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Landscape Ecology Principles - River Basin Center at the University ...

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<strong>Landscape</strong> <strong>Ecology</strong> <strong>Principles</strong><br />

and How They Rel<strong>at</strong>e to Planning and Design


Wh<strong>at</strong> is <strong>Landscape</strong> <strong>Ecology</strong>?<br />

ECOLOGY<br />

The study of <strong>the</strong> interactions<br />

among organisms and <strong>the</strong>ir<br />

environment<br />

LANDSCAPE<br />

An expanse of land over which<br />

particular local ecosystems and<br />

land-uses recur<br />

LANDSCAPE ECOLOGY<br />

The ecology of landscapes


Characteristics of <strong>Landscape</strong>s (Living Systems)<br />

STRUCTURE<br />

Sp<strong>at</strong>ial p<strong>at</strong>tern of landscape<br />

elements<br />

Credit: Plan by Preston & Associ<strong>at</strong>es


Characteristics of <strong>Landscape</strong>s (Living Systems)<br />

STRUCTURE<br />

Sp<strong>at</strong>ial p<strong>at</strong>tern of landscape<br />

elements<br />

FUNCTION<br />

movement and flow of resources<br />

through <strong>the</strong> structure


Characteristics of <strong>Landscape</strong>s (Living Systems)<br />

STRUCTURE<br />

Sp<strong>at</strong>ial p<strong>at</strong>tern of landscape<br />

elements<br />

FUNCTION<br />

movement and flow of resources<br />

through <strong>the</strong> structure<br />

CHANGE<br />

Disturbance or evolution of<br />

structure and function over time


Wh<strong>at</strong> <strong>Landscape</strong> <strong>Ecology</strong> offers<br />

1. Examines how <strong>the</strong> sp<strong>at</strong>ial<br />

arrangement of land affects<br />

functions for humans, o<strong>the</strong>r life<br />

forms and abiotic processes.<br />

2. Allows us to infer something<br />

about n<strong>at</strong>ural processes and<br />

biodiversity protection, even in<br />

<strong>the</strong> absence of d<strong>at</strong>a about a<br />

specific site.<br />

3. Concepts of <strong>Landscape</strong> <strong>Ecology</strong><br />

apply to almost any site, <strong>at</strong> any<br />

scale.<br />

Perlman & Milder, 2005


Concepts of <strong>Landscape</strong> Scale<br />

GRAIN<br />

Sp<strong>at</strong>ial resolution of a study.<br />

Smaller grain = ability to<br />

distinguish smaller objects.


Concepts of <strong>Landscape</strong> Scale<br />

GRAIN<br />

Sp<strong>at</strong>ial resolution of a study.<br />

Smaller grain = ability to<br />

distinguish smaller objects.<br />

EXTENT<br />

size of <strong>the</strong> area being studied


Concepts of <strong>Landscape</strong> Scale<br />

Perlman & Milder, 2005<br />

“think globally, plan regionally, and <strong>the</strong>n act locally.” -- R.T.T. Forman


<strong>Landscape</strong> Structure<br />

PATCHES + CORRIDORS + MATRIX =<br />

MOSAIC


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Origins of P<strong>at</strong>ches:<br />

• Remnant<br />

• Introduced<br />

• Disturbance<br />

• Environmental Resources


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Origins of P<strong>at</strong>ches:<br />

• Remnant<br />

• Introduced<br />

• Disturbance<br />

• Environmental Resources


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Origins of P<strong>at</strong>ches:<br />

• Remnant<br />

• Introduced<br />

• Disturbance<br />

• Environmental Resources


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Origins of P<strong>at</strong>ches:<br />

• Remnant<br />

• Introduced<br />

• Disturbance<br />

• Environmental Resources<br />

Analyzed in terms of:<br />

•Size<br />

• Quantity<br />

• Loc<strong>at</strong>ion<br />

• Shape<br />

• Edge structure


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Origins of P<strong>at</strong>ches:<br />

• Remnant<br />

• Introduced<br />

• Disturbance<br />

• Environmental Resources<br />

Analyzed in terms of:<br />

•Size<br />

• Quantity<br />

• Loc<strong>at</strong>ion<br />

• Shape<br />

• Edge structure


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Origins of P<strong>at</strong>ches:<br />

• Remnant<br />

• Introduced<br />

• Disturbance<br />

• Environmental Resources<br />

Analyzed in terms of:<br />

•Size<br />

• Quantity<br />

• Loc<strong>at</strong>ion<br />

• Shape<br />

• Edge structure


<strong>Landscape</strong> Structure<br />

PATCHES<br />

CORRIDORS MATRIX MOSAIC<br />

Five major functions:<br />

• Habit<strong>at</strong><br />

• Conduit<br />

• Filter / Barrier<br />

• Source<br />

•Sink<br />

Credit: Sketch from Yaro, 1988


<strong>Landscape</strong> Structure<br />

PATCHES<br />

CORRIDORS MATRIX MOSAIC<br />

Five major functions:<br />

• Habit<strong>at</strong><br />

• Conduit<br />

• Filter / Barrier<br />

• Source<br />

•Sink


<strong>Landscape</strong> Structure<br />

PATCHES<br />

CORRIDORS MATRIX MOSAIC<br />

Five major functions:<br />

• Habit<strong>at</strong><br />

• Conduit<br />

• Filter / Barrier<br />

• Source<br />

•Sink<br />

Analyzed in terms of:<br />

• Width<br />

• Connectivity<br />

Credit: Sketch from Yaro, 1988


<strong>Landscape</strong> Structure<br />

PATCHES<br />

CORRIDORS MATRIX MOSAIC<br />

Five major functions:<br />

• Habit<strong>at</strong><br />

• Conduit<br />

• Filter / Barrier<br />

• Source<br />

•Sink<br />

Analyzed in terms of:<br />

• Width<br />

• Connectivity


<strong>Landscape</strong> Structure<br />

PATCHES<br />

CORRIDORS MATRIX MOSAIC<br />

Five major functions:<br />

• Habit<strong>at</strong><br />

• Conduit<br />

• Filter / Barrier<br />

• Source<br />

•Sink<br />

Analyzed in terms of:<br />

• Width<br />

• Connectivity


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Simply,<br />

The dominant context of <strong>the</strong> landscape.<br />

Credit: Sketch from Yaro, 1988


<strong>Landscape</strong> Structure<br />

PATCHES CORRIDORS MATRIX MOSAIC<br />

Simply,<br />

The dominant context of <strong>the</strong> landscape.<br />

Wh<strong>at</strong> is identified as <strong>the</strong> m<strong>at</strong>rix<br />

depends on <strong>the</strong> extent of <strong>the</strong> landscape<br />

th<strong>at</strong> is being analyzed.<br />

Credit: Sketch from Yaro, 1988


<strong>Landscape</strong> Structure<br />

PATCHES + CORRIDORS + MATRIX =<br />

MOSAIC<br />

N<strong>at</strong>ural Mosaic based on:<br />

• Soil types<br />

• Moisture<br />

• Topography<br />

• Disturbances<br />

Key Sp<strong>at</strong>ial Processes<br />

resulting from human<br />

activity:<br />

• Dissection<br />

• Perfor<strong>at</strong>ion<br />

• Fragment<strong>at</strong>ion<br />

• Shrinkage<br />

• Attrition Credit: Sketch from Yaro, 1988<br />

Perlman & Milder, 2005


<strong>Landscape</strong> Structure<br />

PATCHES + CORRIDORS + MATRIX =<br />

MOSAIC<br />

Key Sp<strong>at</strong>ial Processes:<br />

• Fragment<strong>at</strong>ion<br />

• Dissection<br />

• Perfor<strong>at</strong>ion<br />

• Shrinkage<br />

• Attrition<br />

Analyzed in terms of:<br />

• Scale<br />

• P<strong>at</strong>tern / Connectivity<br />

The gre<strong>at</strong>est impact to sensitive n<strong>at</strong>ive species<br />

occurs early in <strong>the</strong> land transform<strong>at</strong>ion process<br />

Dispersed development is almost always more<br />

detrimental to n<strong>at</strong>ural communities than a<br />

comparable amount of concentr<strong>at</strong>ed development.<br />

Perlman & Milder, 2005


<strong>Landscape</strong> Function<br />

Flow of Resources:<br />

• Soil / Nutrients<br />

• W<strong>at</strong>er<br />

• Species<br />

• Energy


<strong>Landscape</strong> Function<br />

Flow of Species:<br />

• provide Home Range used<br />

for day-to-day feeding and<br />

shelter<br />

• allow Migr<strong>at</strong>ion – seasonal<br />

movement from one habit<strong>at</strong> to<br />

ano<strong>the</strong>r<br />

• allow Dispersal – movement<br />

beyond typical range to allow<br />

establishment of new<br />

popul<strong>at</strong>ions<br />

Perlman & Milder, 2005


<strong>Landscape</strong> Change<br />

N<strong>at</strong>ural Disturbance:<br />

•Fire<br />

• Flood<br />

•Wind<br />

• Drought<br />

Human Activities<br />

• Construction<br />

• Management techniques<br />

• Introduction of exotic sp.<br />

Succession


<strong>Landscape</strong> Change<br />

.<br />

Succession


Applying <strong>Landscape</strong> <strong>Ecology</strong> <strong>Principles</strong><br />

Different Scales:<br />

•Region<br />

• <strong>Landscape</strong><br />

• Site


Applying <strong>Landscape</strong> <strong>Ecology</strong> <strong>Principles</strong><br />

Different Scales:<br />

•Region<br />

• <strong>Landscape</strong><br />

• Site<br />

Planning<br />

• Land Use Plans<br />

• Greenspace Acquisition Plans<br />

• Conserv<strong>at</strong>ion Plans


Applying <strong>Landscape</strong> <strong>Ecology</strong> <strong>Principles</strong><br />

1. Large n<strong>at</strong>ural p<strong>at</strong>ches.<br />

• Protect interior species<br />

• Accommod<strong>at</strong>e n<strong>at</strong>ural disturbances<br />

2. Veget<strong>at</strong>ed riparian corridors.<br />

• Essential protection for aqu<strong>at</strong>ic sp.<br />

• Important corridors for migr<strong>at</strong>ion<br />

3. Connectivity between large p<strong>at</strong>ches.<br />

• Necessary for movement, migr<strong>at</strong>ion<br />

and dispersal.<br />

4. N<strong>at</strong>ural remnants in humandomin<strong>at</strong>ed<br />

areas.<br />

• Areas of high conserv<strong>at</strong>ion value<br />

• Areas providing essential<br />

ecosystem services<br />

• Remnants of former n<strong>at</strong>ural m<strong>at</strong>rix<br />

Wh<strong>at</strong> should be preserved?<br />

“Indispensable P<strong>at</strong>terns” for Biological Conserv<strong>at</strong>ion<br />

Perlman & Milder, 2005


Applying <strong>Landscape</strong> <strong>Ecology</strong> <strong>Principles</strong><br />

Different Scales:<br />

•Region<br />

• <strong>Landscape</strong><br />

• Site<br />

Planning<br />

• Land Use Plans<br />

• Greenspace Acquisition Plans<br />

• Conserv<strong>at</strong>ion Plans<br />

Site Design<br />

•Parks<br />

• Golf Courses<br />

• Subdivisions...


Applying <strong>Landscape</strong> <strong>Ecology</strong> <strong>Principles</strong><br />

Different Scales:<br />

•Region<br />

• <strong>Landscape</strong><br />

• Site<br />

Planning<br />

• Land Use Plans<br />

• Greenspace Acquisition Plans<br />

• Conserv<strong>at</strong>ion Plans<br />

Site Design<br />

•Parks<br />

• Golf Courses<br />

• Subdivisions...

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