369
To do so an extensive relation study has to
be made of the succession in different
locations. To analyse the relations between
the changes of any one site with its spa
tial characteristics the use of a Geograp
hic Information System will be indispensab
le. The most important factors to examine
are:
* distance to sea (salt spray, windvelo-
city) * age of the landscape (soil proper
ties) * groundwaterlevel (xero-, hygrosere
succession) * vegetation in surrounding
sites * human an animal interference
In the study area a further rise of the
groundwatertable is expected in the next 10
to 20 years. Probably groundwater will
influence the succession in the dune
slacks. Without human interference this
will stimulate the growth of the woody
species. Dense and tall shrub and woodland
will increase even more. Loss of the youn
ger succession stages has to be feared.
Réintroduction of livestock and activation
of blowouts may be used as managment tools
to restore the characteristics of the youn
ger dunes.
6 CONCLUSIONS
The the time interval between the sets of
photographs fit in with the rates of chan
ges in the structure of vegetation.
Aerial photographes give sufficient infor
mation in landscape transitions and can be
very useful to develope an adequate dune
management. In dune areas landscape succes
sion is a relatively fast process. A dune
manager should harmonize his way of acting
to this process.
Analysis and classification has to be done
in a systematic way. The great advantage of
using a determination key is that:
* interpretation is done systematically
* all photos are handled in the same way
* and all maps get the same legend.
For the case study area the conclusion is
that:
Diversity in vegetation structure increa
sed. Moss/herb/grass vegetations were rep
laced by shrub and woody vegetations. The
landscape changed by this bush encroachment
and became more and more fixated. . If the
succession in the Haasvelderduinen conti
nues loss of the open moss and grass vege
tation , younger succession stages and
geomorphological processes has to be fea
red.
To prevent this loss and to restore dune
forming processes, (belonging to the grey
dune area) succession has to be retarded.
Cattle and sheep grazing and the activation
of blowouts maybe used as managment tools
to reintroduce the characteristics of the
younger dunes.
ACKNOWLEDGEMENTS
The author is very grateful to dr. G Bae-
yens, ing. J.Duyve dr. P. Ketner and ir. A.
Ehrenburg for their assistance in this
research.
REFERENCES
Dorp, D. van , R. Boot & E. van der Maarel,
1985. Vegetation succession on the dunes
near Oostvoome, The Netherlands, since
1934, interpreted from airphotographes and
vegetation maps. Vegetatio,58 : 123-136.
Ehrenburg ,A. & L.H.W.T. Geelen, 1986. De
ontwikkeling van de vegetatiestructuur in
de Haasvelderduinen in de periode 1931-
1985. Gemeentewaterleidingen Amsterdam.
Gevers van Endegeest, D.T., 1826. Verhande-
ling over het toegangbaar maken van de
duinvalleien langs de kust van Holland.
Maatschappij ter bevordering van de land-
bouw, Amsterdam.
Meulen,F. van der & P.D. Jungerius, 1989.
The decision enviroment of dynamic dune
managment.In: F. van der Meulen et.al.
(eds.), Perspectives in coastal dune manag
ment. SPB Academic Publishing bv, Den Haag,
pp 133-140.
Tansley,A.G., 1946. Introduction to Plant
Ecology. London.
Zonneveld,I.S., 1974. Land evaluation and
Land(scape) science. ITC textbook VII.4,
Enschede, pp 133.