Landscape
Landscape
fragmentation
fragmentation
due
due
to
to
transportation
transportation
infrastructure
infrastructure
and urban
and urban
development
development
Dr. Jochen Jaeger Dr. Jochen Jaeger
ETH
ETH ZurichZurich, , SwitzerlandSwitzerland, May 2004, May 2004
20 years later:
Motorway intersection „Singen“ in 1988
Baden-Wurttemberg
(Jaeger et al. 2001)
How much has the degree of landscape fragmentation
increased?
How can the
consequences be assessed?
Black Forest
Structure of this talk
Structure of this talk
Measuring landscape fragmentation
Measuring landscape fragmentation
Effective mesh sizeEffective mesh size
Time seriesTime series
Use as environmental indicatorUse as environmental indicator
Effects of roads on animal populations
Effects of roads on animal populations
Road-Road-density thresholddensity threshold
Suitability of fencingSuitability of fencing
How to measure the degree of
How to measure the degree of
landscape fragmentation
landscape fragmentation
9 suitability criteria9 suitability criteria
Serious problems with existing landscape indicesSerious problems with existing landscape indices
New measure: New measure: effective mesh sizeeffective mesh size,, mmeffeff
Based on the probability that two randomly chosen Based on the probability that two randomly chosen
points can be connected: points can be connected:
mmeffeff now available in Fnow available in FRAGSTATSRAGSTATS (on the www)(on the www)
Jaeger (2000),
Spatial
Spatial
comparisons
comparisons
m
m
effeffin the
in the
44 rural districts
44 rural districts
in Baden
in Baden
-
-W
W
urttemberg
urttemberg
Jaeger et al. (2001) Jaeger et al. (2001) 30.26 24.61 24.60 18.65 17.26 15.91 15.48 14.80 14.16 13.05 12.17 11.61 10.25 10.22 8.98 8.87 8.83 8.69 8.18 8.09 7.96 7.78 7.46 7.25 7.24 7.13 7.11 6.89 6.63 6.21 6.17 5.51 5.42 5.01 4.96 4.62 4.29 3.82 2.68 2.55 2.37 2.31 1.74 1.63 0.00 5.00 10.00 15.00 20.00 25.00 30.00 35.00 Ortenaukreis Emmendingen Freudenstadt Breisgau-Hochschw. Rastatt Reutlingen Zollernalbkreis Tübingen Calw Baden-Baden Lörrach Tuttlingen Schwarzwald-Baar-Kreis Heidenheim Alb-Donau-Kreis Ostalbkreis Waldshut Main-Tauber-Kreis Rottweil Neckar-Odenwald-Kreis Göppingen Freiburg i. B., St. Böblingen Karlsruhe Esslingen Biberach Sigmaringen Heilbronn Rhein-Neckar-Kreis Rems-Murr-Kreis Ravensburg Schwäbisch Hall Enzkreis Hohenlohekreis Konstanz Heidelberg, Stadt Ludwigsburg Bodenseekreis Heilbronn, Stadt Pforzheim Karlsruhe, Stadt Ulm Mannheim Stuttgart km2Landscape change: Time series
Landscape change: Time series
Used as indicator (impact on biodiversity) in the Used as indicator (impact on biodiversity) in the
Environmental Report of Baden
Environmental Report of Baden--WuWurttemberg (2003)rttemberg (2003)
0 10 20 30 1920 1940 1960 1980 2000 2020 Year meff [km2] Year Baden-Wurttemberg 1930 1940 1950 1966 1977 1989 1998 0.00 2.00 4.00 6.00 8.00 10.00 12.00 P L U K B R H Pforzheim Ludwigsburg Ulm Konstanz Bodenseekreis Ravensburg Hohenlohekreis meff [km2]
Useful for m
Useful for measurementseasurements and
and assessmentsassessments::
Results published in:
Results published in:
Jaeger, J. 2002: Jaeger, J. 2002: Landschaftszerschneidung Landschaftszerschneidung. . Ulmer, Stuttgart. Ulmer, Stuttgart.
(English translation in planning)
(English translation in planning)
time time seriesseries ((environmentalenvironmental
indicator
indicator))
settingsetting environmentalenvironmental
standards
standards
managementmanagement and and regulationregulation
for
m
m
effeffcurrently used in
currently used in
5 states of Germany:5 states of Germany:
BadenBaden--WuWurttemberg,rttemberg,
HesseHesse, ,
Bavaria,Bavaria,
ThuThuringiaringia,,
SchleswigSchleswig--Holstein.Holstein.
Ongoing discussion about using it in all states of Ongoing discussion about using it in all states of
Germany as one of 24 core indicators of Germany as one of 24 core indicators of
sustainability. sustainability.
European Environmental Agency (EEA)European Environmental Agency (EEA)
0.00 2500.00 5000.00 7500.00 10000.00 B elgium Denmark Netherlands Luxembo urg Germany Czech Republic Hugary Slo venia A ustria Cro atia P o rtugal Switzerland Slo vakia France B ulgaria Ireland P o land United Kingdo m Yugo slavia Spain Italy B o snia and Herzego wina M acedo nia Ro mania Greece A lbania Latvia No rway Lithuania Sweden Esto nia Finland Collaboration Collaboration with the with the European European Environmental Environmental Agency (EEA) Agency (EEA)
since Nov. 2003since Nov. 2003
32 European 32 European
countries countries
Jaeger et al.,
Jaeger et al., in prepin prep..
Effects of roads and railroads
Effects of roads and railroads
Road Road EcologyEcology: an : an
emerging
emerging newnew and and relevant
relevant disciplinediscipline
Road Road EcologyEcology isis
“
“thethe sleepingsleeping giantgiant of of conservation
conservation biologybiology““ (Forman 2002)
(Forman 2002)
Buch
Buch Forman et al. (2003) Forman et al. (2003) scannen
scannen hierhier
Reduced Population Persistence Reduced Population Size
Roads and Traffic
Habitat Loss Traffic Mortality
R.I.P.
Road Avoidance
Population Subdivision
Increasing road density
Increasing road density
…
…
…
…reduces probability of population persistence: reduces probability of population persistence: Linearly or with a threshold?
Linearly or with a threshold?
. . .
The
The
road
road
density
density
threshold
threshold
0 0.2 0.4 0.6 0.8 1 0 2 4 6 8 10 12 Number of roads Probability of population persistence
Jaeger, J., Fahrig, L., Ewald, K., in prep.
Behavior at the road
Behavior at the road
road avoidance
road avoidance = animals don= animals don’’t try to crosst try to cross traffic mortality
traffic mortality = percent of animals killed on the road= percent of animals killed on the road
proportion of animals avoiding the road
proportion of animals killed 100% proportion of succeeding animals 1- R R 1- K K road
Spatially explicit individual
Spatially explicit individual
-
-based simulation model
based simulation model
0 0.2 0.4 0.6 0.8 1 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 Pers. prob. traffic mortality road avoidance Persistence probability effect of a fence
0 0.2 0.4 0.6 0.8 1 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 Pers. prob. traffic mortality road avoidance Persistence probability
0 0.2 0.4 0.6 0.8 10 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 traffic mortality road avoidance
When do fences enhance population survival?
fence reduces survival
fence enhances survival
Fence
Fence threshold line
Jaeger and Fahrig (2004),
Future research questions
Future research questions
Bundling of roads Bundling of roads
Relative importance of road configuration and Relative importance of road configuration and
road length road length
Response times to new roadsResponse times to new roads
Landscape connectivityLandscape connectivity
Effect of different matrix typesEffect of different matrix types
Time series of landscape fragmentation in Time series of landscape fragmentation in
Switzerland Switzerland
Comparison with Comparison with metapopulationmetapopulation modelsmodels
Empirical dataEmpirical data
Collaboration
Collaboration
L. L. FahrigFahrig, Carleton University, Ottawa, ON, Canada, Carleton University, Ottawa, ON, Canada
A. ClevengerA. Clevenger, Montana State Univ., USA, Montana State Univ., USA
A. SeilerA. Seiler, Univ. of Uppsala, Sweden, Univ. of Uppsala, Sweden
S. S. KleeschulteKleeschulte, EEA, Univ. , EEA, Univ. AutonAuton. de Barcelona, Spain. de Barcelona, Spain
K. FrankK. Frank, UFZ Leipzig, Germany, UFZ Leipzig, Germany
H.H.--G. SchwarzG. Schwarz--von von RaumerRaumer, Univ. of Stuttgart, Germany, Univ. of Stuttgart, Germany
R. R. SerrouyaSerrouya, , KokaneeKokanee ForestForest ConsultingConsulting, , BC, CanadaBC, Canada
S. AlexanderS. Alexander, Univ. of Calgary, AB, Canada, Univ. of Calgary, AB, Canada
M. PercyM. Percy, Banff National Park, BC, Canada, Banff National Park, BC, Canada
Summary
Summary
Monitoring landscape fragmentation Monitoring landscape fragmentation
(as environmental indicator) (as environmental indicator)
Effects of roads: Thresholds in Effects of roads: Thresholds in
response to road density and response to road density and
suitability of fences suitability of fences
IndividualIndividual--based based
population models population models