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Other Recent Projects
This research was funded by the DOE Waterpower Program. A key challenge addressed by this research is to push beyond the status quo of using simple fixed constraints (conservation targets such as minimum flows) to protect downstream environmental resources of concern and,
instead, identify and incorporate environmental criteria as objectives to be maximized. This effort builds on previous modeling research to optimize flows for salmon by thinking "outside the channel"
and quantifying the role of floodplain inundation on riparian habitat and the growth and production of juvenile fish. In its second year, seasonal energy values were considered
as a second objective and a Pareto-optimal frontier of non-dominated solutions was estimated using genetic algorithms. Energy value was infered from the
temperature-related fluctuations in the value of electricity and loss of energy associated with water that spills (bypasses turbines). Two key results emerged: (1) solutions for both economic and salmon objectives
allocated flow in summer, and (2) in wetter years, solutions favoring salmon allocated a second pulse flow in late winter to enable juvenile salmon to grow fast and migrate out of the river
before water temperatures rise.
More information about ORNL's role in the optimization project is available here pdf. and the Water power program
at ORNL is described here.
The California Department of Fish and Game, headed by Dean Marston, is developing a full-lifecycle population model for fall Chinook salmon in the San Joaquin River and its three tributaries. ORNL provided guidance and relationships for the inland portion of the model. In particular, results included a metaanalysis and review of primary studies of temperature influences on egg and alevin development and survival, as well as thermal tolerances. Uni-modal survival relationships were fitted to data from all of these studies.
Predicting population response to summer water quality required simulating growth, movement, reproduction, and survival of individual sturgeon in response to gradients in temperature, salinity and dissolved oxygen in the Ogeechee River. We simulated water quality using empirical models based on measurements taken throughout 2008-2009. In addition, a study of headwater watersheds on Fort Stewart related nutrient and sediment concentrations draining watersheds to watershed attributes including vegetation, road densities, and military training.
The EFDC water quality model will simulate salinity changes caused by rice canals that link the Little Ogeechee and the Ogeechee rivers. A bioenergetic and mercury-uptake model developed for shortnose sturgeon was used to estimate egg concentrations and potential reproductive effects. The supporting field component of this effort measured methyl mercury concentrations in amphipods along a salinity gradient in the Ogeechee River. We found that our bioenergetic-mercury uptake model produced reasonable predictions of gonadal concentrations, which were not sufficiently high to cause concern.
Shortnose sturgeon killed by shad net captures were simulated using a individual-based and spatially explicit PVA model based on data from net surveys conducted in late-winter and spring, 2008. This project was a collaborative effort with Doug Peterson at the University of Georgia, Mark Bevelhimer and myself at ORNL, and the Natural Resources Branch at Fort Stewart, with support from the UGA Marine Extension at Brunswick (chemical analyses) and Dynamic Solutions LLC (EFDC implementation). Daniel Farrae (UGA) and Roy King (ORISE) conducted field surveys and collecting water samples, respectively.
Watch our movies of the Ogeechee River (avi format):
Daniel Farrae's maps of shortnose sturgeon habitat suitability
Mark Bevelhimer's EFDC maps of salinity with rice canals and without rice canals:
In this ORNL seed project, headed by Rebecca Efroymson, we examined the potential use of ecological models to derive relative values for animal populations and their habitat. Ecological models were used to transfer values from populations to habitat and vice versa, and to examine how extinction thresholds influence use and non-use values, measured by willingness-to-pay surveys. Efroymson, Jager and Hargrove reviewed and projected future use of population and landscape models in valuation of wildlands. Jager, Oladosu and Efroymson demonstrated the combined use of a population model and an economic model in a case study involving Chinook salmon. The age-based population model showed that equilibrium population sizes increased with total annual flow, whereas minimum viable population size decreased with total annual flow. Marginal willingness to pay for equilibrium population size was optimal at an intermediate, but relatively low level of annual flow, whereas marginal willingness to pay for minimum viable population size decreased with flow.
We
developed a PVA model for white sturgeon populations in the
Because there are a number of
different factors that potentially influence white sturgeon in each river
segment, we designed specific models to address those questions. Mark
Bevelhimer developed a bioenergetic model to quantify the effects of
load following operations on white sturgeon growth and reproduction. He
found that temperature differences among the river segments alone explain
significant differences in reproductive potential over the lifetime of a
female (Bevelhimer 2002). This information feeds into the PVA model to
quantify population-level effects.
Annett Sullivan developed a spatial model designed to quantify the
effects of water quality in Brownlee Reservoir. She found that predictions
of population-level effects to depend on model assumptions about movement
(Sullivan et al. 2003).
Our latest research has focused on
understanding the effects of small population size on extinction risk for
white sturgeon in the
Mark Bevelhimer led an effort to quantify the costs and benefits of instream-flow mitigation practices on hydropower generation and on biological communities. I used intervention analysis to test for a significant change in annual generation, accounting for year-to-year variation in flow as a covariate. Relicensing usually had a negative effect on generation, presumably due to flow mitigation, but that the decrease was rarely significant, even after removing the effects of year-to-year variation in climate (flow). For hydropower projects (i.e., dams) that changed from peaking to run-of-river operations, we evaluated changes in the proportion of flow released during peak demand using sub-daily flow data from USGS. Results showed a reduction in this proportion following relicensing primarily at dams with large storage capacity and no upstream regulation. In several cases, the proportion increased at dams passing through flow fluctuations from upstream projects. I also reviewed efforts to optimize hydropower operations for biological objectives, or to constrain operations to protect biological resources.
Rebecca Efroymson led ORNL’s role in this collaboration between LLNL (Tina Carlson), BLM, and ORNL. We are using spatially explicit, individual-based models to study the effects of habitat loss and fragmentation on bird and mammal populations of conservation concern, including the prairie dog (LLNL) and the sage grouse (ORNL). We developed a generalized population viability analysis (PVA) model that permits individuals to be social in some seasons (breeding, primary feeding, winter) and solitary in other seasons. We parameterized this model for sage grouse in the Uintah Basin, Utah and used the model to predict minimum viable population sizes for the species. The model-derived estimates were compared with those published in field studies.
The ORCM was developed between 1995 and 2000 and used to predict seasonal patterns of flow that would maximize Chinook salmon recruitment from the Tuolumne River below New Don Pedro Dam. Since that time, nearly ten years of monitoring have been conducted by Tim Heyne and others at the California Department of Fish and Game, including rotary screw trapping of outmigrating juveniles. This study, funded by the California Energy Commission, had two objectives. First, I compared ORCM predictions to these monitoring data, evaluated discrepancies, and made improvements to the model or its parameters. We conducted a functional validation in which we compared model and data relationships between (measured or predicted) salmon outmigration and flow, spawner density and degree-days. Autocorrelation in predictors were accounted for in the analysis. After two sets of comparisons, agreement was adequate for some years, but considerable differences remained for others. Second, we developed imputation equations to use in estimating smolt outmigration. Third, I implemented a routine to estimate the hydropower generation value associated with simulated flow regimes.
The goal of this project was to evaluate the role of spatial uncertainty or error on projections from PVA
and other ecological models used by DoD. As part of this SERDP-funded
project, we (Tony King, Tom Ashwood, Barbara Jackson and me) developed a
method for generating stochastic simulations to be used in spatial
uncertainty analysis. This
approach was published in Ecological Modelling in 2005. We found that population
viability models were most sensitive for landscapes whose average spatial
statistical properties placed them near extinction thresholds (e.g.,
subject to Allee effects).
We developed an ecological framework to evaluate the impacts of releases at petroleum exploration and production sites. The project team at ORNL was headed by Rebecca Efroymson and is using a case study at the Nature Conservancy's Tallgrass Prairie Preserve in Oklahoma We collaborated with Tina Carlsen and Tanya Kostova at Lawrence Livermore National Laboratory. We developed a landscape model for birds or mammals, with help from Eric Carr, and evaluated the simulated effects of habitat loss and fragmentation on American badger populations. We found that the decline of population viability was steeper on fragmented landscapes, particularly for a species like the American badger that does not avoid poor or risky habitat. We also quantified Allee effects caused by the failure to find mates in disturbed landscapes, which suggests that the presence of unmated females defending territories might be an early warning sign that densities are too low (Jager et al. Ecological Modelling).
In this project, I worked with Steve Krentz to develop a Population Viability
model for pallid sturgeon. The model which simulates hybridization between pallid and shovelnose sturgeon and hatchery
stocking. The pallid sturgeon is listed under the Endangered Species Act and its recovery is the concern of recovery teams throughout the
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Modified: Feb 11, 2009