monitoring
• Land surrender
− private land donated to a permanent protected area

• Upgrade to Protected Area
− government re-classifies public land to higher security
category through legislation
The offsetting process - summary
Developers

Developers required to
provide offsets
• first party
• third party (market)

Loss site assessment,
Permit application
Local Government
Determine small
impacts

Refer large impacts
to
State Government

Permit may be granted
Permit includes offset conditions – offset plan
BushBroker price history Offset market
Bioregion

Number of
Agreements

credit prices

Total number of
Habitat
Hectares

Average price per
Habitat
Hectare *
(of total
Agreements)

Habitat Hectare
price range *
(more than
80% of
Agreements)

Central Victorian
Uplands

8

10

$110,000

$46,000 - $143,000

Gippsland Plain

21

29

$149,000

$85,000 - $250,000

Goldfields

39

38

$45,000

$25,000 - $66,000

Victorian Riverina

10

11

$101,000

$80,000 - $110,000

Victorian Volcanic
Plain

29

54

$170,000

HighlandsSouthern Fall

14

74

$34,000

Other bioregions

11

25

$370,000

•

$20,000 - $38,000
$206,000 $380,000

Third party offsets estimated 25-50% savings over first party

•

$49,000 $267,000

Estimated market turnover up to $100m

Prices vary by bioregion, EVC, location, rarity, demand and urgency of developer, landowner needs. Also initial trade, small or large trades
2013 Revisions

New provisions were recently announced:
• Like for like

 Threatened species – distribution models
 Everything else – increased flexibility

• Use of maps for site assessment
 reduced transaction cost
 assessment consistency
 accuracy of maps?

• Transaction cost reduction
 more ‘over the counter’
Biodiversity offsets in Canada Conference
Biodiversity offsetting in Victoria

Thank you

mlacrowe@gmail.com

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Biodiversity Offsetting in Victoria

  • 1. Biodiversity Offsets in Canada Conference Biodiversity offsetting in Victoria Michael Crowe February 2014
  • 3. Evolution of Offsetting in Victoria 1989 – Initial regulation of native vegetation clearing • an end to large scale clearing However offsetting was sporadic and not codified 1998 - Biodiversity mapping • Extant vegetation, 1750 vegetation, bioregions, threatened species Provided state-wide information base 2002 - Policy - the Native Vegetation Management Framework • No net loss, like-for-like, metrics ….. However developers found it hard to find their offsets 2007 – Offset market based on credit trading • Third party suppliers, brokers, credit register 2013 – Some policy amendments and technical improvements
  • 4. The Regulation Regulation of native vegetation clearing: • A planning permit required to clear native vegetation • Assessment of permit applications based on the biodiversity significance of the impact • Applications must demonstrate ‘avoid’ and ‘minimise’ steps of the mitigation hierarchy • The permit (if granted) requires an offset
  • 5. Offset policy in Victoria - 2002 The nature and size of the offset was set by Native Vegetation Management Framework policy (statutory document): – Avoid, minimise, offset – No Net Loss – Quality/area metric - habitat hectares – Offsets to be secure and ongoing – Additionality – Like for like rules – Biodiversity importance
  • 6. No net loss – quality is important
  • 7. Measuring site quality – 10 attributes in habitat hectares reduced cover of trees reduced recruitment reduced understorey diversity increased cover of weeds Habitat score = 0.50
  • 8. Increased quality at the offset site tree canopy cover size & connectivity of the patch large old trees understorey diversity recruitment of young trees logs & organic litter Habitat score = 0.90
  • 9. Estimating Gain Total gain = area x quality increment/ha • Improvement gain Increments in quality attribute scores resulting from restoration actions (eg revegetation) • Management gain Increments in quality attribute scores resulting from actions to control threatening processes (eg pest & weed control) • Security gain Increments in overall quality score depending on the changes in land use (eg establish protected areas) • Gain scoring includes rules for additionality
  • 10. Secure and ongoing • The landowner agreement – private land − permanent statutory contract − binds future landowners – on title − actions and commitments in the management plan − reporting and monitoring • Land surrender − private land donated to a permanent protected area • Upgrade to Protected Area − government re-classifies public land to higher security category through legislation
  • 11. The offsetting process - summary Developers Developers required to provide offsets • first party • third party (market) Loss site assessment, Permit application Local Government Determine small impacts Refer large impacts to State Government Permit may be granted Permit includes offset conditions – offset plan
  • 12. BushBroker price history Offset market Bioregion Number of Agreements credit prices Total number of Habitat Hectares Average price per Habitat Hectare * (of total Agreements) Habitat Hectare price range * (more than 80% of Agreements) Central Victorian Uplands 8 10 $110,000 $46,000 - $143,000 Gippsland Plain 21 29 $149,000 $85,000 - $250,000 Goldfields 39 38 $45,000 $25,000 - $66,000 Victorian Riverina 10 11 $101,000 $80,000 - $110,000 Victorian Volcanic Plain 29 54 $170,000 HighlandsSouthern Fall 14 74 $34,000 Other bioregions 11 25 $370,000 • $20,000 - $38,000 $206,000 $380,000 Third party offsets estimated 25-50% savings over first party • $49,000 $267,000 Estimated market turnover up to $100m Prices vary by bioregion, EVC, location, rarity, demand and urgency of developer, landowner needs. Also initial trade, small or large trades
  • 13. 2013 Revisions New provisions were recently announced: • Like for like  Threatened species – distribution models  Everything else – increased flexibility • Use of maps for site assessment  reduced transaction cost  assessment consistency  accuracy of maps? • Transaction cost reduction  more ‘over the counter’
  • 14. Biodiversity offsets in Canada Conference Biodiversity offsetting in Victoria Thank you mlacrowe@gmail.com