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Application of the Classification System
The ability to apply conservation ranks to vegetation units is
integral to the success of the classification system as a tool in biodiversity
conservation. Associations are ranked by their relative endangerment to
determine their relative conservation priority. These ranks are based on factors
such as present geographic extent, threats, number of distinct occurrences,
degree of decline from historic extent, and degree of alteration of natural
processes affecting the dynamics, composition, or function of the type. Ranks
are customarily assigned by the various members of the Natural Heritage Programs
and of the national, regional, and state offices of The Nature Conservancy. For
a given community type, ranks are assigned at three declining hierarchical
levels of geography, from global or rangewide (the Global Rank or GRANK),
through national or country (the National Rank or NRANK), to state, province, or
other subnational unit (the State Rank or SRANK).
Imperiled community types (and species), those ranked G1 through
G3, are often regarded as the principal targets for conservation action,
although the Conservancy is dedicated to the conservation of all native
community types. Special attention is generally given to taxa of high
endangerment, as opportunities for their conservation may be limited in space
and time. However, some highly ranked community types may be essentially secure
because of their occurrence in areas that are remote from human alteration, that
already have high degrees of protection, or that are unsuitable as human
habitat. Others are essentially secure because of their intrinsic resistance to
alteration or degradation. The conservation status of highly ranked communities
should be assessed and steps should be taken to ensure their adequate
protection.
More common and less imperiled community types, those ranked G4
and G5, are also conservation priorities. In most parts of the world, these more
common community types have generally been highly altered and degraded by human
action, and have often also been fragmented and their functioning impaired. For
the conservation of many rare and common species, these relatively secure
communities are of critical importance. In eastern North America, a large tract
of a common forest type in pristine condition that occurs in an essentially
intact landscape with relatively intact ecological processes is of high priority
for conservation. Though the type itself is common, large, high quality examples
are rare and the opportunity to conserve such an example may be very limited.
Generally, the conservation of lower ranked community types should be focused on examples in especially good
condition, of large extent, with high landscape integrity/connectivity, and with
ancillary conservation benefits.
Because a primary purpose of the National Vegetation
Classification is to help set conservation priorities for natural community
types, the recognition and naming of units reflects their relative naturalness.
There generally exists a strong correlation between naturalness and conservation
priority.
The dynamic nature of vegetation presents some additional
complications in the evaluation of the naturalness and conservation priority of
community units. Early- and mid-seral vegetation may be readily classifiable as
distinct in composition and physiognomy from later seral vegetation, but may be
transient on the landscape. Transience makes this vegetation difficult to
"track" and the conservation of seral sequences will generally be dependent on
the conservation of large landscapes that contain a mosaic of seral stages.
Also, disturbances cannot be clearly and cleanly classified as
"natural" or "anthropogenic". Some anthropogenic disturbances are similar enough
to natural disturbances that the resulting successional communities cannot be
clearly distinguished, while others may create unique and unprecedented
communities that do not occur in the natural landscape.
We therefore have developed categories and a resulting ranking
system for communities that go beyond those used for species conservation. The
various ranks used for communities presented in this document are listed and
briefly described below.
G1 - Critically imperiled globally;
G2 - Imperiled globally;
G3 - Rare or uncommon;
G4 - Widespread, abundant, and apparently secure, but with cause
for long-term concern;
G5 - Demonstrably widespread, abundant, and secure;
G? - Unranked;
GH - Historic;
GX - Extinct;
GC - Planted/cultivated vegetation;
GW - Ruderal vegetation, or vegetation dominated by invasive
alien species;
GM - Vegetation resulting from the management or modification of
natural vegetation, it is readily restorable by management or time, and/or the
restoration of ecological processes.
Title: Classification of Vegetation Communities of Maryland
Classification of Vegetation
Communities of Maryland: First Iteration
A Subset of the International Classification of Ecological
Communities: Terrestrial Vegetation of the United States
March 2004
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