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Dry heathlands and sandy open grasslands in a suburban environment in the south of Brussels (Belgium) : Assessment of the conservation status

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Academic year: 2021

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Dry

Dry heathlands

heathlands and sandy open grasslands in a suburban

and sandy open grasslands in a suburban

environment in the south of Brussels (Belgium)

environment in the south of Brussels (Belgium)

Assessment of the conservation status

Assessment of the conservation status

TAYMANS Julien & MAHY Grégory

Gembloux Agricultural University Laboratory of Ecology Passage des Déportés, 2 5030 Gembloux – Belgium -Email : taymans.j@fsagx.ac.be

Study area :

• The upstream Dyle hydrographic subbasin (43.000 ha), located in Brabant phytogeographic district This region is characterized by a high diversity of local ecological conditions due to the alternance of important tertiary sand outcrops and quaternary silty layers.

A worrying concern :

• Loss of open semi-natural habitats, in particular dry heathlands, sandy grasslands and grassheaths (further called “heathlands”) due to:

• Abandonment of former agro-sylvo-pastoral activities, causing a natural afforestation towards the climactic forest, and plantation of Pinus sylvestris orchards during the 19thcentury;

• Urbanisation caused by the proximity of Brussels (~25 km) during the 20thcentury.

Introduction

Methods :

• Digitization of heathlands patches of historical maps (1770);

• Exhaustive survey of all ancient heathland patches to determine current affectation and digitization of all current heathland patches.

Evolution of heathlands distribution

Research questions What was the evolution of heathlands distribution from 1770 to the present? What is the current conservation status of heathlands in the study area?

What is the variation of local plant communities within the studied semi-natural habitats?

Current affectation of ancient heathlands (1770)

Number of patches Area (ha)

Proportion of the total area (%)

Urbanisation 58 852,6 58,39

Pinus sylvestris orchard 26 291,6 19,97

Broad-leaved orchard 12 81,5 5,58 Natural afforestation 8 68,9 4,72 Meadow 6 65,2 4,47 Cropland 6 62,5 4,28 Roadway 1 23,3 1,6 Sand quarry 2 14,6 1 Total 119 1460,2 100

current affectation and digitization of all current heathland patches.

Results : dramatic reduction (95%) of heathlands area between

1770 and 2006 in the study area (see tables), mainly caused by urbanization.

Evolution of heathlands area from 1770 to 2006 1460 72 0 200 400 600 800 1000 1200 1400 1600 1770 2006 Date H e a tl a n d a re a ( h a ) -95% Phytosociological characterization Methods :

• 144 vegetation relevés (9m²) using B.B. method; • Directed sampling in representative areas; • Twinspan classification

Results :

• 241 vascular plant species;

• 19 vegetation facies varying in species composition and having their own indicator species

high diversity at the community level Current conservation status

of heathlands in the study area Methods :

• Exhaustive survey of sand outcrops (192 sites analysed - ~737 ha) aiming at:

• Drawing up a floristic list for each of them; • Assessing colonization by shrubs and trees;

• Assessing abundance of structural heathland species (Calluna

vulgaris, Vaccinium myrtillus, Molinia caerulea, Pteridium aquilinum, Deschampsia flexuosa and Cytisus scoparius).

Results :

• 393 vascular plant species observed;

• 30 plant species of high conservation value at the regional scale; • Regional extinction of 4 dry heathlands typical species since 1956 :

Lycopodium clavatum, Genista pilosa, G. anglica and Cuscuta epithymum;

• Invasion of heathlands by social grasses, shrubs and trees, and (exotic) invasive species (10 sp.), in particular Prunus serotina (70% of sites were invaded), Robinia pseudoacacia (15%) and Amelanchier

lamarckii (7%);

• Remaining heathlands (72 ha) are threatened by spontaneous afforestation and urbanization.

Generalized ageing and encroachment since the middle of the

20thcentury = rather bad conservation status

Perspectives • A plan of restoration priorities has been established for the study area and management measures

have been proposed.

• The potential for heathlands restoration is c. 360 hectares, in which c. 40 hectares should be restored in priority.

Picture 1 : Restored dry heathland,

grazed by rustic sheep

Picture 2 : Sandy open grassland, included

in a heathlands complex

Evolution of heathlands from

1770 to 2006 1770 2006

Total area of heathland (ha) 1460 72

Number of patches 119 66

Mean size of patches (ha) (+/- s.d.) 12,3 (14,0) 1,1 (1,6) Size of the largest patch (ha) 82,7 8,6

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