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Focus Species Forestry - Maine Audubon

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Large Ownerships: On a typical township in the unorganized territories, Hunter’s rule<br />

would suggest that equal areas should be allocated to single tree and small group<br />

selection management (openings less than 0.25 acre), large group selection (0.25-2.5<br />

acres), patch cuts and small shelterwood cuts or clearcuts (2.5-25 acres) and large<br />

shelterwood cuts or clearcuts (25-250 acres). Within the shelterwood and clearcut<br />

categories, applying Hunter’s rule would suggest allocating equal areas to different<br />

opening sizes (e.g., the area in cuts from 25 to 75 acres should equal the area in patches<br />

from 75 to 250 acres).<br />

Small Ownerships: Create a diversity of<br />

opening sizes appropriate to the ownership.<br />

Hunter (1999) suggests that the same<br />

general allocation approach used for large<br />

ownerships can be used on small parcels,<br />

but the maximum size of even-aged units<br />

(shelterwood or clearcut) will be much<br />

smaller than on large tracts of commercial<br />

timberland.<br />

This approach to creating a diversity of patch sizes<br />

is probably best viewed as a conceptual model<br />

rather than a quantitative management<br />

prescription. It is a more aggressive approach to<br />

creating large patches than would occur under<br />

natural conditions, so should be used with caution.<br />

However, it is more conservative than much of the<br />

management seen today on industrial and investor<br />

timberlands. Individual stand conditions, landscape<br />

features, landowner objectives, and focus species<br />

habitat will take priority. Nonetheless Hunter’s<br />

rule provides a useful context for evaluating the<br />

diversity of patch sizes in the current landscape<br />

and how that diversity will be impacted by<br />

management prescriptions.<br />

Limit the Area in Single-Aged Stands<br />

If the harvests result in nearly complete overstory<br />

removal, the result will be a harvesting regime that<br />

is much more aggressive than that resulting from<br />

natural disturbance regimes. Even “stand-replacing<br />

disturbances” such as fire, wind, or spruce<br />

Habitat Management and the<br />

<strong>Maine</strong> Forest Practices Act<br />

<strong>Maine</strong>’s Forest Practices Act (FPA) limits the size<br />

of clearcuts and requires separation zones be<br />

retained that meet specified standards. Depending<br />

on the size of the clearcut, the separation zones can<br />

be harvested in approximately 10-15 years. Thus,<br />

clearcutting could be used to create large patches of<br />

early successional habitat consisting of a mosaic of<br />

stands that are separated by 10-15 years in age.<br />

Alternatively, under the FPA there is no limit on<br />

patch size that can be created with the shelterwood<br />

system. When even-aged management is used:<br />

• Whenever possible, use shelterwood harvesting<br />

instead of clearcutting.<br />

• Avoid a uniform application of similar-size<br />

harvest units evenly distributed across the<br />

landscape. See recommendations above on<br />

creating a balanced diversity of patch sizes,<br />

which will result in areas with high levels of<br />

habitat interspersion as well as a few large,<br />

relatively uniform patches.<br />

• Follow the stand-level guidelines for retaining<br />

snags, cavity trees, downed logs and patches of<br />

older forest in even-aged management areas.<br />

• Maintain travel corridors of mature forest in a<br />

landscape where shelterwood and clearcutting<br />

are used.<br />

• Maintain adequate mature forest at all times,<br />

including some areas that do not “shift” across<br />

the landscape (i.e., areas where single-tree<br />

selection, group selection, or two-aged<br />

management are used.<br />

budworm result in irregular two-aged stands. In a review of silviculture and natural disturbance<br />

regimes in <strong>Maine</strong>, Seymour et al. (2002) observe that an artificial landscape pattern exists when<br />

even-aged stands exceed 15-25% of the landscape. The shelterwood-with-reserves method (see<br />

68<br />

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

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