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Representatives
from each Canadian biosphere reserve attended a workshop to explore
and develop landscape change detection methods. Experts in this
field provided training to workshop attendees.
Landscape change information (what has been done and
what was needed) was assessed for each participating biosphere reserve.
Projects were undertaken based on local objectives and resources.
The Niagara Escarpment Biosphere Reserve synthesized land use and
land cover change information for the Escarpment and identified
linkages at different scales of analysis (regional, area and site
level). The term "land use" was used to describe the alterations
made to the landscape by humans, while "land cover" referred
to types of naturally occurring vegetation.
Regional Level
Classified satellite imagery from 1976 and 1995 were
compared to examine changes in land use along the southern portion
of the Escarpment (Niagara to Peel Region). The most drastic change
was an increase in recreational areas (e.g. golf courses) from 0.7%
to 1.8%.
Forest cover in the study area slightly increased over the 20 year
period (from 43% to 44%). The 1995 forests were likely composed
of the original (1976) forests and areas where trees matured from
early successional stages. However, forest fragmentation analysis
showed that the landscape in 1995 consisted of more numerous, smaller
patches with a greater variability in size compared to 1976. The
amount of interior habitat (i.e. forest >100m from the nearest
edge) decreased over the 20 year period from 52% of the study area
to 39%. This decline may represent one of the most serious threats
affecting forest interior-dependent bird species.
Area Level
Area level analysis provides a more detailed view of the
landscape than at a regional scale. For example, forests can be
broken down into physiognomic classes (deciduous, coniferous, or
mixed) and the connectivity of forests can be examined. Area level
analysis is directed at monitoring the cumulative effects of land
use change i.e. the sum of human impacts within a defined area
over time.
Cumulative
effects monitoring of landscape conditions was conducted for the
northern portion of the Halton Region. Aerial photographs dating
1974 and 1994 were the primary tool for classifying the landscape.
GIS was used to generate two final maps: one where landscape
change within the study area resulted in positive cumulative
effects; and the other showing negative cumulative effects. An
example of a positive cumulative effect is increased habitat for
forest interior bird species. The conversion of a forest stand to
farmland is an example of a negative cumulative effect.
The results showed that most areas with negative
cumulative effects in north Halton were associated with habitat
fragmentation, isolation and loss due to resource extraction along
the Escarpment brow. Areas of positive cumulative effects
(increased connectivity between forests, increased forest interior
habitat) occurred in small, isolated areas, most of which were
farms or resource extraction areas that were abandoned between
1974 and 1994 and left to regenerate.
Site Level
Site level analysis addresses threats or targets
stress areas identified at the regional and area levels of
analysis. This "micro" scale of analysis can answer
specific monitoring questions identified at broader scales.
Investigations at the site level (within
the Hilton Falls Conservation Area in the Halton Region) focused
on two integrated research areas:
- a detailed
inventory of a 1 hectare plot to examine long-term changes in
forest biodiversity and dynamics
- forest bird
productivity monitoring to examine breeding success of Wood
Thrush in different sized forests
Summary
of Integrated Analysis
Regional level analysis provides a broad overview
of historic and existing land use and land cover patterns. This
includes establishing a baseline of information and examining
landscape change.
Locations for area level analysis are selected based on
where significant landscape change has been identified at the
regional level. Land use and land cover classifications
established at the regional level can also be confirmed at the
area level.
The identification of stresses / threats at the area level
of analysis guides the location of intensive monitoring plots to
assess the effects of development. The selection of sites to
monitor the breeding success of forest interior-dependent bird
species can also be based on area level information.
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