Benjamin C. Grime’s research while affiliated with The Nature Conservancy and other places

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Publications (3)


Locations of Zostera pacifica (wide-leaved eelgrass) transplant sites and donor bed sites within the Southern California Bight. Sites are indicated by color and site types are designated by shape. Photos from transplant sites of the (A) bundle shoot transplant method and (B) single shoot transplant method are displayed.
Zostera pacifica (wide-leaved eelgrass) transplant survivorship from July 2021 – June 2023, expressed in days after transplanting. Percent survivorship by site (A), color and shape designate site: orange circles (Dockweiler), gold triangles (Redondo Canyon), blue squares (Malaga Cove). Percent survivorship by transplanting method per site (B-D), color designates transplant method: blue (bundle shoot) and orange (single shoot).
Blue color represents transplant sites and red color represents donor bed sites. (A) Species richness at transplant and donor bed sites. Points are averages of all transects at each survey and error bars are standard error. (B) Encounter rates for all fishes at transplant and donor bed sites. Points are averages of all transects at each survey and error bars are standard error. (C) NMDS plot of fish assemblages in transplant and donor bed sites. Each point represents the mean relative encounter rates across all transects during a single survey event at a transplant or donor bed site. Surveys took place from 2021 to 2023. The points remain separate despite passage of time, suggesting relative fish encounters remained different across transplant and donor bed sites. Stress was 0.033. Permutation multivariate analysis of variance (PERMANOVA) results reported on plot.
Temperature exposure timeseries across all transplant and donor sites from July 2021 – June 2023. Solid black line represents mean daily temperature timeseries, while dotted blue line represents site average across the span of the timeseries. Red horizontal line represents temperature threshold set at 20 °C. Gaps in data correspond to sensor malfunctions. Temperature data was unavailable at donor beds until May 2022. Dockweiler (DW), Redondo Canyon (RC), and Malaga Cove (MC) are transplant sites. Palisades (PAL) and East End (EE) are donor beds. Site average ± SD in °C: DW (15.66 ± 1.58), RC (15.30 ± 1.82), MC (16.03 ± 1.69), PAL (16.46 ± 2.41), and EE (16.50 ± 2.64). See Table 2 for percent time each site was above the threshold.
Wave characterization, with H rms (A) and U rms (B), exposure timeseries at the three transplant sites: Dockweiler (DW), Redondo Canyon (RC), and Malaga Cove (MC) and two donor beds Palisades (PAL) and East End (EE). Deployments spanned from July – August 2021 (n = 44 days), September – December 2021 and February – June 2022 (n = 195 days). Note, July – August 2021 sensors were only deployed at transplant sites, and Dockweiler was excluded from the subsequent two deployments while donor beds were added. Solid black line represents daily mean wave data timeseries, while dotted blue line represents site average across the span of the timeseries. Red horizontal line represents Hrms threshold of 0.59 m, and U rms threshold of 0.1 m s⁻¹. H rms site average ± SD in m: DW (0.45 ± 0.08), RC (0.48 ± 0.20), MC (0.50 ± 0.18), PAL (0.37 ± 0.09), and EE (0.38 ± 0.10). U rms site average ± SD in m s⁻¹: DW (0.12 ± 0.02), RC (0.11 ± 0.05), MC (0.13 ± 0.05), PAL (0.09 ± 0.03), and EE (0.11 ± 0.03). See Table 2 for percent time each site was above threshold values.

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Wave, light, and dissolved oxygen exposures drive novel coastal eelgrass (Zostera pacifica) transplant performance
  • Article
  • Full-text available

February 2024

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160 Reads

Rilee D. Sanders

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Benjamin C. Grime

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James J. Leichter

The high ecological and economic value of seagrass has been long recognized, with these foundational habitats providing myriad ecosystem services. Yet through cumulative anthropogenic impacts, seagrasses are exhibiting extensive declines globally. A litany of studies and active restoration trials have demonstrated practical methodologies to restore seagrass habitats and effectively return critical habitat functions to degraded coastal zone systems worldwide. Seagrass loss along the U.S. West Coast has precipitated decades of seagrass protection, conservation, and restoration efforts. Yet, mitigation transplanting efforts have prioritized Zostera marina (narrow-leaved eelgrass) in shallow, protected environments, while a dearth of information is available on species inhabiting offshore islands and exposed mainland coasts. In this study, we conducted a novel transplant of Zostera pacifica, a wide-leaved species found in depths of 7 – 20 m along the offshore islands and mainland coast of California. Transplants were conducted at three geographically distinct sites in Santa Monica Bay, coupled with continuous monitoring of biophysical parameters providing insight into physical drivers at transplant and donor sites. Utilizing in situ data, and environmental thresholds adapted from the literature for Z. marina, we performed exposure analyses to evaluate factors influencing Z. pacifica transplant performance. Exceedances of threshold values for environmental parameters, specifically, wave exposure and near-bed flow speeds (Hrms > 0.59 m and Urms > 0.1 m s⁻¹), photosynthetically active radiation (< 3 and > 5 mol m⁻² day⁻¹) and dissolved oxygen (< 3 mg O2 L⁻¹) exposure impacted transplant survivorship. These results suggest Z. pacifica persist in biophysically dynamic conditions and are sensitive to exceedances of thresholds, underlining the importance of pre-transplant site-selection processes to this species. These data represent the first holistic study of Z. pacifica transplanting on an exposed mainland coast, which provides a view into the baseline environmental envelopes within existing Z. pacifica habitat, and further, may serve as a model for investigating scalable open coast seagrass restoration for temperate regions.

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Fig. 1. (A) High densities of S. purpuratus in an urchin barren state, (B) kelp forest state in southern California, (C) partially dissected Mesocentrotus franciscanus from a kelp forest site, and (D) extracted M. franciscanus urchin gonad (i.e., uni).
Fig. 2. Urchin survey and collection sites on the Palos Verdes Peninsula, California. Site types are designated by color. Some areas within the restoration sites were used as urchin barren collection sites prior to restoration activities beginning in those areas (Sub-site IDs in Table 1).
Fig. 3. The relationship between mean gonad weight (g) and test diameter size (mm) of M. franciscanus collected from April-November 2014 by the site type (color) and site name (shape): Honeymoon Cove (HMC), Lunada Bay (LB), Underwater Arch Cove (UAC), Marguerite Cove (MC), and Rocky Point (RP). Parameter estimates for each curve are reported in Appendix Table A1 and A2. One point in the November panel from Restoration HMC (gonad weight 121.52 g at 91 mm test diameter) is not shown so to better visualize the y-axis range of most data.
Urchin Gonad Response to Kelp Forest Restoration on the Palos Verdes Peninsula, California

March 2023

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129 Reads

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2 Citations

Bulletin Southern California Academy of Sciences

Along the Palos Verdes Peninsula in southern California, high densities of Strongylocentrotus purpuratus (purple sea urchin) have consumed almost all macroalgae on large expanses (61 ha) of rocky reef habitat, creating urchin barrens. Mesocentrotus franciscanus (red sea urchin) harvesting comprises an important fishery in the region, as their gonads are sold as a high-value sushi product called uni. However, with a lack of macroalgal food resources, urchins in barrens are smaller and exist in a starved state, meaning little, if any, gonad product is available to the fishery. To restore local kelp forests and increase gonad biomass available to the M. franciscanus fishery, beginning in October 2013, S. purpuratus were culled in barrens to a target density of 2 per m2 across 5.2 ha of rocky reef on the Palos Verdes Peninsula. Mesocentrotus franciscanus were collected from urchin barren, restoration, and kelp reference sites from April to November 2014 to compare differences in gonad production among the three site types. Culling S. purpuratus resulted in the recovery of normal seasonal M. franciscanus gonad production throughout the 8-month study. Mesocentrotus franciscanus gonad weights at a given test diameter length in restoration sites were equivalent to, and sometimes exceeded, the gonad production of those from the kelp reference sites. The urchin test length distributions of collected M. franciscanus were consistently smaller at urchin barren sites than at kelp reference sites, while those in restoration sites generally fell in between.

Citations (1)


... In addition, several properties related to sea urchins: fecundity, roe quality and feeding rates also had higher values in kelp forests. Therefore, while the density and biomass of urchins are higher in barrens, urchin health and their value as a prey and fishery species are the highest when living in kelp forests [27,91]. In addition to underpinning the function of healthy temperate reef ecosystems, these functions also underpin the ecosystem services that are most valued by people. ...

Reference:

Kelp forests versus urchin barrens: a comparison of ecosystem functions and services provided by two alternative stable marine habitats
Urchin Gonad Response to Kelp Forest Restoration on the Palos Verdes Peninsula, California

Bulletin Southern California Academy of Sciences