Dataset: Counts of organisms recorded during emergent and rapid emergent surveys conducted in the subtidal zone of northern California, Sonoma and Mendocino counties, from 1999 to 2023

ValidatedFinal no updates expectedDOI: 10.26008/1912/bco-dmo.927682.1Version 1 (2024-08-30)Dataset Type:Other Field Results

Principal Investigator, Contact: Laura Rogers-Bennett (University of California - Davis: Bodega Marine Laboratory)

Data Manager: Robert R. Klamt (University of California - Davis: Bodega Marine Laboratory)

BCO-DMO Data Manager: Shannon Rauch (Woods Hole Oceanographic Institution)


Project: Collaborative Research: The effects of marine heatwaves on reproduction, larval transport and recruitment in sea urchin metapopulations (Urchin metapopulations)


Abstract

The Kelp Forest Monitoring data record span surveys across 24 years from 1999 through 2023 at 20 locations on the Sonoma-Mendocino Coast, Northern California. Years without data, inclusive: 2002, 2020, 2021. These surveys are ongoing and are conducted by the California Department of Fish and Wildlife dive team with participation from dive program partners at UC Davis, UC Santa Cruz, Cal Poly Humboldt, Sonoma State, and other dive programs and volunteers. Not all sites were surveyed in all years....

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Data were collected during day-trips aboard California Department of Fish and Wildlife or NOAA patrol boats, generally 2-5 days at select survey locations in 1999, 2000, 2001, 2003-2019, 2022, and 2023.

All surveys were done using SCUBA along 30x2 meter (m) transects (60 square meters total area) randomly placed in the subtidal zone in rocky habitats dominated by bull kelp (Nereocystis luetkeana) forests. These randomly placed band transect surveys were stratified by depth (A=0-15, B=16-30, C=31-45, D=46-60 ft) as we know sea urchin and abalone populations differ by depth. Two divers (a dive team) work together to count and measure organisms.

Divers were deployed as teams to randomly-selected GPS waypoints within designated depth strata (A, B, C, D). Divers typically complete multiple transects within each of the four depth strata ranging from 0 to 60 feet at each site. Divers swim along transect tapes measuring 30 x 2m in area across the rocky reef. All transect surveys were in habitat dominated (>70% rock) by rocky reef.

Emergent Surveys:
Emergent sampling focused on emergent, exposed, or cryptic animals in rock crevices or under rock ledges but visible without turning rocks or the use of a flashlight. Data collected on the transects include depth of transect, dive number, the number of each species of abalone and sizes of Haliotis rufescens, pinto abalone (H. kamtschatkana), flat abalone (H. walallensis), number of sea urchins (red, Mesocentrotus franciscanus, or purple, Strongylocentrotus purpuratus) and size as time allowed, number of associated species and predators, substrate, algal type percent cover. Where needed divers mark abalone shells with yellow forestry crayons to avoid duplicate counts and measures. Data from each dive were recorded on waterproof datasheets which the divers fill out along the transect. Upon return to the boat, data sheets were checked by the lead diver to ensure accuracy and readability for the first field site quality control check.

Rapid Emergent Surveys:
In response to the extreme purple sea urchin population increase and abalone mortality event in 2016-18, survey methodology changed somewhat with fewer transects per site (approx. 12 per site). Divers conducted a rapid assessment sampling technique: Rapid Emergent Abalone Surveys were similar to standard emergent surveys (see above) but focused on purple sea urchin and red abalone counts of live and dead abalone and sea stars. Divers conduct two to four rapid emergent transects per dive.

Primary data collected on each rapid transect are number of live, dying, and dead red sea urchins, purple sea urchins, red abalone, pinto abalone, and flat abalone, as well as empty abalone shells. Additional data collected (if bottom time and/or air allowed): red abalone size, number of associated species and predators, algal habitat coverage, substrate type, and presence of bull kelp. Abalone that were measured were marked with yellow forestry crayons to avoid duplicate counts and measures. As with the emergent surveys, the divers fill out data on waterproof datasheets along the transect. Upon return to the boat data sheets are checked by the lead diver to ensure accuracy and readability for the first field site quality control check.

The data specific to this dataset are the numbers of purple sea urchins, red sea urchins, red abalone, flat abalone, and pinto abalone, as well as associated species along each transect.


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García-Reyes, M., Thompson, S. A., Rogers-Bennett, L., & Sydeman, W. J. (2022). Winter oceanographic conditions predict summer bull kelp canopy cover in northern California. PLOS ONE, 17(5), e0267737. https://doi.org/10.1371/journal.pone.0267737
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Hamilton, S. L., Saccomanno, V. R., Heady, W. N., Gehman, A. L., Lonhart, S. I., Beas-Luna, R., Francis, F. T., Lee, L., Rogers-Bennett, L., Salomon, A. K., & Gravem, S. A. (2021). Disease-driven mass mortality event leads to widespread extirpation and variable recovery potential of a marine predator across the eastern Pacific. Proceedings of the Royal Society B: Biological Sciences, 288(1957), 20211195. https://doi.org/10.1098/rspb.2021.1195
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McPherson, M. L., Finger, D. J. I., Houskeeper, H. F., Bell, T. W., Carr, M. H., Rogers-Bennett, L., & Kudela, R. M. (2021). Large-scale shift in the structure of a kelp forest ecosystem co-occurs with an epizootic and marine heatwave. Communications Biology, 4(1). https://doi.org/10.1038/s42003-021-01827-6
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Okamoto, D. K., Spindel, N. B., Collicutt, B., Mustermann, M. J., Karelitz, S., Gimenez, I., Rolheiser, K., Cronmiller, E., Foss, M., Mahara, N., Swezey, D., Ferraro, R., Rogers-Bennett, L., & Schroeter, S. (2023). Thermal suppression of gametogenesis explains historical collapses in larval recruitment. https://doi.org/10.1101/2023.09.28.559919
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Rogers-Bennett, L., & Catton, C. A. (2022). Cascading impacts of a climate-driven ecosystem transition intensifies population vulnerabilities and fishery collapse. Frontiers in Climate, 4. https://doi.org/10.3389/fclim.2022.908708