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Ecology Centre, University of Kiel Ecosystems: Questions,Concepts, Theories and Indicators

Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

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Page 1: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

Ecology Centre, University of Kiel

Ecosystems:Questions,Concepts, Theories

and Indicators

Page 2: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

Outline• Questions referring to the ecosystem approach

– Operational guidance– Malawi principles

• Concepts to link theory and practice– Orientor theory– Ecosystem indicators– Ecosystems as parts of human-environmental

systems Applications will be shown by W. Windhorst

Ecosystem Approach, Salzau 2006Structure of the paper

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Operational guidance 1-5• Focus on relationships and processes within

ecosystems, e.g. stores and flows of energy, water, nurients)– Ecosystem resilience– Causes of biodiversity loss– Determinants for management decisions

• Enhance benefit-sharing– Environmental security– Sustainability– Valuation of ecosystem goods and services

How to quantify? How to treat irreversible processes?

Ecosystem Approach, Salzau 2006Guidelines and questions

How to conceive? How to apply?

How to quantify?How to link to ecosystem processes?

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Operational guidance 1-5• Use adaptive management practices

– Managing uncertainties– Management as a learning process– Flexible ecosystem management– Long-term orientation

• Select the appropriate scale and improve decentralization

• Ensure intersectoral cooperation

Ecosystem Approach, Salzau 2006Guidelines and questions

How to realize theseimportant demands in a conservative „managementenvironment“?

How to receive anappropriate supportfor LTER activities?

How to find theappropriate scale?

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The objectives of management of land, water and living resources are a matter of societal choice

• How to investigate the relevant societal preferences?• How to realize participative approaches?• How to translate scientific concepts into every-days-

language and how to educate stakeholders?

Many questions for social scientists and environmental planners

Ecosystem Approach, Salzau 2006Principle 1

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Management should be decentralized to the lowest appropriate level

• How to reduce the influence of centralized and hierarchical institutional settings?

• How is this assumption correlated with the scale approach in other principles?

• How will high-level constraints be implemented?

Apply hierarchy theory in environmental mangement

Ecosystem Approach, Salzau 2006Principle 2

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Ecosystem managers should consider the effects (actual or potential) of their activities on adjacent

and other ecosystems

• How to implement risk analysis concepts which indeed take into account indirect and de-localized effects?

• How to couple ecosystem processes with landscape dynamics?

• How to convince managers to use systems analysis approaches?

Link ecosystem science with landscape ecology

Ecosystem Approach, Salzau 2006Principle 3

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Ecosystem managers should consider the effects (actual or potential) of their activities on adjacent

and other ecosystems

Ecosystem Approach, Salzau 2006Principle 3

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Recognizing potential gains from management, there is usually a need to understand and manage the

ecosystem in an economic context• How to quantify (existing and potential) ecosystem

goods and services?• How to compare environmental values with economic

values?

Investigate the structures and functions in human-environmental systems

Look for innovative ecosystem based evaluation systems

Ecosystem Approach, Salzau 2006Principle 4

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Recognizing potential gains from management, there is usually a need to understand and manage the

ecosystem in an economic context

Ecosystem Approach, Salzau 2006Principle 4

Contextualconstraints

__________social change

political changetechnological change

cultural change

Human well-being__________basic supply

healthsocial security

education. . .

Ecosystemservices

__________Provisioning Regulating

Cultural

Landscapestate / integrity

__________

structuralfunctional

Land use__________

spatial (structural)intensity (functional)

Contextualconstraints

__________external

environmentalchanges

Pressure State

Im

pact

Driv

ers

Response

Decisionprocess

__________formation of opinions

governanceparticipation

Drivers__________

socioeconomicsociopoliticaldemographictechnological

cultural/religious

supp

ortin

g

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Conservation of ecosystem structure and functioning, in order to maintain ecosystem services, should be a

priority target of the ecosystem approach.

• How to measure ecosystem functioning?• How are structures and functions interrelated?• How to evaluate ecosystem organizations of future

states?• How to indicate ecosystem services?

Do research on linkages between structures and functions (ecosystem organization, ecosystem theory)

Derive ecosystem indicators Investigate ecosystem services

Ecosystem Approach, Salzau 2006Principle 5

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Conservation of ecosystem structure and functioning, in order to maintain ecosystem services, should be a

priority target of the ecosystem approach.

Ecosystem Approach, Salzau 2006Principle 5

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Ecosystems must be managed within the limits of their functioning.

• Which functions have to be taken into account?• How to quantify those limits?• How to cope with adaptation and constraints‘

dynamics?

Search good ecosystem indicatorsApply those indicators and link them with functioning

ecosystem modelsUse and develop scenario techniques

Ecosystem Approach, Salzau 2006Principle 6

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Ecosystems must be managed within the limits of their functioning.

Ecosystem Approach, Salzau 2006Principle 6

Throughfall

1

2

3

4

5

2Measured variablesModelledvariables

Precipitation

Interception

Stemflow

Infiltration (h)

Seepage

Groundwater

Stand andatmosphere

Humic soil layer

Mineral soil layers

Unsaturated zone

Aquifer

Aquatic system Influent

DischargeWater balance

Infiltration (m)

Precipitation

4

1 3 8

2 7

5

6

12

11

4

10

9

R

RP C

DS

H P

A

E G F

Biologicallydominated

energy flows;foodwebs

Meteorologicallydominated

energy flows

Global radiation

AbsorptionRefelexion Long wave

radiationEvapo-

transpiration

Verticaltemperature

gradients

Soilheat flux

Soiltemperature

P A R

Respiration

RespirationConsumption

Assimilation

Sec. Production

Prim. Production Litter fall Faeces

HumicSubstances

Elimination Growth Reproduction

Harvest

Y

Y

Meat

Emission - Immission

DepositionRainfall Fog

DepositionDry

Deposition Application

Interception AssimilationLeaching Plants Animals

DetritusThroughfall Stemflow

Litter

Adsorption

Precipitation

MicrobialDecomposit.

Vertical

LateralTransport

AssimilationAnimals

AssimilationPlants

Runoff

Interflow

Percolation

Basin

Inflow

Discharge

Sediment

MetabolismSubstances / Elements of InterestCalcium, Sodium, Potassium, MagnesiumOxigen, Nitrogen, Phosphorous, SulfurChloride, Hydrocarbons

Metabolism

Mobility

Detritus

Ground-Flow

GroundwaterDynamics

Gasexchange Transport

SuspendedLoad

Detritus

Dynamics

Atmosphere Stand

Litter

Soil

AquiferSediment

Transport

Heavy Metals, Pesticides, other Pollutants

Dynamics

Hydrochem.

MicrobialDecomposit.

AssimilationAnimals

AssimilationPlants

Plants Animals

water

Aquatic ecosystem

P

PK

SK

TK

Min

PK/SP

SK

Respiration

AktivesNahrungs-netz

Detritus/

- leicht zersetzbar

- schwer zersetzbar

Akt

ivit

ät &

Fre

qu

enz

ReichweiteEmergie

Kontrollfunktion

Speicher

Frequenz

water

nutrients

energy

community

ecosystem organization

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The ecosystem approach should be undertaken at the appropriate spatial and temporal scales.

• How do different scales interact?• How to find the appropriate scales?• How to correlate spatial and temporal features?

Intensify research on hierarchies and scale interactions

Ecosystem Approach, Salzau 2006Principle 7

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Holon Level (-1)

Holon Level (+1)

Holon Level (0)

Spatial Extent: SmallFrequencies: High

Constraints

Spatial Extent: HighFrequencies: Low

Minor Interactions Multiple Interactions

Filter

The ecosystem approach should be undertaken at the appropriate spatial and temporal scales.

Ecosystem Approach, Salzau 2006Principle 7

Focal level

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Recognizing the varying temporal scales and lag-effects ..of.. ecosystem processes, objectives for ecosystem

management should be set for the long term.

• How to foresee the outcome of long-term processes?

Intensify long-term ecological research

Ecosystem Approach, Salzau 2006Principle 8

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Recognizing the varying temporal scales and lag-effects ..of.. ecosystem processes, objectives for ecosystem

management should be set for the long term.

Ecosystem Approach, Salzau 2006Principle 8

http://www.lter-d.ufz.de/

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Management must recognize that change is inevitable.

• How to convince managers that stability is not the primary target any more?

• Where do we want ecosystem to develop towards?

Find quantitaive examples for Holling‘s adaptive cycleImprove models to cope with structural changes

Ecosystem Approach, Salzau 2006Principle 9

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Management must recognize that change is inevitable.

Ecosystem Approach, Salzau 2006Principle 9

Exergystored

Connectedness

exploitation

conservation

releasereorganization

Resiliance Alliance

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The ecosystem approach should seek the appropriate balance between, and integration of, conservation

and use of biodiversity.

• How to derive and compare ecosystem services?• How to integrate conservation and land use (outside

of preserved areas)?

Intensify research on ecosystem servicesInvestigate human-environmental systems

Ecosystem Approach, Salzau 2006Principle 10

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The ecosystem approach should seek the appropriate balance between, and integration of, conservation

and use of biodiversity.

Ecosystem Approach, Salzau 2006Principle 10

Reindeer herding:

Recommendations for sustainable land use

RENMAN

land use integrity

economysocial welfare

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The ecosystem approach should consider all forms of relevant information, including scientific, indegeneous

and local knowledge, innovations and practices.

• How to make all these forms of knowledge available?

Build up comprehensive information systems

Ecosystem Approach, Salzau 2006Principle 11

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The ecosystem approach should involve all releant sectors of society and scientific disciplines.

• How to realize this demand, e.g. in national administration?

• How to organize such a complex attempt?

Strengthen interdisciplinary cooperationBuild up interdisciplinary structures in environmental

administration

Ecosystem Approach, Salzau 2006Principle 12

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• Items to be observed: Ecosystem structures – functions – organizations

• Spatial levels to be integrated: Ecosystems – ecotones – landscapes – watersheds• Hierarchies to be involved: Scale interactions (short-long, small-large)• Destruction and decay to be included: Management of change – ecosystem dynamics• Humans to be integrated: Conservation – land use – services• Conventions to be realized: Sustainability – risk – health - integrity - security• Strategies to be followed: Interdiciplinary cooperation and participation

Ecosystem Approach, Salzau 2006Interim balance

Dem

ands

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Applying ecosystem concepts –a (first) case study

What is ecosystem integrity?

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What is ecosystem integrity?

PoliticalTarget:

SustainableDevelopment

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An alternative formulationfor the ecological component of sustainable development:

...“Meet the needs of future generations“....

= Keep available

the functions of nature(ecosystem services)

intergenerational (long-term)

intragenerational (global)

PoliticalTarget:

SustainableDevelopment

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ProductionFunctions

RegulationFunctions

InformationFunctions

CarrierFunctions

Processual Provision of Services

Page 30: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

- Protection cosmic influences- Regulation energy balance- Regulation chemistry atmosphere- Regulation chemistry ocean- Regulation climate- Regulation runoff & flood prevention- Regulation groundater recharge- Regulation waterbalance catchments- Regulation erosion and sedimentation- Regulation soil fertility- Regulation biomass production- Regulation organic matter- Regulation nutrient budgets- Regulation waste storage- Regulation biological control- Regulation habitat maintenance- Regulation diversity maintenance

ProductionFunctions

RegulationFunctions

InformationFunctions

CarrierFunctions

Processual Provision of Services

Page 31: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

ProductionFunctions

RegulationFunctions

InformationFunctions

CarrierFunctions

- Protection cosmic influences- Regulation energy balance- Regulation chemistry atmosphere- Regulation chemistry ocean- Regulation climate- Regulation runoff & flood prevention- Regulation groundater recharge- Regulation waterbalance catchments- Regulation erosion and sedimentation- Regulation soil fertility- Regulation biomass production- Regulation organic matter- Regulation nutrient budgets- Regulation waste storage- Regulation biological control- Regulation habitat maintenance- Regulation diversity maintenance

Basic processesof ecological

self-organisation

Processual Provision of Services

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The „functions of nature“ build up the framework for the ecological focus of sustainable development.

Providing the functions of nature results in anappropriate performance of the regulation functions

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The „functions of nature“ are based upon self-organizing processes.

The „functions of nature“ build up the framework for the ecological focus of sustainable development.

Providing the functions of nature results in anappropriate performance of the regulation functions

Page 34: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

The „functions of nature“ are based upon self-organizing processes.

To maintain the „functions of nature“ the ability for future self-organization of ecosystems

must be supported.

The „functions of nature“ provide the framework for the ecological focus of sustainable development.

Providing the functions of nature results in anappropriate performance of the regulation functions

Page 35: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

Eco-target „ecological integrity“:

preservation against non-specific ecological risks

The „functions of nature“ are based upon self-organizing processes.

To maintain the „functions of nature“ the ability for future self-organization of ecosystems

must be supported.

The „functions of nature“ provide the framework for the ecological focus of sustainable development.

Providing the functions of nature results in anappropriate performance of the regulation functions

Barkmann et al. 2001

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How to indicate integrity?

Page 37: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

NormativeArguments

System-analytical Arguments

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NormativeArguments

System-analytical Arguments

Risk Minimization and

Ecological Integrity

Thermodynamics,Gradient Principle

andOrientor Theory

Page 39: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

Indicatorsof the

Capacityfor Self-

Organization

Landuse-Intensity

Orientorsas

Indicators

Natural(primary)Sucession

MinorEcological

Risk

MajorEcological

Risk

Maturity

Pioneer Stage

NormativeArguments:

Risk Minimization andEcological Integrity

System-analytical Arguments:

Thermodynamics,Gradient Principle and

Orientor Theory

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Structural Gradients

Functional Gradients

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Structural Gradients

Functional Gradients

• Abiotic Gradients

• Biotic Gradients

• Hydrological Gradients

• Energetic Gradients

• Nutrient Gradients

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Structural Gradients

Functional Gradients

• Abiotic Gradients

• Biotic Gradients

• Hydrological Gradients

• Energetic Gradients

• Nutrient Gradients

• Inputs• Outputs• Efficiencies• Storages

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Structural Gradients

Functional Gradients

• Abiotic Gradients

• Biotic Gradients

• Hydrological Gradients

• Energetic Gradients

• Nutrient Gradients

• Biotop Heterogeneity

• Species Abundances

• Biotic Water Flows• Exergy Capture• Entropy Export• Metabolic Efficiency• Nutrient Loss• Storage Capacity

Proposed Indicators:

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DÄNEMARK

Ostsee

Kiel

HAMBURG

0 50

[km]

N

Amrum

Föhr

Sylt

MECKLEN-BURG -

VOR-POMMERNSchmalensee

BornhövederSee

BelauerSee

Alte Schwentine

0 600[m]

Schwer-

raumpunkt-

Stolper See

Fuhlen-see

Schie-ren-see

SCHLESWIG-

HOLSTEIN

Location of the Bornhöved Lakes District

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Case studyecosystem comparison

Examples from Barkmann et al. (2001): GAIA 10/2 and Müller (2005): Ecological Indicators 5/4

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• Biotic Water Flows• Exergy Capture• Entropy Export• Metabolic Efficiency• Nutrient Loss• Storage Capacity

• Biotop Heterogeneity• Species Abundances

Proposed Indicators:

Beech ForestArable Land

Baumann (2001), Barkmann et al. (2001)

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Exergy Capture

Biodiversity

Abiotic Heterogeneity

Storage

Biotic Water Flows

Nutrient Loss -1

Entropy Export

MetabolicEffiency -1

Capacity for Self-OrganisationCapacity for Self-Organisation

Baumann et al. 2001

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Exergy Capture

Biodiversity

Abiotic Heterogeneity

Storage

Biotic Water Flows

Nutrient Loss -1

Entropy Export

MetabolicEffiency -1

50 %

100 %

150 %

Capacity for Self-OrganisationCapacity for Self-Organisation

Beech Forest

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Exergy Capture

Biodiversity

Abiotic Heterogeneity

Storage

Biotic Water Flows

Nutrient Loss -1

Entropy Export

MetabolicEffiency -1

50 %

100 %

150 %

Beech Forest

MaizeMaizeFieldField

Capacity for Self-OrganisationCapacity for Self-Organisation

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Case studyland use scenarios

Examples from Schrautzer et al. (i.p.): Ecological Studies and Müller et al. (2006): Ecological Indicators 6/1

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Ecosystem types and modelled landscape units

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- nitrogen balance- carbon balance

- chemical budgets storage capacity

- nitrogen net mineralization- nitrate leaching- denitrification

- chemical budgets nutrient loss

- evapotranspiration / transpiration- hydrological budgets biotic water flows

- NPP/soil respiration- energy budgets metabolic efficiency

- microbial soil respiration (MSR)- energy budgets entropy production

- net primary production (NPP)- energy budgets exergy capture

- number of plant species- plant strategy types

- biotic structures

Indicator(s)Indicandum

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deforestationdrainage

grazingmowing

DE, MO, GR

wet grasslands , weakly drained, mesotrophic wet grasslands , weakly

drained, eutrophic

wet grasslands ,moderately drained

EU, DR, GR, MO

wet grassland ,intensively drained

EU, DR

wet alder carrs,mesotrophic wet alder carrs,

eutrophic

drained alder carrs,mesotrophic drained alder carrs,

eutrophic

EU

DE, MO, GR

EU

DRDR

EU : ploughing

States of development

DE: deforestationDR: drainageEU: eutrophicationGR: grazingMO: mowing

DE, MO, GR

wet grasslands , weakly drained, mesotrophic wet grasslands , weakly

drained, eutrophic

wet grasslands ,moderately drained

EU, DR, GR, MO

wet grassland ,intensively drained

EU, DR

wet alder carrs,mesotrophic

wet alder carrs,mesotrophic wet alder carrs,

eutrophicwet alder carrs,

eutrophic

drained alder carrs,mesotrophic

drained alder carrs,mesotrophic drained alder carrs,

eutrophicdrained alder carrs,

eutrophic

EU

DE, MO, GR

EU

DRDR

EU Pl :

Retrogressional sequence on histosols

Disturbances:

Land

use

int

ensity

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Ecosystem Indicators for Wet Grassland Ecosystems(Intensively Drained Ecosystems = 100%)

0

50

100

150

200

ID MD WDEU WDME

Net Primary Production

N Net Mineralization

N Leaching

Denitrification

Microbial Soil RespirationCarbon Balance

Nitrogen Balance

NPP / Soil Respiration

Evapotranspiration /Transpiration

No. of Plant Species

Hem 2

Intensively Drained

Moderately Drained

Weakly Drained, Eutrophic

Weakly Drained, Mesotrophic

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Ecosystem Indicators for Wet Grassland Ecosystems(Intensively Drained Ecosystems = 100%)

0

50

100

150

200

ID MD WDEU WDME

Net Primary Production

N Net Mineralization

N Leaching

Denitrification

Microbial Soil RespirationCarbon Balance

Nitrogen Balance

NPP / Soil Respiration

Evapotranspiration /Transpiration

No. of Plant Species

Hem 3

Hem 2

Intensively Drained

Moderately Drained

Weakly Drained, Eutrophic

Weakly Drained, Mesotrophic

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Ecosystem Indicators for Wet Grassland Ecosystems(Intensively Drained Ecosystems = 100%)

0

50

100

150

200

ID MD WDEU WDME

Net Primary Production

N Net Mineralization

N Leaching

Denitrification

Microbial Soil RespirationCarbon Balance

Nitrogen Balance

NPP / Soil Respiration

Evapotranspiration /Transpiration

No. of Plant Species

Hem 4

Hem 3

Hem 2

Intensively Drained

Moderately Drained

Weakly Drained, Eutrophic

Weakly Drained, Mesotrophic

Page 57: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

Ecosystem Indicators for Wet Grassland Ecosystems(Intensively Drained Ecosystems = 100%)

0

50

100

150

200

ID MD WDEU WDME

Net Primary Production

N Net Mineralization

N Leaching

Denitrification

Microbial Soil RespirationCarbon Balance

Nitrogen Balance

NPP / Soil Respiration

Evapotranspiration /Transpiration

No. of Plant Species

Hem 5

Hem 4

Hem 3

Hem 2

Intensively Drained

Moderately Drained

Weakly Drained, Eutrophic

Weakly Drained, Mesotrophic

Page 58: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

0

50

100

150

200

ID MD WDEU WDME

Net Primary Production

N Net Mineralization

N Leaching

Denitrification

Microbial Soil RespirationCarbon Balance

Nitrogen Balance

NPP / Soil Respiration

Evapotranspiration /Transpiration

No. of Plant Species

Loss of Structures

Loss of Cycling Efficiencies

Loss of Metabolic Efficiencies

Management Target and Ecosystem Consequences

Gradient Degradation

Landscape Functional Sink

Landscape Functional Source

Page 59: Ecosystems: Questions,Concepts, Theories and Indicators · Ecosystems: Questions,Concepts, Theories and Indicators. Outline ... Seepage Groundwater Stand and atmosphere Humic soil

Conclusions• Ecosystem states can be indicated on a

holistic level• Ecosystem development can be depicted on

the base of complex models• Ecosystem science is ready for further

applications

• Ecosystem principles provoke many questions to science and practice

Ecosystem Approach, Salzau 2006Guidelines and questions