Full text: Resource and environmental monitoring

ımber 
UMZs 
  
  
  
for 
a of 
mber 
ause 
t-up 
1984 
reas 
that 
one 
logy 
mask 
l as 
from 
an 
1991 
by 
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mask 
ges. 
many 
the 
be 
mall 
1 to 
of 
1995 
s in 
ngle 
1984 
tant 
Chil] 
e UMZs existent in Lisboa and Oeiras do 
not show a great difference from 1984 to 
1995. Notice however that, this does not 
mean that there was not a change on the 
areas occupied by built-up cover, since 
the UMZ also includes non-built-up areas 
that are within the same UMZ; 
e Loures and Sintra experienced a large 
change in the county area covered by 
UMZs. In these counties individual UMZs 
that were close to the LUMZ connected 
themselves to the LUMZ. On the other 
hand, in the North part of these 
counties many built-up areas that were 
in different and small contiguous 1984 
UMZs are in a single, and larger, 1995 
UMZ, which results from the aggregation 
of the 1984 scattered UMZs; 
e Amadora and V.F. de Xira experienced a 
small expansion of the UMZs, and Cascais 
experienced a moderate increase of the 
UMZs. 
5. CONCLUSIONS 
In this study we presented a methodology 
for the delimitation of UMZs (as defined by 
EUROSTAT) by using satellite data and 
methodologies based on automatic 
procedures. First, EO and ancillary data 
were used to generate a landuse map. Then, 
the built-up areas were identified and an 
algorithm to identify the UMZs based on the 
principle of continuity was developed and 
applied to two dates (1984 and 1995) for 
the Área da Grande Lisboa (AGL). 
An analysis of the UMZs for the two dates 
reveals a significant increase of the 
built-up areas in AGL from 1984 to 1995. 
This expansion of the built-up area was 
mainly done by expansion of existent UMZs 
rather than on new UMZs. 
AKNOWLEDGEMENTS 
This study was partially supported by 
EUROSTAT, Programme Teledetection et 
Statistics (Contract RS/12/031/MF/SW). 
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Contextual correction: 
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