
NSF Org: |
OCE Division Of Ocean Sciences |
Recipient: |
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Initial Amendment Date: | August 3, 2015 |
Latest Amendment Date: | March 25, 2019 |
Award Number: | 1538582 |
Award Instrument: | Standard Grant |
Program Manager: |
Cynthia Suchman
csuchman@nsf.gov (703)292-2092 OCE Division Of Ocean Sciences GEO Directorate for Geosciences |
Start Date: | August 15, 2015 |
End Date: | January 31, 2021 (Estimated) |
Total Intended Award Amount: | $708,588.00 |
Total Awarded Amount to Date: | $774,348.00 |
Funds Obligated to Date: |
FY 2017 = $21,920.00 FY 2018 = $21,920.00 FY 2019 = $21,920.00 |
History of Investigator: |
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Recipient Sponsored Research Office: |
1156 HIGH ST SANTA CRUZ CA US 95064-1077 (831)459-5278 |
Sponsor Congressional District: |
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Primary Place of Performance: |
100 Shaffer Rd. Santa Cruz CA US 95060-5730 |
Primary Place of
Performance Congressional District: |
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Unique Entity Identifier (UEI): |
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Parent UEI: |
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NSF Program(s): | BIOLOGICAL OCEANOGRAPHY |
Primary Program Source: |
01001718DB NSF RESEARCH & RELATED ACTIVIT 01001819DB NSF RESEARCH & RELATED ACTIVIT 01001920DB NSF RESEARCH & RELATED ACTIVIT |
Program Reference Code(s): |
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Program Element Code(s): |
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Award Agency Code: | 4900 |
Fund Agency Code: | 4900 |
Assistance Listing Number(s): | 47.050 |
ABSTRACT
A key goal of ecology is to understand how species interactions -- competition, predation, mutualism -- influence the structure (e.g., biodiversity) and functions (e.g., productivity) of ecological communities and contribute to the stability and resilience of ecosystems. Kelp forests along the West Coast of North America have been a model ecosystem in which marine ecologists have explored these questions. That work has provided evidence that predators, including sea otters, sea stars, and fishes, can be important in controlling sea urchins that otherwise overgraze forests and create alternative "barrens" states, devoid of kelp. However, other examples suggest that disease and disturbance, not predators, suppress urchin overgrazing. Here we employ experiments and surveys to determine whether and how sea otters and sea stars act separately and in combination to control the rapid growth of sea urchin populations that is occurring in concert with a sea star "wasting" epidemic along the West Coast of North America. The results of this work will (i) advance our understanding of how multiple predators interact to influence community structure, stability and resilience, and (ii) shed light on how species interactions contribute to the stability of these forests that are the foundation of productive commercial and recreational fisheries. The project will involve citizen scientists contributing to surveys of sea otter abundance, foraging behavior and diet, and underrepresented (largely Latino) undergraduates and results will be disseminated in several public outreach facilities and K-12 educational programs.
This project will advance our understanding of the combined roles of species diversity and predators in contributing to the stability and resilience of community structure. Though both predators and diversity have been the focus of numerous studies, fewer have explored how predator diversity does or does not enhance the resilience of marine ecosystems. The investigators will determine the relative contributions of southern sea otters (Enyhda lutris lutris) and two species of sea stars (Pycnopodia helianthoides and Pisaster giganteus) in controlling the density and size structure of two prey species, the purple sea urchin (Strongylocentrotus purpuratus) and a snail (Promartynia pulligo), and the cascading effects on survival and density of giant kelp (Macrocystis pyrifera). Orthogonal manipulations of predator access in large field enclosures/exclosures will be used to assess the relative roles of redundancy, complementarity and "sampling effect" (i.e. particular importance of either species) among the two predators on both direct mortality and indirect (trait-mediated) foraging behavior of their prey. The PIs will evaluate whether results from the experiments "scale up" to explain geographic variation in the relative densities of predators (otters and stars), prey (urchins) and the major primary producer (giant kelp) and the ability of sea otters to compensate for declines in sea stars to control the rapid growth in purple sea urchin populations that can otherwise cause phase shifts (forests to barrens) of these ecosystems.
PUBLICATIONS PRODUCED AS A RESULT OF THIS RESEARCH
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PROJECT OUTCOMES REPORT
Disclaimer
This Project Outcomes Report for the General Public is displayed verbatim as submitted by the Principal Investigator (PI) for this award. Any opinions, findings, and conclusions or recommendations expressed in this Report are those of the PI and do not necessarily reflect the views of the National Science Foundation; NSF has not approved or endorsed its content.
Many ecosystems are experiencing unprecedented environmental changes, underscoring theimportance of understanding ecological processes that impart ecosystem resistance and resilience.Many kelp forests around the world have experienced dramatic declines, including forests of giant kelp(Macrocystis pyrifera) along the coast of central California. We investigated the causes andconsequences of these declines and the ecological mechanisms of ecosystem resistance and resilience.
Loss of giant kelp forests along the Monterey Peninsula in central California coincided with (i) the localecological extinction of the sunflower star (Pycnopodia helianthoides), a significant predator of seaurchins, in 2013 and (ii) a marine heatwave that persisted from 2014 to 2016. Loss of Pycnopodia wasassociated with the sea star wasting disease (SSWD) epidemic. During and since these events, weobserved outbreaks of the purple sea urchin (Strongylocentrotus purpuratus), which created a spatialmosaic of ?urchin barrens? devoid of macroalgae, and remaining kelp forests.
We combined community surveys with field and laboratory (mesocosm) experiments to test alternativeexplanations for these urchin outbreaks. Surveys of community structure before, during and after theSSWD and MHW revealed a decline and persistent loss of Pycnopodia, increase in counts of purple seaurchins, and the coincident decline in densities of kelps and other algae. Many sites that exhibited thistransition from forested to ?urchin barens? have persisted through 2021.
Surveys of purple urchin size structure (i.e. relative abundance of urchin sizes) and size-baseddemographic modelling indicate that rapid increases in counts of large (4-5 cm diameter) purple urchinswas initiated by a foraging response, with subsequent larval recruitment contributing to the persistenceof barrens. With the loss of a predator and declining abundance of kelp, purple urchins emerged fromcracks and crevices and possibly migrated from deeper depths to overgraze algae. Field and labexperiments substantiate that the lack of predators and drift kelp precipitate the emergence of purpleurchins and overgrazing of kelps.
We evaluated the role of alternative predators, sea otters (Enhydra lutris nereis) and the red rock crab(Cancer productus), in reducing grazing by urchins in barrens and facilitating forest recovery. Weexplored direct numerical responses and indirect behavioral responses of predators and their urchinprey. The number of sea otters specializing on urchin prey caused an increase in urchin consumption,increase in sea otter survivorship, and local population size. However, sea otter foraging was confined toenergetically profitable urchins with high gonad volumes within remaining forests and not linked to highdensities of urchins with poor gonad condition in barrens. Therefore, while sea otter foraging enhancedthe resistance of remaining forests to overgrazing, it did not contribute to the decline of urchins inbarrens. Nonetheless, the remaining forests are the sources of kelp spores required to reforest barrensand thereby enhance forest resilience.
To evaluate the role of rock crabs, we conducted experiments in lab mesocosms (1.1 m 3 cattle troughs),and on small (0.5 m 3 ) and large (6 m 3 ) caged rocky reefs in the field. These experiments differ in theircontrol, accuracy, and frequency of observations (mesocosms>small cages>large cages) and how wellthey represent the natural environment (large cages>small cages> mesocosms). Results across theseexperiments demonstrated that rock crab, unlike sea otters, kill gonad-poor sea urchins from barrensand reduce grazing rates and kelp loss by at least 50%. Moreover, the direct mortality of urchins and the
behavioral response of urchins to seek shelter from predators contribute equally to the increasedsurvival of kelp. Efforts to quantify the abundance of rock crabs in urchin barrens are ongoing.
We observed forest recovery in one of the monitored urchin barrens. Purple sea urchins migrated fromthe deeper barrens to shallow reefs that supported beds of red algae. A forest eventually reestablishedon the deeper reef vacated by the sea urchins, demonstrating the important role of foraging migrationsin the process of forest recovery.
Together, our results demonstrate the importance of diversity of alternative predators for the resilienceof communities to disturbance, the crucial role of behavior, both of predators and prey, in determiningthe state (forested vs. deforested) of an ecosystem, and how the pattern of disturbances (thejuxtaposition of forest and barrens) influences the behavior and interactions between predators andprey and ecosystem resilience.
Broader impacts of this project include the training of eight high school and over 30 undergraduateunderrepresented minority students, many of whom produced independent studies, theses, andpresentations. Many of these students graduated and are now in graduate programs or working forresource management agencies. The project demonstrates the productive collaboration betweenacademic (UCSC), federal (USGS) and non-profit (Monterey Bay Aquarium) organizations. Results havebeen presented at multiple scientific and public venues, informing the public and state and federalresource managers of the importance of predator diversity in the persistence and resilience of kelpforest ecosystems.
Last Modified: 01/21/2022
Modified by: Mark H Carr
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