Impacts of Coastal Acidification on the Pacific Northwest Shellfish Industry and Adaptation Strategies Implemented in Response
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Impacts of Coastal Acidification on the Pacific Northwest Shellfish Industry and Adaptation Strategies Implemented in Response Barton, A., Waldbusser, G. G., Feely, R. A., Weisberg, S. B., Newton, J. A., Hales, B., ... & McLaughlin, K. (2015). Impacts of coastal acidification on the Pacific Northwest shellfish industry and adaptation strategies implemented in response. Oceanography, 28(2), 146-159. doi:10.5670/oceanog.2015.38 10.5670/oceanog.2015.38 Oceanography Society Version of Record http://cdss.library.oregonstate.edu/sa-termsofuse EMERGING THEMES IN OCEAN ACIDIFICATION SCIENCE Impacts of Coastal Acidification on the Pacific Northwest Shellfish Industry and Adaptation Strategies Implemented in Response By Alan Barton, George G. Waldbusser, Richard A. Feely, Stephen B. Weisberg, Jan A. Newton, Burke Hales, Sue Cudd, Benoit Eudeline, Chris J. Langdon, Ian Jefferds, Teri King, Andy Suhrbier, and Karen McLaughlin Photo credit: Sandra Barton Vickers 146 Oceanography | Vol.28, No.2 ABSTRACT. In 2007, the US west coast shellfish industry began to feel the effects at optimal levels, but the chemistry of of unprecedented levels of larval mortality in commercial hatcheries producing incoming seawater varies (Barton et al., the Pacific oyster Crassostrea gigas. Subsequently, researchers at Whiskey Creek 2012). Subsequent work, in part the result Shellfish Hatchery, working with academic and government scientists, showed a of monitoring larval oysters in shellfish high correlation between aragonite saturation state (Ωarag) of inflowing seawater and hatcheries, documents a mechanism for survival of larval groups, clearly linking increased CO2 to hatchery failures. This work direct Ωarag sensitivity in early shell forma- led the Pacific Coast Shellfish Growers Association (PCSGA) to instrument shellfish tion of bivalve larvae (Waldbusser et al., on the Pacific Northwest hatcheries and coastal waters, establishing a monitoring network in collaboration with 2013; 2015), responses previously thought university researchers and the US Integrated Ocean Observing System. Analytical to be related solely to changes in the developments, such as the ability to monitor Ωarag in real time, have greatly improved organisms’ acid-base chemistry (Pörtner, Shellfish Industry the industry’s understanding of carbonate chemistry and its variability and informed 2008). These findings have immediate the development of commercial-scale water treatment systems. These treatment implications for the Pacific Northwest systems have generally proven effective, resulting in billions of additional oyster shellfish industry, which has experienced larvae supplied to Pacific Northwest oyster growers. However, significant challenges significant seed shortages since 2007. remain, and a multifaceted approach, including selective breeding of oyster stocks, In nearshore California Current sur- expansion of hatchery capacity, continued monitoring of coastal water chemistry, and face waters off the coast of Oregon, the improved understanding of biological responses will all be essential to the survival of increase in atmospheric CO2 has shifted the US west coast shellfish industry. the median Ωarag from approximately 2.5 to 2.0 (Feely et al., 2008; Harris et al., INTRODUCTION sensitive to the effects of ocean acidifi- 2013), and values of Ωarag less than 2.0 are The coastal ocean along the west coast cation (OA), such as reduced saturation already common throughout the spring of the United States supports some of state (Fabry et al., 2008; Hofmann et al., and summer across major sections of the most productive fisheries in the 2010; Hettinger et al., 2012; Bednaršek US Pacific coastal waters and Puget Sound world, including the 120-year-old Pacific et al., 2012, 2014; Gazeau et al., 2013; (Feely et al., 2008, 2010, 2012b; Hauri Northwest shellfish industry. Seasonal Kroeker et al., 2010, 2013; Gaylord et al., et al., 2009). OA has contributed signifi- coastal upwelling, which annually sup- 2014), including many commercially cantly to shoaling of Pacific Northwest plies nutrient-rich water to the inner con- important shellfish species (Kurihara aragonite and calcite saturation horizons tinental shelf from late spring to early et al., 2007; Green et al., 2009; Miller (Feely el al., 2012b), and recent observa- fall, drives this productivity. However, et al., 2009; Talmage and Gobler, 2011; tions along the Oregon/Washington coast the same upwelling that fuels the indus- Barton et al., 2012; Hettinger et al., 2012; have recorded Ωarag <1.0 in upwelled water try also threatens it. Decomposition of Waldbusser et al., 2013, 2015). Organisms at the surface, a condition not expected in organic matter at depth naturally raises that deposit calcareous shells or skele- the open ocean for decades (Feely et al., CO2 in upwelled seawater, and increasing tons may respond to decreasing Ωarag at 2008). Modeling of the California Current atmospheric CO2 concentrations have values as high as 2, and are expected to System predicts that this trend will con- raised the baseline, leading to increased encounter increasing physiological chal- tinue and accelerate relative to the open intensity, magnitude, and duration of lenges as carbonate saturation decreases oligotrophic ocean, with undersaturated acidified water over the continental shelf in the ocean (Fabry et al., 2008; Barton conditions in surface waters predicted to (Feely et al., 2008; Hauri et al., 2009, 2013; et al., 2012; Bednaršek et al., 2012, 2014; be the norm more than 50% of the time Gruber et al., 2012). Waldbusser et al., 2015). Except for a few during summer by 2050 (Gruber et al., When gaseous CO2 dissolves in sea- studies at underwater seeps that vent 2012; Hauri et al., 2011, 2013). water, it reacts with the water to form CO2, this research has almost exclusively These changes in Pacific Northwest a weak acid (H2CO3), which dis- been carried out in laboratories, where ocean conditions have already resulted sociates to release a hydrogen ion saturation states were reduced with CO2 in major oyster seed production declines + – (H2CO3 H + HCO3) or reacts and held constant to match the expected (Barton et al., 2012; Washington directly to consume carbonate ions changes in surface ocean chemistry sev- State Blue Ribbon Panel on Ocean 2– – (H2CO3 + CO3 2HCO3 ). This acid- eral decades in the future. Acidification, 2012), and the shellfish ification process decreases the satura- Recent research shows a clear link industry has adopted a comprehensive tion state of aragonite (Ωarag) and calcite between natural variability in seawater strategy to understand, and mitigate, fur- (Ωcal), the two mineral forms of calcium Ωarag along the Oregon coast and com- ther impacts on commercial production carbonate that most bivalves use to form mercial production of Pacific oyster lar- (Washington State Blue Ribbon Panel on their shells. A variety of shell-forming vae in a hatchery setting, where food Ocean Acidification, 2012). Using fund- organisms have been shown to be highly and water temperatures are maintained ing from state, federal, and industry Oceanography | June 2015 147 groups, shellfish hatcheries have forged academia, federal and state scientists, and seed became prohibitively expensive, and partnerships with university research- the local management community flour- it became clear that growers could not ers, and are now some of the best instru- ished in ways that benefited all sectors; rely solely on inconsistent natural spawn- mented monitoring stations for collecting and the industry’s strategy to adapt as OA ing events (Dumbauld et al., 2011) to sup- carbonate chemistry measurements in the continues to advance globally. port their burgeoning industry (Gordon coastal zone. Industry uses these mon- and Blanton, 2001). itoring data as a real-time management PACIFIC NORTHWEST By the late 1970s, successful commer- tool to optimize water treatment systems SHELLFISH INDUSTRY cial hatcheries were established in the and improve commercial production of Shellfish have been harvested in the Pacific Northwest and began supplying oyster larvae. Additionally, hatcheries Pacific Northwest for thousands of years, billions of “eyed” (setting size) larvae to provide a perfect environment for mon- and commercial oyster farming has been growers each year. The three major com- itoring biological responses, given that an important cultural and economic part mercial hatcheries that currently supply typical hatchery protocols require rou- of coastal communities in the Northwest larvae to the West Coast shellfish indus- tine tracking and measurement of larval since the late 1800s. Today, shellfish farm- try are Whiskey Creek Shellfish Hatchery cohorts. The industry has capitalized on ing supports over $270 million in eco- (Netarts Bay, OR), Taylor Shellfish this by forging relationships with phys- nomic activity and over 3,000 family Hatchery (Dabob Bay, WA), and Coast iologists and geneticists to determine wage jobs in rural areas throughout the Seafoods Hatchery (Quilcene Bay, WA). the mechanisms behind larval mortality region. Although shellfish farms can be These hatcheries combine with smaller events and develop long-term strategies found throughout Oregon, Washington, hatcheries in Washington and Hawaii to adapt to further declines in water qual- Alaska, California, and Hawaii, most to produce 40–60 billion eyed larvae ity predicted for the coming decades. of the oysters harvested in the Pacific each year, and their 30 years of consis- More importantly,