
Policy on Monterey Pine Forest
Adopted March 1995
Policy Statement
Because of habitat fragmentation and other cumulative impacts
to Monterey Pine Forests, CNPS recommends that there should be
no further removal of healthy, non-hazardous native Monterey
Pine trees, except for minimal removal on existing lots of
record and to meet fire safety requirements. Preservation
efforts should be concentrated on stands 20 acres or larger and
contiguous stands of smaller acreages that provide wildlife
corridors, habitat connectivity, or occupy rare terrace soils.
Fire resistant construction should be required for homes located
in and near Monterey Pine Forests.
In landscaping, reforestation and/or mitigation projects,
replanting of native Monterey Pine Forest habitat with trees
grown from locally-collected seeds, preferably from trees
uninfected with pitch canker, should be encouraged. Special care
should be taken to avoid contamination of seedlings with pitch
canker. Monterey Pines propagated from non-native genetic stock
should be replaced when they occur near native forests. In some
cases where Monterey Pine Forest stands are not regenerating,
management techniques that encourage natural seedling
establishment and forest rejuvenation should be considered. This
includes prescribed fire where appropriate. As new information
is developed, additional management techniques may be
identified.
While breeding programs for resistant strains will be a part
of the response to the pitch canker threat, the primary emphasis
of action should be on maintaining the maximum appropriate
natural genetic and ecological diversity in the native forest
habitat.
CNPS recommends that all remaining natural stands of Monterey
Pine Forest be incorporated into an effective regional forest
conservation plan, with specific criteria for identifying areas
essential to maintain the full complement of genetic and
floristic diversity. The plan should propose a strategy,
alternatives and a timeline for achieving permanent protection
of the Monterey Pine Forest.
Background
Native Monterey Pine Forest provides the scenic backdrop
highlighting the distinctive character and ambience of the
Monterey Peninsula, Cambria, and Swanton-Ano Nuevo areas. These
three Monterey Pine Forest areas are relicts of the Pleistocene
coastal coniferous forest that supported Monterey Pine from
modern Marin County in the north to Riverside County in the
south.
In 1994, CNPS considered the native Monterey Pine to be Rare
and Endangered (List 1B) because this forest type is naturally
confined to these three small areas on the central California
coast and two small Mexican islands. Throughout its natural
range, Monterey Pine Forest is subject to increased threats from
clearing, fragmentation, feral animals, and disease. Monterey
Pine is also on the California Department of Fish and Game
Special Plant List and is a federal candidate for endangered
species listing and protection.
A recent study finds that the native Monterey Pine Forest on
the Monterey Peninsula is grouped into distinct community
sub-types based on soil and geomorphic surfaces. Further, pine
forest sub-types found on the six granitic marine terraces in
the Del Monte Forest area differ from the pine forest sub-types
found on sandstone and shale terraces of Jacks Peak. Subtypes
are also expected to exist in Cambria and Swanton-Ano Nuevo. The
natural stands of Monterey Pine Forest form plant and animal
ensembles found nowhere else on Earth. For example, Del Monte
Forest supports 10 rare and endangered plant species.
Monterey Pines propagated from nursery stock of unknown
origin have been widely planted in and near the native Monterey
Pine populations. If these introduced trees hybridize with
native Monterey Pines, the offspring may lack genetic traits
necessary to adapt to changing conditions.
Pitch canker, a fungal disease introduced to California in
1986, has been spreading rapidly throughout the central coast.
Pitch canker has infected planted stands of Monterey Pine, as
well as native trees on the margins of developed areas.
Preliminary research suggests that between 5 and 15 percent of
the pines in the affected stands are resistant to the disease.
Trees weakened by pitch canker are susceptible to fatal attacks
by a variety of beetles for which there is no practical control.
Foresters and scientists have recommended funding a breeding
program to develop trees that are resistant to pitch canker;
this may result in the loss of genetic diversity among native
stands that support trees resistant to pitch canker and other
pathogens. Some authorities have recommended that there should
be no further extensive planting of Monterey Pines in order to
limit the spread of pitch canker; but unless native forests can
be restocked to balance tree removal and mortality, the
long-term survival of the forest may be threatened. Experts
agree that the largest possible stands of native trees should be
preserved as a buffer to pitch canker and a reservoir of
potential resistance.
Recent fire protection proposals have recommended that the
"defensible space" around dwellings be expanded to
150' in Monterey Pine Forest areas. This proposal threatens to
result in the removal of large numbers of Monterey Pines and the
increase of "edge effect" on remaining trees, thus
exacerbating the disease hazard. Such proposals may be
inconsistent with Local Coastal Plans and county ordinances, as
well as with the fire hazard rating of Monterey Pine Forest
habitat. Although the Monterey Pine is a closed-cone species
with a reproductive strategy that benefits from fire or hot
temperature, the existence of fog in its habitat during much of
the fire season reduces the actual danger of fire occurring.
The preservation of the full genetic heritage of the Monterey
Pine Forest is a matter of global concern. Monterey Pine is the
most widely planted timber tree in the world and could provide a
source of wood that reduces logging pressure and potential
extinction trends in tropical rainforests. In tree plantation
settings, cultivated Monterey Pines selected for rapid growth,
straight trunks and maximum height, may not have critical
genetic traits and disease resistance that could be provided
from breeding with native stock.
(Most of the information on which this policy is based
appeared in the January 1995 Fremontia. For documentation
of issues not covered in the January 1995 Fremontia,
contact the Monterey Bay
Chapter of CNPS.)

|