Title: Fragmentation in Landscape -Review
1- EEES4760/6760
- Landscape Ecology
- Jiquan chen
- Feb. 25, 2009
- Fragmentation
- Island Biogeographic Theory (IBT)
21km
50 m
1km
30 m
81 ha 69 ha 59 ha
3Case 7.2 (A) Degree of fragmentation of major
river basins of the world
47.4 A fragmentation sequence
57.8 A constellation of separate habitat patches
may be critical to the survival of individuals or
populations
67.9 Many animals require a suite of different
habitats or resources to meet life history needs
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97.13 Roads can be significant barriers to the
movement of small vertebrates and invertebrates
10EFFECTS OF FRAGMENTATION
- Landscape structure
- Patch density
- Patch size
- Inter-patch distance
- Connectivity
- Boundary length
- Interior/edge ratio
- Maximum of core (interior forest)
- Total interior
- Stepping stones
- Corridors
- Species
- Isolation
- Number of generalist
- Exotic species
- Nest predation
- Extinction rate
- Others
- Metapopulation dynamics
- Genetic inbreeding
- Size of disturbance patches
- Cumulative effects (rain, snow and flooding
effects)
11The Checkerboard Landscape
Patterns of clearcutting development under
various models(a-c) Progression of clearcutting
using the dispersed patch model in which areas
are selected for cutting so as to be distributed
regularly across the landscape shown are 25, 50,
and 75 cutover points. (e-f) Pattern of cutting
at 50 point using single, four nucleus, and
aggressive-parallel cutting systems. (Franklin
Forman 1987)
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13Creating Land Mosaics
14An old-growth patch surrounded by a long rotation
island that is cut in a programmed sequence such
( Harris 1984).
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16- Conclusions
- The number, size, and arrangement of the patches
in a mosaic created by forest managers strongly
influence the degree to which management
objectives are fulfilled. - Two recommendations are (1) reduce the emphasis
on dispersing small clearcut patches through the
forest landscape, and (2) identify and reserve
large patches of primeval forest in the landscape
for maintenances of interior and amenity values. - SLOSS debate
17What do we want to know about fragmentation?
- What are the relationships among patch area,
shape, isolation, edge, the interaction of these
factors, and various population and ecosystem? - How do various landscape elements (e.g.,
corridors, linear networks, and matrix) affect
ecosystem processes and the connectivity of
populations in fragmented landscapes? - How do pattern-process linkages function in
spatially and temporally dynamic landscapes
across the range of spatial and temporal scales? - What levels of habitat loss and fragmentation
does population viability decline drastically? - How long does it take population and ecosystem
processes to respond to physical changes in the
landscape associated with fragmentation?
18Island Biogeographic Theory
- Early interest in habitat fragmentation arose
from island biogeographic theory (MacArthur
Wilson 1963 1967).
(MacArthur and Wilson, 1963)
1919.4 fish 1982
(Preston, 1962 Nilsson et al. 1988)
2019.3 mammal 1989
21- The equilibrium model of island biogeography by
MacArthur and Wilson (1963)
22Manipulative and Mensurative Experiment- Two
Major Approaches -
- Manipulative experiment
- Physically manipulates some attribute of the
system in a controlled manner, while holding all
other attributes constant. - Mensurative experiment
- Simply observes or measures the system at
different locations or times - The treatment is the different conditions in
space or time.
23- Generally, manipulative experiments lead to
stronger inferences and therefore more reliable
knowledge than mensurative experiments. - An ideal manipulative experiment requires
- The similarity among landscape minimizes the
experimental error - The size of the landscape are functionally
relevant to the process/organism(s) under
consideration - Areal extent and configuration manipulation is
needed to assess independent and interactive of
processes - Replication and random
- Temporal and spatial controls (natural
variability) - Observing the delayed effect
24Mensurative Experiment
- Can overcome some of the important limitations
- The practical and logistical difficulties of
implementing large-scale treatment - No practical limit to the spatial or temporal
scale of the study system - Flexibility in time lag effect
- Still problems
- Additional sources of variation associated with
inconsistent and uncontrolled past perturbations - Lack in pretreatment control owing to
substituting space for time inherent
variability and autocorrelation
25Lack in
- Landscape level study
- Isolation of a process
- Extinction threshold/ time lag/ synergisms
between habitat area and configuration - Inequity in the organismal focus
- Invertebrates, reptiles, and amphibians
- Replication / poorly controlled
- Spatial information