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‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs...

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‘How do we know and make sure estuaries and seas are healthy?’ Mike Elliott Institute of Estuarine & Coastal Studies, University of Hull, U.K. http://www.hull.ac.uk/iecs
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Page 1: ‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs Flood & Water Management Act Flood & Coastal Erosion Risk Management River Basin

‘How do we know and make sure

estuaries and seas are healthy?’

Mike Elliott

Institute of Estuarine & Coastal Studies, University of Hull, U.K.

http://www.hull.ac.uk/iecs

Page 2: ‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs Flood & Water Management Act Flood & Coastal Erosion Risk Management River Basin

Pressures, Valuing, Valuation and Management

• Paradigm 7: Estuaries have more human-induced pressures than

other systems and these include both exogenic unmanaged

pressures and endogenic managed pressures. Consequently their

management has to not only accommodate the causes and

consequences of pressures within the system but, more than other

ecosystems, they need to respond to the consequences of external

natural and anthropogenic influences.

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Challenges for TW management:

• Where are the problems?

• What changes do they cause?

• What is the impact of these on ecosystem structure and functioning?

• What are the repercussions for ecosystem valuation based on economy-

ecology interactions?

• What are the future environmental changes and economic futures?

• What governance framework is there, what do stakeholders need?

• What can we do about the problems?

• Where are the risks and how to address them now and in the future?

• What are the governance successes, failures and implications?

• How ‘good’ is the decision-making?

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Socio-ecological science & tools - Integrating Concepts:

Physico-chemical structure / stock

Physico-chemical processes / functioning

Ecological structure / stocks

Ecological processes / functioning

Individual (use & non-use) values

Total Economic

Value

Stock of natural capital - Natural carrying capacity

Shared (monetary & non-monetary)

Natural environmental system & Total Ecological Value

Ecological capital

Total Social Value

[ME/JPA/DB (UoH) & RKT (UEA) Coastal zone ecosystem services HG v9]

Physico-chemical capital

Socio-Econo-Techno System measured as TSSV (Total Societal & System Value) & Socio-economic carrying capacity

Intermediate ecosystem services

Final ecosystem services

Complementary assets (human capital – population expending

energy, time, money, skills)

Ecosystem goods Societal benefits

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DPSIR modelling framework

(Also * DPSWR, DPSEEAC)

Drivers (D):The human activities

responsible

State Change (S):The change in background

status

Impact (I):The changes to the

system

Response (R):The 'human' responsePressures (P):

The causes of the problem(s)

EnvironmentBoundary

System

Natural Change

- Climate Change- Natural variability

- ...

*

Drivers

Pressures

State change

Welfare

Response;

Drivers

Pressures

State change

Exposure

Effects

Action

Context

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VECTORS of Change – From Drivers through Impacts to Policy Responses - Examples

Driver Pressure State Change Impact Response

Increasing

urbanisation,

agriculture and

industrialisation

Changes in

temperature regimes

and weather patterns

(storminess)

Climate change and related impacts (natural and anthropogenic;

effects on structure and functioning and on Ecosystem Services)

Local adaptation,

compensation; policy,

economic & legal

mechanisms

Increased CO2 and

decreased pH

Ocean acidification Reduced ecosystem services,

ability for waste removal

Global agreements

Diffuse and point

source land-based

pollution

Polluted components; HAB

formation

Environmental and food

quality reduction, reduced ES

Diffuse and point-

source discharge

controls

Space removal Loss of carrying capacity Loss (& gain) of ecosystem

services

Planning controls,

MSP

Demand for food Capture fisheries Changes to local populations,

spawning sustainability, by-catch

and habitat damage

Stock viability, ecosystem

services reduction

Economic and legal

instruments

Aquaculture Changes to local ecology Ecosystem services (+ and -)

Maritime transport

(demand for

movement of

goods, etc)

AIS introduction,

infrastructure

demands, pollution,

dredging

Community change, habitat

alteration

Pest introduction, invasive and

nuisance species; effects on

ecosystem services

Introduction of new

ballast water

technologies and

practices

Energy demands Infrastructure

demands

Habitat loss and gain,

energy/hydrodynamic change

Effects on ecosystem services

(+ and -)

Marine spatial

planning, economic

and legislative

constraints

Tourism &

recreation

demands

Loss of natural habitats,

reduction in resilience

Planning controls,

coastal spatial

planning

Total societal

demands

Interactions between

multiple users &

sectors

Cumulative effects on natural

structure and functioning

Effects on ecosystem services Changes in policy

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Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

ExUP

ExUP

ExUP

EnMP

EnMP

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Example I: Commercial fisheries (DPSIR I), recreational fishing (DPSIR II)...

Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

• Bylaws through NESFC to allow taking of fish,

shrimps and shellfish.

• Historical fisheries within the estuary and near-

coast and deepwater commercial fisheries.

• Historical eel-fishery in estuary and

licensing/conservation measures for migratory

salmonids.

• Extensive recreational fishing off seawalls and

at Spurn Point.

• Samphire collection at outer saltmarsh areas

Page 9: ‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs Flood & Water Management Act Flood & Coastal Erosion Risk Management River Basin

Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

Aim of

Management

Plan

P

S

D

I

R

PS

DI

R

P

S

D

I

R

P

SD

IR

P

S

D

I

R

Environment

Boundary

System

Natural

ChangeNatural

Change

Natural

Change

Natural

Change

Natural

Change

I

II

IIIIV

...N

Page 10: ‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs Flood & Water Management Act Flood & Coastal Erosion Risk Management River Basin

International

Law, EU

Directives &

National

Implementation

(England)

Site designations (e.g. SSSI)

Marine (water) Environmental

Protection

UWWTD

Bathing Waters

Nitrates

ProposedMSP &

ICM

Urban Waste Water

Treatment Regs

Sensitive area

Bathing beaches

Bathing Water Regs

Nitrate Vulnerable

Zones

Nitrate Pollution Prevention Regs

Good Chemical Status & Good

Ecological Status

Marine spatial planning &

coastal zone management

Pollution Prevention & Control Regs

Water Environmental (WFD) Regs

Licences, Consents &

Authorisations

Flood Risk & Hazard

Maps

Multimetric Indices

Programme of measures, qualitative descriptors,

ecosystem-based management approach, MPAs

Sea Fish Regulation

Act Sea Fisheries (Shellfish) Act

Salmon & Freshwater

Fisheries Act

?

Implementation method

Enabling Legislation

Protection Afforded

EC Directive or Strategy

(*) In 2013 the WFD replaced the Dangerous Sub. Dir.; Freshwater Fish Dir.; Shellfish Waters Dir. & Groundwater Dir.

Marine Strategy

Regs

Energy Act

?

International Law or Commitments

International Bodies &

Conventions

Byelaws, Orders, gear and catch

restrictions

Sea Fish (Conservation) Act as amended

by the Sea

Fisheries (Wildlife Conservation) Act

Sustainable fisheries & safeguarding the marine environment

Renewable Energy

Renewables targets for

2020

Policy & Targets

UN CONV. on BIOLOGICAL DIVERSITY

UNCLOS

MARPOLSafer shipping

navigation, pollution control and operation

Various EU Regs to control

shipping & pollution from

ships

RAMSAR CONV.

BERN CONV.

BONNCONV.

Endangered species

protection

Control of Trade in Endangered

Species (COTES) Regs

Enforcement

IPPC

Strategic Environmental Assessments to include transboundary effects

Environmental Assessment Regs

Licences, Consents &

Authorisations

Marine projects are subject to Environmental Impact

Assessment

Town & Country Planning (EIA)

Regs

Marine Works (EIA)

Harbour Works (EIA) Regs

Waste Hierarchy &

Good Practice

Waste Regs

Environmental Standards

Waste FD

LONDON CONV. &

PROTOCOL

KEY

OSPAR, HELCOM,

UNEP-MAP, BUCHAREST

Reg. Seas Conv

Marine Notices -shipping, guidance

& information

BALLAST WATER CONV.

Prevention, management &

control of harmful aquatic organisms

& alien species

Basic Fish Regs

CFP

ICES

Favourable Conservation

Status

EU Strategy on

Invasive Alien Sp.

ProposedIAS Reg

Sets maximum acceptable

levels

Contaminants in Food Regs

Safe consumption

of fish & shellfish

Contaminants in Food Reg

WFD (*)

Env Liability

Prevention & remedy of

env. damage

Env. Damage (P&R) Regs

Polluter pays principle & remedial measures

FRMD

Flood Risk Assessment

Flood Risk Regs

Flood & Water Management Act

Flood & Coastal Erosion Risk Management

River Basin Management Plans, Heavily Modified Water

Bodies & Artificial Water Bodies

MSFD

Various Regs to control

CITES fauna & flora

CITESHabitats & Species

Natura 2000 sites (SAC/SPA)

Habitat & Species

Protection

Biodiversity & Species

Action Plans

Conservation of Habitats

and Species Regs

Offshore Marine

Conservation Regs

Reg 35 advice, Article 17 condition monitoring, Appropriate

Assessments (AA), Habitat Regulations Assessment (HRA) &

Likely Significant Effect (LSE)

Licences, Consents &

Authorisations

Marine planning

Conservation / Biodiversity

protection (MCZ)

Management Plans &

Schemes

Coastal Recreation

Licences

Licences, Consents &

Authorisations

Licences, Consents &

Authorisations

H1 Method

UN FRAMEWORK CONV. ON CLIMATE CHANGE (UNFCCC)

KYOTO PROTOCOL

Harbours Act

Revision and Empowerment

Orders. Conservation duties on ports

Local Harbour Acts

Harbour & Works Licences

Merchant Shipping Regs

Licences, Consents &

Authorisations

ESPOO CONV.

SEA

Applications for Nationally Significant Infrastructure Projects

(NSIPs) / Marine Licences

Planning Act (as amended)

Infrastructure Planning (EIA)

Regs

IMO

INT. CONV. ON SALVAGE

Marine archaeology

Protection of marine archaeology

National Heritage Act

Protection of Wrecks Act

Merchant Shipping Regs

Electricity Act

Climate Change Act

Conserving wider biodiversity

Ancient Monuments & Archaeological Areas

EIA

Licences, Consents &

Authorisations

Wild Birds

EU Biodiversity

Strategy

Wildlife & Countryside Act (as amended)

NERC Act

EU Integrated Maritime Policy

Marine & Coastal

Access Act

Good Environmental

Status

Site designations

(MPAs e.g. SAC / SPA)

Page 11: ‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs Flood & Water Management Act Flood & Coastal Erosion Risk Management River Basin

The ecosystem-based approach

‘A comprehensive integrated management of human activities based on the best

available scientific knowledge about the ecosystem and its dynamics, in order to identify

and take action on influences which are critical to the health of the marine ecosystems,

thereby achieving sustainable use of ecosystem goods and services and maintenance of

ecosystem integrity.’

The Qualitative Descriptors within the Marine Strategy Framework Directive

Biodiversity Fishing Foodwebs

Seafloor integrity

Hydrography Pollution Litter

The Marine Strategy Framework Directive

Page 12: ‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs Flood & Water Management Act Flood & Coastal Erosion Risk Management River Basin

2. No alien

species

4. Protect trophic and

reproductive

functioning

3. Protect

commercial species

Pressures 2:

Physical & biological

extraction (water,

space, substrata,

fisheries)

11 Prevent harm from

energy inputs, including

noise

10. Prevent harm

from marine litter

6. Protect hydro-

sediment functioning for

the benthos

8. Stop contamination

becoming pollution stricto

sensu

Pressure 1: Physical,

chemical & biological

inputs

Physical control of

the ecological

system

5. Minimise eutrophication and

its undesirable effects

9. Stop contamination

harming consumers

7. Protect

hydrographical regime

1. Biological

diversity

maintained

Pressures 1 & 2 are ‘endogenic

(regionally) managed pressures’

onto which are superimposed

‘exogenic unmanaged pressures’

(e.g. climate change); for the latter

the consequences rather than the

causes are managed.

Physical control

Pressures on the system

Pressure descriptors

Biological descriptors

Hydrological descriptors

Climate change

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Ecological Status (WFD)

Reference Variation

High None or small

Good Slight

Moderate Moderate

Poor Important

Strong Bad

Environmental Status (MSFD)

Good

Not Good

Comparison of the WFD and MSFD

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Unhealthy systems?

Medical ( *1 ) – • Diagnosis • Prognosis • Treatment • Recovery

Prevention (*1 Steevens et al 2001 - Human Ecol. Risk Ass.)

Environmental – • Assessment (*2)

• Prediction • Remediation/Creation/

Restoration • Prevention

(* 2 using extension of symptoms for the diagnosis of ecosystem pathology)

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Definitions of degradation and recovery:

‘Degradation - the reduction and removal of self-

sustaining ecological functioning and of carrying

capacity (manifest as poorer ecosystem services)

showing an ecological structure and functioning

(and reduced fitness for survival at one or more

levels of biological organisation) reflecting

disturbed conditions and an ultimate loss of

societal benefits’;

‘Recovery - the attainment of self-sustaining

ecological functioning and carrying capacity (as the

maintenance and delivery of ecosystem services)

with appropriate ecological structure at population

and community level reflecting undisturbed

conditions and a restoration of societal benefits’.

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INCREASING ECOSYSTEM QUALITY

(Structure x Functioning)

DEGRADATION

Enhancement

Mitigation

Recovery

Rehabilitation

Restoration

Replacement

Original Ecosystem Improved-Habitat New Ecosystem

Active Process Passive Process

Degraded Ecosystem

(with Mitigation)

Degraded Ecosystem

(without Mitigation)

Habitat Creation

Compensation

Page 17: ‘How do we know and make sure estuaries and seas are …...Flood Risk Assessment Flood Risk Regs Flood & Water Management Act Flood & Coastal Erosion Risk Management River Basin

Functioning

What should there

be (status)?

Ecological & economic goods

& services

Ecosystem

Approach

& why (habitat needs)?

What is lost (reduced

carrying capacity)?

No

Pro

du

ce

Ma

na

ge

me

nt P

lan

!

Can it be

recovered?

HMWB

(hydromorphology)

Yes

Recreate

habitats

Economic justification

(xGEcS)

Report

Compensate the

system

Temporary

habitat loss

Water quality

barrier

Remedial action -

pollution control

Restore habitat

Measure functioning

(need indices of change)

Regain carrying

capacity

Permanent habitat loss

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Biological change

changes in cells

changes in organisms

changes in populations

changes in

communities

changes in

ecosystems

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Biological change

changes in cells

changes in organisms

changes in populations

changes in

communities

changes in

ecosystems

Speed of

response

Inherent

variability

Ease of

detection

of effect

Complexity

of system

Specificity

of cause

Confidence

in methods?

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XENOBIOTIC

EXPOSUREExternal

Site of

damage

Morphological

change

Morphological

anomalies

Entry of parasites

and pathogens

Life history

stage

Internal Gills

Mortality

Stomach

Liver

Change to

behaviour

Avoidance

Ecological

Genetic

Changes in ecological

population structure

Effects on

condition

Growth

Effects on

Survivability

Marketability

Immunological

response

SOCIO-

ECONOMICS

Changes in

Community Structure

EFFECT ON

YIELD

Uptake

Genetic

damage

Genotypic

Adaption

Change in genetic

population

structure

Decreased

fecundity

Poorer

condition

Decreased

growth

Increased

respiration

Physiological

response

Non-

Adaption

Biochemical

response

Adaption

Nervous system

damage

Hormonal

Detoxification

Anatomy

Marketability

Storage

Reproduction

Passage to

offspring

Storage

breakdown

Bioaccumulation

Gonad storage

Excretion

Liver

tumours

Liver/ somatic

index

Survival

Somatic

index

Energetics &

scope for growth

*

*

Figure 10.4 Pollution effects in fishes – conceptual model (Elliott & Hemingway, 2002; also Elliott et al 2003; Lawrence & Hemingway 2003 - XENOFISH)

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Science & Types of Monitoring: • Surveillance monitoring

• Condition monitoring

• Operational monitoring

• Compliance monitoring

• Check monitoring

• Self-monitoring

• Toxicity testing

• Investigative monitoring

• Diagnostic monitoring

• Feedback monitoring

(Elliott, Mar Poll Bull, 2011; See also Elliott &

de Jonge (1996) The need for monitoring the

monitors and their monitoring. Mar. Poll. Bull.

32(3): 428-9)

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Ecosystem health assessment (or monitoring)

programme:

1. Analysis of main processes and structural

characteristics of ecosystem;

2. Identification of known or potential stressors;

3. Development of hypotheses about how those

stressors may affect each ecosystem;

4. Identification of measures of environmental quality

and ecosystem health to test hypotheses.

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Proactive/A priori assessment:

• EIA (process) linked to outcome (ES) (Directive, planning permission)

• Appropriate Assessment (linked to HSD)

• Status and pressures Monitoring (linked to WFD)

• Cumulative Impact Assessment

• Strategic Environmental Assessment - linked to Marine Spatial Planning

• H1/EpiSuite - linked to complex effluents, IPPC authorisation (IPPC Directive)

• Data-base toxicology assessment (linked to licence creation, assess re. ability to accumulate, be persistence, magnify, be toxic) (but limitations cf. synergy/antagonism) (see Gray & Elliott 2009)

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Risk Analysis comprises:

• Hazard Identification: involves specifying the adverse

event, which is of concern.

• Risk Assessment: takes into account the probability (the

actual likelihood and not just the possibility) of the hazard

occurring, the consequences of that hazard occurring, and

the degree of uncertainty involved.

• Risk Management: involves identifying and implementing

the best option for reducing or eliminating the likelihood of

the hazard occurring.

• Risk Communication: implies the open exchange of

explanatory information and opinions that leads to better

understanding and decisions.

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Hazard leading to Risk (depending on assets)

A) Surface hydrological hazards

B) Surface physiographic removal by natural processes - chronic/long-term

C) Surface physiographic removal by human actions - chronic/long-term

D) Surface physiographic removal - acute/short-term

E) Climatological hazards - acute/short term

F) Climatological hazards - chronic/long term

G) Tectonic hazards - acute/short term

H) Tectonic hazards - chronic/ long term

I) Anthropogenic microbial biohazards

J) Anthropogenic macrobial biohazards

K) Anthropogenic introduced technological hazards

L) Anthropogenic extractive technological hazards

M) Anthropogenic acute chemical hazards

N) Anthropogenic chronic chemical hazards

Hazard & Risk Typology:

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Attributes for the diagnosis of ecosystem pathology: = 7 indicators for general application:

• primary production

• nutrients (fate & effects)

• species diversity (abiotic areas)

• community instability (biotic composition)

• size and biomass spectrum

• disease/anomaly prevalence

• contaminant uptake and response

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Selection Criteria for Indicators of Ecosystem Response:

• high signal to noise ratio

• rapid response

• reliability/specificity of response

• ease/economy of monitoring

• relevance to end-point

• monitoring feedback to regulation

+

• general applicability

• backed-up by good science

Types of Indicators:

• structure vs. functioning

• spatial vs. temporal

• taxonomic vs. non-taxonomic

• bottom-up causes vs. top down responses

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Basis - TraC Footprints and Trajectories

• HA1 The footprint of an impact due to an anthropogenic stressor has an extent and

magnitude proportional to the intensity of the stressors and the sensitivity of the

receiving environment.

• HA2 The determination of effect is dependent on the complexity and variability of

the component or habitat being influenced by the stressor such that

environmentally or ecologically variable systems require a greater stressor in order

to manifest a change.

• HA3 The speed of recovery from the effects of the stressor is dependent on the

turnover rate of the ecological components being affected by the stressors and the

timing of the removal of the action of the stressor.

• In the European context Article 1(3) of the Marine Strategy Framework Directive

(MSFD) (EC 2008) states that:

‘Marine strategies shall apply an ecosystem-based approach to the

management of human activities, ensuring that the collective pressure of such

activities is kept within levels compatible with the achievement of good

environmental status and that the capacity of marine ecosystems to respond to

human-induced changes is not compromised, while enabling the sustainable

use of marine goods and services by present and future generations’.

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Resistance

(amount of pressure that can

be applied without major

deterioration in status)

Inherent variability and ability to

change without collapse ( due to

resistance)

Pressure

increasing hysteresis

(type I) Amount system is

disturbed (deterioration

in status)

May be zero

Resilience

(b) (a)

hysteresis (type II)

Pressure

decreasing

System

status (*)

Pressure

Key:

(*) relative to a defined metric of structure or function

(a) total resilience

(b) partial resilience

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Integrated Environmental Assessments

e.g.

community health

(sea-bed quality as shown by benthic analyses);

individual health

(as shown by invertebrate bioassay, e.g. amphipod

burrowing bioassay);

environmental (abiotic component)

degree of contamination

(concentration of persistent chemicals in

sediments)

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Gaia outfall –

Biotic data

(Quintino etal

2003)

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Example: changes in environmental chemical determinands (Adapted from de

Quintino et al., 2001).

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Corophium multisetosum

Sediment total bioassay

Acute assay – LC50

Chronic assay – EC50

(from Quintino etal 2003)

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Example: changes in sedimentary quality using triad approach (high values

against reference values for the triad components (Adapted from Quintino et al.,

2001).

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Aim (economic &

ecological goods &

services)

Set indicators (birds/fishes;

tonnage/ wealth creation, quality

of life/non-infraction) Perform monitoring (surveillance,

condition, compliance,

investigative)

Measure status (EII,

habitat mapping)

Action required (defined in

advance)

Set objectives

(ecological,

economic, societal,

legislative)

Fulfil ‘The Ecosystem

Approach’

Action not required

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To be successful, management measures or responses to

changes resulting from human activities should be:

The 10 tenets: From Philosophy to Tool:

• Ecologically sustainable

• Technologically feasible

• Economically viable

• Socially desirable/tolerable

• Legally permissible

• Administratively achievable

• Politically expedient

• Ethically defensible (morally

correct)

• Culturally inclusive

• Effectively communicable

Marine management

tools needed to cover

all of these.

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Figure 1: considerations in holistic & adaptive environmental management

(red arrows denote linkages between topics; black arrows denote direction of influence)

Extractors (D, P) (econ., technol.)

Inputters (D, P) (econ., technol.)

Regulators (R) (leg., admin.)

Affectees (I) (soc., ethic., cult.)

Influencers (I) (polit.)

Beneficiaries (I) (soc., ethic, cult.)

Horizontal Integration across stakeholders (refer to DPSIR and 10 tenets)

.... Ecosystem Services & deliver ..... (I(W))

who raise awareness of ...... (comm.)

....Societal Benefits for the ...

uses/users providing .../affecting .... .... who control the ...

…. fundamental processes (S) (ecol.) to create … (D+P) + R ≠ S + I

e.g. Conflict Res., 10 tenets, PPP, PP, EIA, CBA, MCA, LPI

Indicators + monitoring, e.g. EII

Maintaining, protecting and enhancing nature & .... (S) (ecol.)

The Ecosystem Approach

(b) localised human demands (endogenic managed pressures)

(a) wider pressures, e.g. climate change (exogenic unmanaged pressures)

Vertical Integration of governance across geopolitical levels

global

ecoregion

regional

national

local

Source of problems (activity-pressure-impact chain) which require ....

..... Risk assessment methods & response

to ensure no impact on .....

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[email protected]

A premise – “changing systems are not a problem for the

ecology as it will adjust to any new situation and

create a new equilibrium, they are only a problem

for society, i.e. we might not be able to obtain the

societal benefits from ecosystem services that we

wish to and we may not like the new ecology but

eventually we will have to accept it”

The challenge - What do we mean by environmental health, how

do we measure it and how do we communicate

that to a non-specialist audience, how does this

relate to current national and European

legislation and policy and what are the

repercussions of this for monitoring?


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