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Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham [email protected]

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Page 1: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

Roy Haines-Young,Centre for Environmental Management,School of Geography,University of [email protected]

Page 2: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

A system of conservation based solely on economic self-interest is hopelessly lopsided. It tends to ignore, and thus eventually to eliminate, many elements in the land community that lack commercial value, but that are (as far as we know) essential to its healthy functioning. It assumes falsely, that the economic parts of the biological clock will function without the uneconomic parts.

2

Page 3: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

Thinking about ecosystem services in the context of urban systems is a fundamental challenge for the future. Already most of us are urban dwellers…

▪ Majority of projected population growth is expected to occur in cities

▪ Worldwide 1.75 billion new urban residents are expected by 2030, most concentrated around fairly small cities in developing countries (UNPD, 2005).

▪ At global scales the impact of land use change on biodiversity by 2100 is likely to be more significant than climate change, nitrogen deposition, species introductions and changing atmospheric concentrations of carbon dioxide (Chapman et al. 2007; Sala et al. 2000)

Implications for ecosystem services….3

Page 4: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

Ecosystem services are the outputs of ecosystem functioning that directly contribute to human well-being….

4

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)Σ Pressures

Limit pressures via policy action?

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)Σ Pressures

Limit pressures via policy action?

Page 5: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

5

Page 6: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

Ecosystem services are the outputs of ecosystem functioning that directly contribute to human well-being….

6

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)Σ Pressures

Limit pressures via policy action?

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)Σ Pressures

Limit pressures via policy action?

Page 7: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

7

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)Σ Pressures

Limit pressures via policy action?

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Biophysical structure or

process(e.g. woodland habitat or net

primary productivity )

Service(e.g. flood

protection, or harvestable products)

Service(e.g. flood

protection, or harvestable products)

Function(e.g. slow

passage of water, or biomass)

Function(e.g. slow

passage of water, or biomass)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)

Benefit (Value)(e.g. willingness to pay for woodland protection or for

more woodland, or harvestable products)Σ Pressures

Limit pressures via policy action?

Or are outputs dependent on the abotic, urban fabric count too?

Page 8: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

8

Luck et al. (2009) BioScience 59: 223–235

Service providing units (SPUs) & Ecosystem Service Providers (ESP)

Page 9: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

9Luck et al. (2009) BioScience 59: 223–235

E.g. Eurasian jays (Garrulus glandarius) in oak forest in the National Urban Park of Stockholm, Sweden

E.g. Pest control….and some regulation services?

Page 10: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

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L: Diffuse pollution load

IncreasingStableDeclining

20.040.040.0

0.2 ± 0.75

K: Drainage management

New drainageNo changeRestoration

050.050.0

1.25 ± 0.75

G: Temperature increase (+ baseline)

0 to 0.50.5 to 11 to 22 to 2.52.5 to 3

30.040.020.09.00 1.0

0.905 ± 0.66

B: Carbon balance for peat (t/ha/yr)

IncreasingStableDecreasing

41.141.617.4

0.119 ± 0.36

A: Peat decomposition

highmoderatelow

65.111.623.3

3.5 ± 3.6

D: Peat_formation

ActiveInactive

92.27.81

4.72 ± 3.8

E: Habitat type

HeathlandMireAcid grasslandWoodlandImproved grasslandArable

0 100 0 0 0 0

2

R: Water table

RisingStableDropping

24.041.035.0

0.147 ± 1.8

Q: Decomposition Type

Newly aerobicTypically anerobicAnerobic

029.870.2

0.298 ± 0.46

F: Rainfall amount

IncreaseStableDecrease

30.060.010.0

0.2 ± 0.6

M: Liming

DoneNot done

0 100

-1

J: Grazing

HeavyLightNone

20.060.020.0

0.5 ± 0.77

H: Burning

NoneManagedWildfire

50.050.0 0

0.25 ± 0.25

V: Carbon Offset Value (£/ha/yr)

Value 10.8811

Ecological Structure or ProcessEcological Funcion or CapacityServiceBenefit

Driver (direct and indirect)

S: NO2-Emissions N: CH4-Emissions

C: Summer drought

likelyunlikely

60.040.0

1.2 ± 0.98

Bayesian Belief NetworkBayesian Belief Network

Page 11: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

11

L: Diffuse pollution load

IncreasingStableDeclining

20.040.040.0

0.2 ± 0.75

K: Drainage management

New drainageNo changeRestoration

050.050.0

1.25 ± 0.75

G: Temperature increase (+ baseline)

0 to 0.50.5 to 11 to 22 to 2.52.5 to 3

30.040.020.09.00 1.0

0.905 ± 0.66

B: Carbon balance for peat (t/ha/yr)

IncreasingStableDecreasing

28.335.636.1

-0.0392 ± 0.4

A: Peat decomposition

highmoderatelow

75.812.112.1

4.28 ± 3.2

D: Peat_formation

ActiveInactive

58.441.6

1.34 ± 5.7

E: Habitat type

HeathlandMireAcid grasslandWoodlandImproved grasslandArable

0 0

100 0 0 0

1

R: Water table

RisingStableDropping

24.041.035.0

0.147 ± 1.8

Q: Decomposition Type

Newly aerobicTypically anerobicAnerobic

36.031.432.7

1.03 ± 0.83

F: Rainfall amount

IncreaseStableDecrease

30.060.010.0

0.2 ± 0.6

M: Liming

DoneNot done

0 100

-1

J: Grazing

HeavyLightNone

20.060.020.0

0.5 ± 0.77

H: Burning

NoneManagedWildfire

50.050.0 0

0.25 ± 0.25

V: Carbon Offset Value (£/ha/yr)

Value -3.5990

Ecological Structure or ProcessEcological Funcion or CapacityServiceBenefit

Driver (direct and indirect)

S: NO2-Emissions N: CH4-Emissions

C: Summer drought

likelyunlikely

60.040.0

1.2 ± 0.98

Bayesian Belief NetworkBayesian Belief Network

Page 12: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

Ecosystem services are the outputs of ecosystem functioning that directly contribute to human well-being…. Are we dealing with ecosystem services OR environmental services? AND are we dealing with only those services generated by urban

systems and those on which they depend or affect?

12

The Urban Funnel Model (Luck et al. 2001)

‘The net flow of ecosystem services is invariably into rather than out of urban systems…. ’ (MA, 2005, Ch27)

Page 13: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

13

• Is the value of services supplied to urban systems fully recognised? What are the limits of supply?

• What can be done within urban areas to manage demand sustainably? What kinds of service can urban systems generate?

• How can we minimise the ‘dis-benefits’ flowing from urban systems and maximise the benefits

Page 14: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

Is the value of services supplied to urban systems fully recognised? What are the limits of supply? Market vs non-market goods ‘PES’ schemes & creating markets for

environmental services Investment in public goods….

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Page 15: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

What can be done within urban areas to manage demand sustainably? What kinds of service can urban systems generate? Exploitation and design of urban

structures and processes Retro-fitting urban areas to help manage

consumption and impacts ‘Decoupling’ and ‘reconnecting’ Understandings of place and locality…

and their hinterlands!15

Page 16: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

How can we minimise the ‘dis-benefits’ flowing from urban systems and maximise the benefits Urban expansion

▪ 8% of terrestrial vertebrate species on the IUCN Red List are threatened by urban development (McDonald et al. 2008).

Managing ‘downstream’ effects by planning and design (e.g. Jansson & Colding, 2008)

Cities as net exporters of ecosystem services?

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Page 17: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

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Page 18: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

In 1946 the economist Sir John Hicks defined (true or sustainable) income as the amount a person can consume over a given period and still be as well off at the end of that period as at the beginning….

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Human made capital

Natural capital

Benefit flowsBenefit flowsR

Benefit flowsBenefit flows

R

R

R

.. And so our planning system must take account of the reinvestment we need to sustain that natural

capital

Page 19: Roy Haines-Young, Centre for Environmental Management, School of Geography, University of Nottingham roy.haines-young@nottingham.ac.uk

A system of conservation based solely on economic self-interest is hopelessly lopsided. It tends to ignore, and thus eventually to eliminate, many elements in the land community that lack commercial value, but that are (as far as we know) essential to its healthy functioning. It assumes falsely, that the economic parts of the biological clock will function without the uneconomic parts.

19