emily shultz-optimized seperation of estuarin plankton to determine association with vibrios pdf
TRANSCRIPT
Optimized Separation of Estuarine Plankton to Determine Associations with Vibrio SpeciesE. Shultz1,2, E. Deyett1,2, M. Hartwick1,2, E. Urquhart1,2, and S. Jones1,3
IntroductionVibrio related illness is a complex public health problem that is intrinsically linked
to ecosystem conditions that support the proliferation of pathogenic strains. Since
1996, the rate of reported Vibrio-related food borne illness in the United States has
increased by 115%. Most transmission occurs indirectly through contaminated
seafood consumption, especially raw oysters. Nutrient-rich microenvironments
associated with plankton selectively enrich Vibrio species to higher densities than
the surrounding water column, and Vibrio parahaemolyticus is highly associated
with zooplankton blooms. To study the interactions between Vibrio species and
plankton in estuaries, a series of experiments were designed to adapt a fresh water
plankton separator created by Nancy Leland under the direction of Dr. Jim Haney
of UNH, for use in an estuarine ecosystem. The plankton separation device utilizes
phototactic behavior to separate phytoplankton from zooplankton with minimal
intermixed contamination to allow quantification of Vibrio concentrations in
separated plankton samples. Optimization of this method required repeated study
over discreet time periods to determine the purity of plankton separation and the
effectiveness of this method.
Figure 1. Protocol for sampling for plankton time trial separation
Results and DiscussionA key outcome of this initial study is that the separation time with the least cross-
species contamination occurs between 30-40 minutes. On the 07/08/2014
sampling date, there was an initial quality separation at 10 minutes, followed by
negative phototaxis of the zooplankton from the zooplankton fraction up into the
phytoplankton fraction, but quality separation was achieved between 30-40
minutes. On the 07/28/2014 sampling date, standard deviations and variability in
data were high, but provided valuable data. There was no separation from 0-20
minutes, zooplankton and phytoplankton were moving back and forth between
fractions.
The current results provide important starting points for continuing to optimize
both the methods and the separation time needed to efficiently separate
phytoplankton species from zooplankton species in estuarine ecosystems. The
upcoming sampling season will benefit from this study because it will help
produce valuable data for understanding the association of plankton species with
Vibrio species in order to determine its potential use in the monitoring of Vibrio
species. The methods outlined in this current study could be utilized in current
empirical modeling methods in coastal regions enabling prediction and prevention
of disease outbreaks from contaminated shellfish. This is a mathematical
representation that attempts to model how plankton species behave in the natural
world, and further how they can be used as a proxy for Vibrio species
concentrations in coastal waters and shellfish found in those waters. This model
takes into consideration environmental factors, nutrient availability and uptake,
community composition, and human influence. Future research will include an in-
depth look at seasonal shifts, same-day tide comparisons, and taxonomic shifts in
plankton composition in order to determine how those relate to Vibrio species
populations and rate of human exposure.
Objectives1. Develop and standardize methods for using a fresh water plankton separator in
estuarine environments.
2. Determine the optimum plankton separation time in estuarine environments.
3. Determine efficacy of separated plankton species to inform molecular and
remote sensing applications.
MethodsChlorophyll a and phycocyanin concentrations were determined by fluorometry
and evaluated at varying time periods on two different sample dates to identify
optimal separation time, where there is the least cross-contamination between
phytoplankton and zooplankton. This optimum time corresponds to when there is
the lowest chlorophyll a concentration in the zooplankton fraction and the highest
chlorophyll a concentration in the phytoplankton fraction. Separated samples were
massed to determine zooplankton mass and thus the time required for the most
zooplankton to move out of the phytoplankton fraction into the zooplankton
fraction via phototaxis. Community analysis was used to determine the
concentration and make-up of zooplankton species in the zooplankton fractions.
Community analysis was accomplished by using an Amscope compound
microscope, counting a minimum of 200 individuals per subsample volume,
taxonomically sorting each individual into its genus/species, and then adjusting the
count data to reflect the total sample volume.
Figure 2: Map of Adams Point and Jackson Estuarine Laboratory in Durham, NH.
Phytoplankton
Zooplankton
Shellfish
Vibrio species
Vibriosis
Water
Sediment
Why does this Research Matter?
1 Northeast Center for Vibrio Disease and Ecology, University of New Hampshire, Durham, NH
2 Department of Molecular, Cellular, and Biomedical Sciences, University of New Hampshire, Durham, NH
3 Department of Natural Resources and the Environment, University of New Hampshire, Durham, NH
Figure 3: Separation efficiency graphs where phytoplankton concentrations are represented by Chloropyll a and Phycocyanin, and zooplankton concentrations are represented by
community analysis counts sorted into Acartia hudsonia, Pseudocalanus, Copepodites, and Nauplii. Quality separation is achieved between 30-40 minutes; no quality separation is
seen from 0-20 minutes.
AcknowledgementsA special thank you to Amanda Murby,
Nancy Leland, Stephanie Rodriguez,
Jackie Lemaire, and Jim Haney PhD
References1. Baker-Austin, C., Trinanes, J.A., Taylor, N.G.H., Hartnell, R., Siitonen, A., and Martinez-Urtaza, J. (2012) Emerging Vibrio risk at high
latitudes in response to ocean warming. Nat Clim Chang 3: 73–77. doi: 10.1038/NCLIMATE1628.
2. Hlavsa, M.C., Roberts, V.A., Anderson, A.R., Hill, V.R., Kahler, A.M., Orr, M., et al. (2011) Surveillance for waterborne disease outbreaks
and other health events associated with recreational water – United States, 2007–2008. MMWR Surveill Summ 60: 1–32.
3. Martinez-Urtaza, J., Bowers, J.C., Trinanes, J., and DePaola, A. (2010) Climate anomalies and the increasing risk of Vibrio parahaemolyticus
and Vibrio vulnificus illnesses. Food Res Int 43: 1780–1790.
4. Martinez-Urtaza, J., Blanco-Abad, V., Rodriguez-Castro, A., Ansede-Bermejo, J., Miranda, A., and Rodriguez-Alvarez, M.X. (2011)
Ecological determinants of the occurrence and dynamics of Vibrio parahaemolyticus in offshore areas. ISME J 6: 994–1006.
5. Rawlings, T.K., Ruiz, G.M., and Colwell, R.R. (2007) Association of Vibrio cholerae O1 El Tor and O139 Bengal with the copepods Acartia
tonsa and Eurytemora affinis. Appl Environ Microbiol 73: 7926–7933
Figure 1: Ecology of Vibrio species.
Figure 4: Collection, processing, and separation methodology.