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Focus Species Forestry - Maine Audubon

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8. Property-Wide and Landscape-Scale <strong>Forestry</strong><br />

<strong>Focus</strong> species management integrates management at both the stand and landscape scales by<br />

identifying a suite of species with different habitat requirements and territory sizes. Since some<br />

focus species like the marten and goshawk require suitable habitat conditions at the landscape<br />

scale, forest managers must consider how management of individual stands will affect the overall<br />

mix of forest age classes and types at the landscape scale. Small woodland owners cannot<br />

manage at the landscape scale, but they can manage at the overall property level, not just stand<br />

by stand, and adjust management based on surrounding<br />

landscape conditions.<br />

Stands and Landscapes<br />

Following are some basic principles of landscape-scale<br />

ecology.<br />

Habitat Loss and Fragmentation<br />

Habitat loss is the conversion of one habitat type to another,<br />

for example the conversion of mature forest to young forest,<br />

or the loss of the forest itself when it is converted to<br />

development or agriculture. Forest harvesting may result in<br />

temporary loss of mature forest, but conversion to nonforest<br />

is permanent.<br />

Habitat fragmentation occurs when a relatively large patch<br />

of habitat is cut into smaller patches. This may occur by<br />

perforation, which occurs when many smaller cuts are<br />

scattered throughout a large forest block, or when scattered<br />

A stand is a unit of forestland typically<br />

delineated on the basis of species, size,<br />

and density of trees. Most forest<br />

management maps delineate forest<br />

stands. Stands typically range in size<br />

from a few acres to several hundred<br />

acres. Stand-level management is the<br />

fundamental building block of forestry<br />

and focus species management.<br />

A landscape is a large-scale mosaic of<br />

forest stands and other non-forested<br />

community types and ecosystems such as<br />

bogs and streams. Landscapes may range<br />

in size from thousands of acres to tens of<br />

thousands of acres.<br />

homes are built in a forested area. The other end of the fragmentation spectrum is isolation,<br />

which occurs when harvesting or development results in habitat patches that are surrounded by<br />

large areas of dissimilar habitat. Studies have shown that habitat isolation is generally a greater<br />

threat than perforation, especially when the size of the remaining patch is small relative to the<br />

habitat needs of an animal.<br />

Habitat connectivity is the inverse of habitat isolation, and occurs when patches of suitable<br />

habitat are located adjacent to one another or are connected by travel corridors.<br />

Habitat loss and fragmentation typically occur together and may have a compounding effect, and<br />

scientists sometimes have a difficult time identifying which effect is the strongest.<br />

Habitat Interspersion and Large Forest Patches<br />

Habitat interspersion occurs when different habitat types occur adjacent to one another. Some<br />

animals prefer a high level of interspersion in relatively small patches. For example, the ruffed<br />

grouse does best when three age classes in 1-10-acre patches ranging from regeneration to<br />

intermediate or mature stands are interspersed in a 10-50-acre area. In contrast, American marten<br />

<strong>Focus</strong> <strong>Species</strong> <strong>Forestry</strong> 65

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