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Implementing the Habitats Directive: how science can support decision making 1 Gerald Louette International Conference Antwerp, 12-13 December 2012

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Page 1: Implementing the Habitats Directive: how science can ... · Implementing the Habitats Directive: how science can support decision making 1 ... Favourable Conservation Status range,

Implementing the Habitats Directive:

how science can support decision making

1

Gerald Louette

International Conference Antwerp,

12-13 December 2012

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Contents

Science and the Habitats Directive

Support of science in decision making

Examples from Flanders (northern Belgium)

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Science and the Habitats Directive

Art. 1 and 2 Favourable Conservation Status

range, area, structure & functions, typical species

range, population, habitat of species

Favourable Reference Values (Interpretation manual, Evans & Arvela 2011) should be based purely on scientific grounds

should be based on the ecology and genetics

must be at least the area / population when the HD came into force

Art. 11 Surveillance of the conservation status

Art. 17 A report on the implementation of measures and main results of surveillance

Art. 18 Research and scientific work with respect to Art. 2 and 11

Scientific work with respect to Art. 4 (delineation of sites) and 10 (essential features for migration)

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Favourable Conservation Status

Priorities

Calibration model

Conservation Measures

Cost-efficiency

Manual for nature management

Monitoring Conservation Status

Participation & leanness

Data gathering agreement

Role of science

Ambition of society

Fusion results to …

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Favourable Conservation

Status

Priorities

Calibration model

Support of science in decision making

Favourable Conservation Status

Population Viability Analysis,

modeling, ecological signatures,

actual and historical data, expert

judgment

Conservation objectives on

member state level (Paelinckx et

al. 2009, Louette et al. 2011)

Conservation objectives on a local

level (Adriaens et al. 2008, T’jollyn

et al. 2008)

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Favourable Conservation Status

Regional conservation status

Local conservation status (tables)

European dry heaths Triturus cristatus

Regional (Flanders)

Range 6167 ha 11852 ha

Area 5788 ha

Structure & Functions incl. Typical species Quality

Spatial coherence (75% of the area in a patch of minimal size) 5 ha

Typical flora & fauna species no Red List status

Populations 240 ponds

Local quality (sample unit: permanent quadrat)

Disturbance Grass encroachment less than 50%

Forest encroachment less than 30%

Structure Age structure shrubs more than 1 stage

Shrubs more than 50%

Vegetation Number of typical flora species more than 1

Local quality (sample unit: reproduction site)

Population Size more than 20 adults

Reproduction more than 20 juveniles

Spatial structure (distance to nearest) less than 2 km

Habitat quality Presence of fish no

Shrubs (distance to) less than 50 m

Shading less than 33%

Submerged vegetation more than 10%

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Favourable Conservation Status

Local conservation status (tables)

A pond should harbor

20 adults

Reproduction

No fish

Distance less than 2 km

A permanent quadrat (4x4 m)

should harbor

Less than 50 % grass

Less than 30 % trees

> one typical species

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Favourable Conservation Status

Art. 2

Measures taken shall take account of economic,

social and cultural requirements and regional

and local characteristics

Priorities (Society)

Economical use of space

Strongest shoulders heaviest loads

Efficient

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Favourable Conservation Status

Calibration model

Integrates science and society

extra area for habitats is assigned to SCI to reach FCS

ecological preconditions

range, area, quality ~ patch size and typical species

spatial distribution over Flanders takes into account

socio-economical requirements from various sectors:

agriculture, industry, private and nature conservation

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Favourable Conservation Status

0 10 20 30 405Kilometers

BRU

ANT

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Favourable Conservation Status

Grey: sites of community importance

Yellow: actual area European dry heaths

Red: additional area European dry heaths

meeting the ecological preconditions and taking into account of socio-economical requirements

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Support of science in decision making

Conservation Measures

Restoration trajectories

Management measures

Population recovery

Reintroduction schemes

Optimal environmental levels

Conservation Measures

Cost-efficiency

Manual for nature

management

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Conservation Measures

Cost-efficiency (Society)

Financial cost

Sustainable

Public acceptance

Development time

Manual for nature management

Managers can choose among field measures to reach ‘high-quality’ habitat (Van Uytvanck & De Blust 2012)

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Support of science in decision making

Monitoring Conservation Status

Delineation of sites for habitats

and species (Art. 4)

standard data forms (listing

and conservation value)

appropriate assessment

(plans/projects)

Art. 17 reporting

conservation status on

biogeographical level of

member states

range

area

structure & functions incl.

typical species

future prospects

natura 2000 network

Monitoring Conservation

Status

Participation & leanness

Data gathering agreement

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Monitoring Conservation Status

Statistically sound

Varying recording cycle (6 or 12 years)

Power of detecting trends (10 or 15 %)

Indicators (versus binary assessment)

Ecological knowledge

Favourable Conservation Status

Biotic proxies (versus abiotic measurements)

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Monitoring Conservation Status

European dry heaths Triturus cristatus

Regional assessment

Area (12 year cycle) total surface-coverage mapping of all known locations (in- and outside SCI) x

registration of new habitat during nature construction / compensation projects x

registration of new habitat after succesful nature management x

Populations registration of new locations through volunteer network (waarnemingen.be) x

Quality sample oriented monitoring using the Local conservation status tables 14 / year (12 year cycle) 40 / year (6 year cycle)

SCI assessment

Area (12 year cycle) x

Populations x

Quality only on an extensive scale x x

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Monitoring Conservation Status

Participation & Leanness (Society)

Public support

Cost reduction (only what is required and use of cheaper proxies)

Maximal coupling with other monitoring schemes

water framework directive (European legislation)

monitoring of nature reserves (Flemish legislation)

Data gathering agreement

NGOs (different sectors)

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Thank you!

Information

www.inbo.be

[email protected]

Questions

Gerald Louette

Dries Adriaens

Desiré Paelinckx