Gulf of Maine Projects
1996 Coastal Habitat Restoration Report
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Tidal Marshes
Restoration of tidal marshes may be conducted either to mitigate for
permitted impacts or to compensate and offset cumulative or historical
impacts through proactive efforts. For the 111 tidal marsh restoration
projects listed in Table 1, including both mitigation and proactive
projects, 45 involved tidal restrictions, 42 involved the removal of
fill, 19 involved the creation of tidal marsh habitat, and 35 involved
Open Marsh Water Management. Some projects may have involved more than
one type of restoration work. Compensatory mitigation and proactive
projects are very different in terms of project objectives, and, quite
often, in the type of work conducted.
Mitigation
Compensatory mitigation projects aim to compensate for unavoidable
adverse impacts through the restoration, creation, or enhancement of
natural resources. The primary goal of these projects is to replace
habitat functions and values lost during a permitted activity. These
projects are often the least cost effective, especially those that involve
habitat creation such as the conversion of an upland habitat to a tidal
wetland. For example, it cost Logan Airport in Boston over $700,000
to construct a 1.3 acre salt marsh (Louis Berger & Assoc., 1997). This
high cost reflects the high expense of permitting, planning, and construction
often involved with compensatory mitigation projects.
As Table 2 shows, many opportunities for restoration have been identified.
If restoration opportunities do not exist on-site for effective compensatory
mitigation, resources should be allocated to support projects offsite.
Mitigation banks are designed to pool money from mitigation and implement
larger and more effective restoration projects. Restoration sites selected
for mitigation banks may be located outside of the town where impacts
occurred. This makes it difficult to convince local municipalities of
the long-term ecological benefits. Information collected indicates that
few mitigation projects are tracked and evaluated on a long-term basis
and reveals the need for more rigorous tracking programs to enforce
permit compliance and to document ecological changes. Existing permit
tracking databases could be modified to include information on acres
impacted versus acres restored and a brief description of the type and
location of compensatory work. In addition, monitoring and assessment
reports need to be written in a consistent manner and their submittal
to regulatory agencies enforced.
Proactive
Proactive projects aim to restore degraded habitats to offset historical
and cumulative impacts rather than compensate for permitted activities.
These projects are becoming numerous and are often the most cost effective
(other than conservation of existing habitats) due to the types of work
involved and in-kind contributions of resources. By replacing a culvert
or installing a self-regulating tide gate, tidal marshes can be restored
at minimal cost. For example, restoring tidal flow to a 50 acre salt
marsh in Rye, New Hampshire, was completed at a cost of $40,000 (Louis
Berger & Assoc.,1997). Other projects may involve the excavation of
fill material and planting of vegetation or Open Marsh Water Management
(OMWM). OMWM aims to restore ditched and drained wetlands and control
mosquito populations. Resources need to be allocated toward initiatives
that identify and evaluate restoration opportunities, and more importantly,
toward those projects that have already been identified as having strong
restoration potential. (See Table2.)
Project Overview -- Freshwater
impoundments
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