Significance of
the Resource or Issue to the park - Reduction and containment of exotic species
in nationally-important natural areas is a high priority goal of the National Park Service
(NPS Strategic Plan, 1997). Based on the overall conservation mandate specified in the
legislation creating Yellowstone National Park, preservation of native aquatic communities
has been an often reiterated management objective in the park (Statement for Management,
1991), e.g., "a principal objective is the preservation of native fish populations
and the associated aquatic life in a natural environment .... management efforts in the
future must encourage the maintenance of natural, environmentally regulated
ecosystems" (Yellowstone National Park Master Plan, 1974).
In 1994, New Zealand mud snails Potamopyrgus antipodarum were discovered in the Madison
River near the park boundary. Subsequent investigations by independent researchers have
documented a rapid spread of this exotic species to the Firehole and lower Gibbon rivers.
Similar to other invasions of aquatic nuisance species, long-term effects of this exotic
species on the indigenous invertebrate fauna are unknown; however, studies conducted on
the middle Snake river in central Idaho suggest that native molluscs may be reduced in
abundance or eliminated entirely. Although a long-term monitoring study may evolve from
information collected in the phase, our current proposal is restricted to development of
appropriate sampling techniques, and support of research needed to most efficiently assess
watershed-level impacts of this prolific invertebrate on other aquatic species.
Severity of Resource Threat, Problem, or Needs - Despite their
tiny size (1/4"), New Zealand mud snails are capable of rapid population growth.
Localized infestations in the Madison River in 1997 have approached a density of 28,000
individuals /sq. ft. Thus, these small molluscs have the potential to "cover the
stream bottom", similar to impacts observed with the Zebra Mussel in the midwestern
U.S. Preliminary baseline surveys indicate that the mudsnails may be impacting the
invertebrate community in the Madison, Firehole, and Gibbon rivers not only through
physical displacement or crowding, but also through competitive interactions such as food
availability. These streams not only support world famous recreational fisheries, but they
also historically contained an abundance of native aquatic insects that form an important
part of the aquatic food chain. Reductions in the insect species diversity or abundance
could diminish the availability of this critical food resource to fish. Mud snails are a
poor substitute for the traditional food base, yielding as little as 2% of their
nutritional value when eaten by trout. The rapid spread of the mud snail throughout the
Madison River watershed may have been assisted by human transport. Mud snails are able to
withstand dessication, a variety of temperature regimes, and are small enough that many
types of water users (anglers, swimmers, picnicers, pets) could inadvertently be the
mechanism for interbasin transfer of this nuisance species.
Problem definition and Information base - The overall goal of park
managers is to prevent spread of the New Zealand mud snail to other Yellowstone Park
waters. It is unknown how the mudsnails were introduced into park streams, but human
transport is strongly suspected. One of the park's primary tools available for reducing
additional expansion of mud snails is an extensive public information campaign detailing
the potential problems associated with this exotic invader. Preparation of brochures and
interpretive signs in areas of high visitor use is a necessary first step in educating the
public. The lack of extensive historical information about the aquatic invertebrate
communities in the affected streams and the uncertainty surrounding potential impacts of
the mud snail on those communities is a major concern of park managers. Preliminary
results from 1-3 year baseline studies by independent researchers reveal that the mud
snails are rapidly increasing in some park waters. Furthermore, certain types of aquatic
invertebrates (mayflies, stoneflies, and caddisflies) appear to be declining in abundance
at sites where mud snails now account for more than 50% of the relative abundance of
aquatic invertebrates. Expanded NPS support of these research-level projects is necessary
to ensure that information presented to the public is timely and accurate.
Feasibility - Participants at a recent informational workshop
indicated that there are few effective treatments to completely eliminate mud snails. Each
mud snail population consists of parthenogenic clones, that is, genetically identical
egg-laden females. Consequently, attempts at crushing or physical removal of the snails
may only exacerbate the problem by spreading eggs to new sites. Chemical treatment would
not necessarily be selective for snails only and could eliminate remnant invertebrate
populations. Alternatively, expanding NPS efforts to increase public awareness of
potential threats to existing aquatic communities may be one of the best tools for
containing the mud snail. As a "sociological treatment" of a pest invasion, this
approach supports recommendations of the parks IPM criteria (YNP Resource Management
Plan, 1995). However, success at preventing spread of this invader can only be evaluated
with a rigorous monitoring program. Selection of long-term standardized protocols, study
areas, and initial sampling can all be accomplished in consultation with expert
researchers within one or two years.
Problem Resolution - Much of the current knowledge regarding New
Zealand mud snails in the park is derived from baseline studies of independent
researchers. The Aquatic Resources staff of the NPS has initiated preliminary planning for
monitoring the mud snail distribution during summer of 1998. However, staff expertise is
limited with respect to the most appropriate mud snail sampling protocols. Additional
inventories and research studies by recognized experts are critical to accurately define
the scope of the current snail infestation. Only with a thorough understanding of impacts
of mud snails on invertebrate communities in YNP can emerging control solutions be
effectively initiated. If the new projects yield new methods of control, long-term
monitoring by NPS will be necessary to assess the effectiveness of any control efforts.
Transferability - The recent one-day workshop hosted by NPS
included university researchers, consultants, and state and federal biologists. All of the
participants indicated that they were very concerned about the potential range expansion
of mud snails to aquatic systems outside of Yellowstone. Part of this concern arises from
the studies in central Idaho, which suggest that mud snails thrive in degraded habitats.
However, the very high mud snail densities observed in non-degraded Yellowstone streams
indicate that mud snails may be adaptable to a variety of habitats. Information derived
from Yellowstone studies on rate of spread of mud snails, changes in aquatic insect
communities, and subsequent effects on recreational fisheries will be useful to managers
within the affected and contiguous watersheds.
Cost effectiveness - NPS support thus far is primarily logistical;
preliminary sampling and consultation with independent researchers. What is needed is
adequate funding of graduate projects, parkwide mollusc survey, development of NPS survey
techniques and selection of long-term sites.