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Volume 6, Issue 2
Published June 2011
Special Issue:
Quagga Mussels in the Western United States
Edited by:
Wai Hing Wong and Shawn L. Gerstenberger Department of Environmental and Occupational Health, University of Nevada Las Vegas, Las Vegas, USA
Papers from this issue were prepared by participants attending the workshop entitled “Quagga Mussels in the Western United States – Monitoring and Management”
held in San Diego, California, USA on 1-5 March 2010. The workshop was organized within the framework of the National Shellfisheries Association, American
Fisheries Society (Fish Culture Section) and World Aquaculture Society’s Triennial Conference. The main objective of this workshop was to exchange and share
information on invasive quagga mussels among agencies. The data presented in this special issue provide critical baseline information on quagga mussel monitoring
and management at the early stages of introduction in the western United States.
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Guest Editorial |
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Wai Hing Wong and Shawn L. Gerstenberger
Quagga Mussels in the Western United States: Monitoring and Management
(pp 125-129)
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Research articles |
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Robert F. McMahon
Quagga mussel (Dreissena rostriformis bugensis) population structure during the early invasion of Lakes Mead and Mohave January-March 2007
(pp 131-140)
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Shell length-frequencies were determined for samples of Dreissena rostriformis bugensis collected <2 m depth from Las Vegas Boat Harbor (LVBH),
Callville Bay Marina (two samples, CBM-1 and CBM-2), and Lake Mead Marina (LMM) in the Boulder Basin of Lake Mead and Katherine Landing Marina (KLM)
in the lower end of Lake Mohave within two months of initial discovery of D. rostriformis bugensis in Lake Mead at LVBH on 06/01/2007.
Two annual shell length (SL) cohorts were present at all four sites consisting of individuals presumed to have settled during spring-fall of 2005
and 2006, respectively. Members of the most recently settled 2006 cohort numerically dominated all samples; relative ratios of individuals in the LVBH,
CBM-2, LMM, and KLM 2006 versus 2005 cohorts being 174:1, 95:1, 172:1 and 65:1, respectively. Mean shell lengths of the LVBH, CBM-1, CBM-2, KLM and LMM 2006
cohorts were 6.86 (s.e. = ±0.126), 9.59 (±0.080), 9.31 (±0.194), 10.49 (±0.287) and 12.15 mm (±0.105), respectively. The mean shell lengths of the 2005
cohorts in the LVBH, CBM-2, KLM and LMM samples were 17.5 mm (n = 1), 18.9 mm (n = 4), 21.2 mm (n = 1) and 20.1 mm (n = 4), respectively. The occurrence
of the 2005 cohort in all four sampled sites suggested that quagga mussel introduction to the Boulder Basin occurred prior to 2005. This supposition is
based on the very low probability of individuals from a localized initial introduction appearing in the samples. It is hypothesized that a reproducing
quagga mussel population must have been established somewhere in the Boulder Basin by 2003 or 2004 in order to generate enough veliger larvae to settle
as relatively wide-spread members of the 2005 cohort and be transported downstream to establish a 2005 cohort at KLM in lower Lake Mohave. Essentially
equivalent population structures at all three sampled sites makes speculation on the original site of quagga mussel introduction to the Boulder Basin difficult.
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Chad L. Cross, Wai Hing Wong and Tongda Che
Estimating carrying capacity of quagga mussels (Dreissena rostriformis bugensis) in a natural system:
A case study of the Boulder Basin of Lake Mead, Nevada-Arizona
(pp 141-147)
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Estimation of carrying capacity for bivalves is generally carried out for mussel culture systems wherein maximizing mussel numbers requires
the consideration of both ecological and economic endpoints. We adapted an existing culture-system model to estimate potential carrying
capacity of an invasive species, the quagga mussel (Dreissena rostriformis bugensis) in the Boulder Basin of Lake Mead, Nevada.
We parameterized the model using both field measurements and known quantities previously published in the literature.
To make this model most useful to ecologists and managers, we provide a detailed description and derivation, as well as an example
calculation for the model. The model is based on mean Chlorophyll a concentrations in the Boulder Basin of Lake Mead, and the number
of quagga mussels needed to filter a given reduction in food particles from the water column. Estimates ranged from a total of
1.51 × 1012 mussels with a net reduction of 50% of food particles to 1.02 × 1013
mussels when the net reduction was at the threshold
level of survival (0.017 μg/L). Limitations to the model and potential environmental and ecological considerations are discussed.
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Dong Chen, Shawn L. Gerstenberger, Sara A. Mueting and Wai Hing Wong
Environmental factors affecting settlement of quagga mussel (Dreissena rostriformis bugensis) veligers in Lake Mead, Nevada-Arizona, USA
(pp 149-156)
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Environmental factors that can affect the settlement rate of quagga mussel veligers include flow velocity, water temperature,
pH, dissolved oxygen (DO), conductivity, total organic carbon (TOC), and the surface roughness of monitoring substrates.
In the present study, six artificial substrates, Acrylonitrile Butadiene Styrene (ABS) plastic, High Density Polyethylene (HDPE) plastic,
Concrete Underlayment Board (CUB), aluminum, stainless steel and fiberglass, were used to monitor the settlement of quagga mussel veligers
at different water depths in Lake Mead, Nevada-Arizona, USA. Considering the hierarchical data structure of observed mussel densities,
we investigated the relationship between mussel settlement on monitoring substrates and the surrounding environmental variables by applying
the Linear Mixed Effects (LME) model. After normalization, the above six environmental variables were considered as independent factors
in fixed-effect calculation, while water depth and substrate roughness acted as the group variable and the random term, respectively.
The results indicated that flow velocity, water temperature, and DO were significant factors in determining the mussel settlement on substrates.
TOC was barely significant while conductivity and pH had no impact on settlement of quagga mussel veligers. As to the random effect, no preference
for substrate type could be found, while water depth caused considerably more variation in modeling since it might correlate with most environmental
variables. There is need to emphasize the critical role of flow velocity which is often ignored by biologists - higher flow velocities significantly
decreased the settlement of quagga mussel veligers on substrates. Therefore, to more efficiently monitor quagga mussel colonization in water bodies,
artificial substrates should be deployed in areas without strong flow.
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Eric M. Loomis, Jon C. Sjöberg, Wai Hing Wong and Shawn L. Gerstenberger
Abundance and stomach content analysis of threadfin shad in Lake Mead, Nevada: Do invasive quagga mussels affect this prey species?
(pp 157-168)
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Lake Mead, Nevada is the largest reservoir by volume in the United States, as well as a popular sport fishing destination.
In January 2007, the invasive quagga mussel Dreissena rostriformis bugensis (Andrusov, 1897) was discovered in the reservoir
and concerns began to arise about potential alterations to the aquatic environment. The Lake Mead sport fishery is reliant on
the sustainability of prey species like the threadfin shad [Dorosoma petenense (Günther, 1867)]. This study examined 20-year
trends in historic abundance of the threadfin shad, before, and shortly after, the discovery of quagga mussels in the system.
Larval shad trawl data collected in Las Vegas Bay and Overton Arm portions of Lake Mead were analyzed in the present study.
Two-way analysis of variances showed that the abundance of this prey fish has not changed following quagga mussel invasion (P > 0.05).
Post-quagga mussel discovery collections of adult threadfin shad from Las Vegas Bay ranged from 113 to 212 mm total length (TL)
(mean = 184 mm; n = 170). Shad from Overton Arm ranged from 131 to 197 mm TL (mean = 150 mm; n = 27). Stomach contents were analyzed.
The proportion of cladocerans in stomach contents differed significantly from spring to winter in Las Vegas Bay (P = 0.008);
whereas the proportion of copepods did not show statistically relevant differences regarding seasonality (P = 0.562).
Initial trends in lower trophic level dynamics in response to quagga mussel invasion has yet to reveal significant effects in Las Vegas Bay
or Overton Arm. Long-term monitoring on threadfin shad is needed to evaluate potential impacts from invasive quagga mussels in Lake Mead.
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David K. Britton and Sandra Dingman
Use of quaternary ammonium to control the spread of aquatic invasive species by wildland fire equipment
(pp 169-173)
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Wildland firefighting equipment moves large volumes of raw water during fire incidents in order to extinguish flames or control fire growth.
This water movement may serve as pathways for aquatic invasive organisms to be moved between water bodies and watersheds.
The equipment used may become contaminated and serve as vectors for future invasions across large geographic areas.
New guidelines used by federal firefighting agencies recommend the application of sanitation solutions using quaternary
ammonium compounds for decontaminating wildland fire equipment to prevent the spread of aquatic invasive species that may foul the equipment.
While quaternary ammonium compounds have been tested on other aquatic organisms, the effectiveness of such compounds has not been systematically
tested on dreissenid mussels. We tested the survival of quagga mussel veligers after exposure to a 3% solution of Sparquat
256® for 5 and 10 minutes.
We assessed survival immediately after treatment and then after 60 minutes in fresh water. We found that a 5 minute exposure duration was insufficient
to kill 100% of tested veligers. However a 10 minute exposure, as prescribed in the interagency operational guidelines for preventing spread of aquatic
invasive species, was effective in killing all tested veligers, but not immediately after treatment. An additional 60 minutes were required after
the quaternary ammonium solution was removed before 100% mortality was achieved. This work highlights the need for more rigorous evaluation
of the effectiveness of various sanitation solutions in killing quagga and zebra mussels under different ambient temperatures in order to validate
and refine the sanitation protocol for firefighting equipment and other applications.
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Hongyan Zhang, David A. Culver and Leon Boegman
Dreissenids in Lake Erie: an algal filter or a fertilizer?
(pp 175-194)
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After successfully occupying the benthos of all the Laurentian Great Lakes and connecting channels, quagga mussels
[Dreissena rostriformis bugensis (Andrusov, 1897)] have been colonizing the western United States at a much faster rate.
Study findings and management experience in the Great Lakes will benefit the water resource managers in the western United States
and help them be better prepared to act quickly and effectively to mitigate mussel impacts. We investigated the impacts of dreissenid
mussels on nutrients and plankton using a two-dimensional Ecological model of Lake Erie (EcoLE), and compared their impacts with those
of mesozooplankters. Model results showed that in the shallow western basin, mussel daily grazing impact was less than 10% of the combined
Non-Diatom Edible Algae (NDEA) and diatom biomass, although they cleared a volume equivalent to 20% of the water column daily. Moreover,
in the deep central and eastern basins, dreissenids grazed only 1-2% of the NDEA and diatom biomass per day. The relative importance
of dreissenids’ grazing impact on diatoms and NDEA to those of zooplankton’s varied among years and basins in Lake Erie. In general,
zooplankton had slightly higher grazing impacts than did the mussels on NDEA and diatoms in the western basin but much higher grazing
impacts in the central basin. Dreissenid mussels excreted a big portion of phosphorus in the bottom water, especially in the western basin,
while zooplankton kept a big portion of algal phosphorus in the water column, especially in the central and eastern basins. Non-Diatom
Inedible Algae (NDIA) abundance increased with more phosphorus available and was less responsive to mussel selective grazing. Dreissenid
mussels affected crustacean zooplankton mainly through their impacts on NDEA. Our results thus indicate that dreissenid mussels have weak
direct grazing impacts on algal biomass due to a concentration boundary layer above the mussel bed, while their indirect effects through
nutrient excretion have much greater and profound negative impacts on the system. EcoLE is a modification of CE-QUAL-W2, which is frequently
applied to western aquatic systems, and we suggest that with this modification, the models can be used to predict dreissenid impacts in western lakes,
reservoirs, and rivers in which they may become established.
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Management in Practice |
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Kent Turner, Wai Hing Wong, Shawn L. Gerstenberger and Jennell M. Miller
Interagency Monitoring Action Plan (I-MAP) for quagga mussels in Lake Mead, Nevada-Arizona, USA
(pp 195-204)
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Following the discovery of quagga mussels in Lake Mead, Nevada-Arizona, USA, a variety of federal, state and regional agencies
set up monitoring programs to evaluate and gain information to help minimize the impacts, or potential impacts, of quagga mussels
to their facilities and lake ecology. While the agencies have worked closely and shared monitoring data and findings from the beginning
of the infestation, there has been no documented comprehensive monitoring program to describe and record the various quagga mussel-related
monitoring needs. Ad hoc interagency quagga mussel meeting representatives established an Interagency Monitoring Action Plan (I-MAP),
which outlines agency objectives related to quagga mussel monitoring and provides approaches to realize these objectives. I-MAP team members
and their respective agencies provide technical, logistical, and financial support in monitoring quagga mussels and their environmental impacts
to Lake Mead. The goal of this effort is to develop a long-term, cost-effective, and consistent monitoring plan for quagga mussels in Lake Mead
to inform various agencies and to gain efficiencies from shared operations and information. The plan attempts to build upon current monitoring
activities and capabilities, identifies the next steps that can occur within existing capabilities and, finally, outlines gaps and areas of future need.
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Wai Hing Wong, Shawn L. Gerstenberger, Jennell M. Miller, Craig J. Palmer and Bryan Moore
A standardized design for quagga mussel monitoring in Lake Mead, Nevada-Arizona
(pp 205-215)
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The discovery of quagga mussels (Dreissena rostriformis bugensis) in Lake Mead, Nevada-Arizona, on January 6, 2007
is the first known occurrence of dreissenid species in the western United States. This study developed elements of a cost-effective
and standardized quagga mussel-monitoring program for Lake Mead using preliminary data to arrive at statistically based numbers
of sampling sites. To represent the abundance of adult/juvenile quagga mussels in Lake Mead’s heterogeneous floor with 95% confidence,
a stratified simple random sampling design revealed a requirement of 41 samples from hard substrates (i.e., rocky areas) and 97 samples
from soft substrates (i.e., sandy and muddy areas). A simple random sampling design demonstrated that 42 samples from the lake’s water column
are necessary to represent veliger abundance with 95% confidence. Other important elements of the sampling program, such as standardization
of protocols and processes and suggested data analyses, are discussed. The monitoring program, which is based on reconnaissance data,
is intended to be optimized with data from its first year’s samples. The sample number-selection approach and the other elements of this
plan can be easily implemented by lake managers and can also be adapted to other locations where dreissenid mussel monitoring is needed.
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Denise M. Hosler
Early detection of dreissenid species: Zebra/Quagga mussels in water systems
(pp 217-222)
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Early detection of dreissenid species in water systems is critically important to maintaining structure and function of dam related structures.
If mussels are detected early, facility operators may have approximately three to five years to adjust systems before the population of mussels
are large enough to restrict the flow of water, clog pipes, restrict water intakes, affect cooling systems, and impede power generation.
However, early detection of dreissenids in water with the current methods has some inherent issues with variability in sampling and reliability
with analytical methods which creates management decision dilemmas. Since current control methods of these mussels are very limited in regulated
water systems, Reclamation is conducting intensive research. To improve early detection in water systems, Reclamation has developed an analytical
strategy that includes cross polarized light microscopy, scanning electron microscopy (SEM), flow cell cytometry, and polymerase chain reaction (PCR).
This analytical strategy is used on water samples collected using a plankton tow net to collect primarily from reservoirs and also from water flow
within facilities, usually from a tap or pipe.
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Sara A. Mueting and Shawn L. Gerstenberger
The 100th Meridian Initiative at the Lake Mead National Recreation Area, NV, USA:
Differences between boater behaviors before and after a quagga mussel, Driessena rostiformis bugensis, invasion
(pp 223-229)
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The 100th Meridian Initiative was developed to help prevent the spread of aquatic nuisance species (ANS) through boater education
and research on boater movement patterns and behaviors. Surveys employing these elements were conducted at Lake Mead National
Recreation Area (LMNRA) in 2002-2003 before the discovery of the quagga mussel (Dreissena rostiformis bugensis Andrusov 1897)
and in 2007-2008 after an established population of quagga mussels was found in the Lake. Boaters were asked questions in a personal
interview or a mail-in survey regarding what body of water they had previously launched their watercraft in, where they were planning
to launch next, if they cleaned their watercraft between each launch, and if they were aware of quagga mussels or other ANS.
Results from the personal interviews and mail-in surveys indicated a significant increase in mussel awareness between the pre-
and post- mussel invasion groups. Cleaning habits between the study periods for both interviews and mail-in surveys did not
differ significantly. Boat trailer states of registration were also documented in both study periods in the parking lots of LMNRA.
In 2002-2003, 0.6% of the trailers documented were from states with known zebra or quagga mussel populations, whereas in 2007-2008,
98.2% of states documented had known zebra or quagga mussel populations. Increased boater awareness will help prevent the spread of
aquatic invasive species and the 100th Meridian Initiative is a helpful way to educate boaters and collect relevant data on future
mussel invasions. The preservation of natural waters is vital for the conservation of native species and the prevention of zebra
and quagga mussel invasions will assist in this preservation. Further efforts should be directed toward educating boaters on effective
cleaning methods.
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