4 TH ANNUAL CAPE COASTAL CONFERENCE Acidification impacts on larval shellfish Daniel C. McCorkle Senior Scientist Department of Geology and Geophysics Woods Hole Oceanographic Institution
4 TH ANNUAL CAPE COASTAL CONFERENCE Daniel C. McCorkle Anne L. Cohen (WHOI) Lisa M. Milke (NOAA-NMFS Milford CT) Meredith White (WHOI,Mook Sea Farm) Lauren Mullineaux (WHOI) Ryan Petit Cailan Sugano Gabrielle Fignar Scott Lindell (MBL)
Ocean acidification culture experiments at WHOI larval bay scallops (Argopecten irradians) larval sea scallops (Placopecten magellanicus) 10 day, 100 µm
Why do we care? National - fisheries managers use quantitative models to help set appropriate harvest levels models which include linked environmental, biological, and economic components. > $550M / yr Local - Coastal managers need to understand the impacts of changes in coastal water quality on coastal ecosystems (e.g., nutrient pollution (eutrophication), which can drive acidification of estuaries).
Broad questions: Are shellfish vulnerable to ocean acidification, and if so, over what range of ph? Are particular life stages more/less vulnerable? Are particular species more/less vulnerable? Does food availability influence the impact of acidification?
Today: Laboratory culture experiments at WHOI to assess bay scallop and sea scallop larval sensitivity to acidification. Two treatments in each experiment: acidification (elevated carbon dioxide) feeding rate Two metrics to assess impacts: survival frequency of shell deformities Elevated carbon dioxide levels acidification has negative impacts on larval survival, and on the frequency of shell-shape abnormalities (deformities).
Triplicate 15 L buckets Initial stocking density = 10-30 embryos / ml Water temp ~ 25 C, 15 C Sea scallop broodstock from Cape Cod bay (12 males, 12 females) 2 3 carbon dioxide levels (high CO 2 = low ph) Daily feeding at two rates
Scanning electron microscope imaging (Marine Biological Laboratory) to determine shell size and to quantify shell shape abnormalities. Survival light microscopy to count shells with protoplasm (live) and without (dead)
Types of Shell Deformities Normal D shell Sea scallop at 10 days
Types of Shell Deformities Normal D shell Expectation: Larvae with deformed shells Sea scallop don t at survive. 10 days
Exposure to high CO 2 ( = low ph) reduces survival of larval bay scallops Age of culture inoculation Age at which switch occurs High ph Low ph White et al. (submitted)
100 2014 Bay Scallop Shell Deformities Exposure to high CO 2 ( = low ph) increases the frequency of larval bay scallop shell deformities Percent shell deformities 80 60 40 20 0 Low Food High Food Low Food High Food Ambient pco 2 2200 ppm pco 2 pco 2 Ambient High ph 8.00 7.40 Sugano et al. (2015)
Exposure to high CO 2 reduces survival of larval sea scallops
Exposure to high CO 2 increases the frequency of larval bay scallop shell deformities Percent deformed shells 100 90 80 70 60 50 40 30 20 10 0 2015 Sea scallop 10 day percent deformed shells Low food High food pco 2 Ambient Medium High ph 7.99 7.76 7.53 Assumption: Larvae with deformed shells don t survive.
Elevated carbon dioxide levels acidification has negative impacts on larval survival, and on the frequency of shell deformities.
Some outstanding questions, in order to use these results in fisheries models: Do larval shell deformities actually lead to mortality? Is the adult population (fishery resource) sensitive to larval mortality? Not necessarily, under current conditions. But what if larval mortality increases dramatically? Can high food availability offset negative impacts of elevated carbon dioxide? Would reduced food availability exacerbate acidification impacts?
Future culture studies (WHOI / NMFS): Are there parental influences on acidification impacts on bivalves? If so, what is the natural range of sensitivity to acidification? Is this variability genetic, or linked to parental nutrition, or? Does this variability offer the prospect of adaptation, or breeding (for hatchery species)?
An introduction to ocean acidification Carbon dioxide in the atmosphere (Mauna Loa, HI) http://scrippsco2.ucsd.edu mauna_loa_record
400,000-year Antarctic ice core record of atmospheric CO 2 CO 2 concentration (ppm v) 400 350 300 250 200 150 400 The current rate of CO 2 increase is much faster than natural rates. 300 200 100 A ge of entrapped air (kybp) Natural cycles in atmospheric carbon dioxide + fossil fuel combustion, deforestation, 0 Today Pre-industrial atmosphere ~ 280 ppmv Last Glacial Maximum atmosphere (18-21 kybp) ~ 180 ppmv Barnola et al., 1999
Current budget for CO 2 from human activities Removal of CO 2 from the atmosphere is good, but addition to the ocean is not
CO 2 Ocean acidification the chemistry of carbon dioxide in seawater CO 2(g) Atmosphere CO 2(aq) + H 2 O H 2 CO 3 * Ocean H 2 CO 3 * HCO 3 - + H + HCO 3 - CO 3 2 - + H + As CO 2 is added to water, H + is produced: ph decreases ( = acidification), and CO 3-2 (carbonate ion) decreases
Ocean Acidification is observable - the ph of the surface ocean is dropping. Atmospheric CO 2 Seawater CO 2 Seawater ph Open Pacific: 20-year decrease, and annual cycle in ph, less than 0.05 units
Monthly discrete samples just before low tide from 4 stations (NERR system-wide monitoring program (SWMP)) O 2 data from continuous monitoring stations (NERR CDMO Centralized Data Management Office) Childs River Menauhant Focus on: Menauhant (most like inflow water) Childs River (most strongly modified).
- Strong seasonality of ph, pco 2. - Most extreme in Childs River: Low (volume)/(bottom area) Low flushing rate ph(total) values well below 7.5 (all sites below 7.8) Childs River summer: pco 2 above 2000 ppmv (all sites 100s of ppm above atm) Calculated Ω, ph and pco 2, from measured Alkalinity and DIC and temperature
ph (total scale) O xygen (mm ol/l) Larvae affected by multiple stressors. W aquoit B ay 2008-2010 400 M enauhant Childs River 300 200 100 0 1/1/08 1/1/09 1/1/10 1/1/11 1/1/12 8.0 7.5 7.0 1/1/08 1/1/09 1/1/10 1/1/11 1/1/12 Low ph and high pco 2 linked to low dissolved oxygen. Driven by organic matter decomposition in sediments (which produces CO 2, and groundwater discharge. Natural and anthropogenic contributions to both processes (e.g., eutrophication). As atmospheric pco 2 increases, the ph and Ω(ar) at a given oxygen concentration will drop. ph (total, calc) 8.5 8.0 7.5 Is acidification the biggest threat to shellfish health (recruitment and growth)? Or low oxygen? Or combined impacts? 7.0 0 100 200 300 400 O xygen (mm ol/l) O 2 data from WBNERR continuous monitoring stations (NERR CDMO Centralized Data Management Office)
Exposure to high CO 2 reduces survival 12 hour switch Age of culture inoculation Age at which switch occurs White et al. (submitted)
Shell size impacted by CO 2 level during the initial calcification (12-24 hr). They don t catch up. 24 Hour Switch White et al. (submitted)
2011 surf clam experiment, day 6 50 40 380 ppm v 91.1 +/- 11.2 mm 2011 Surf C lam Size distribution - Day 6 Shell length histograms reveal a range of responses for each treatment (each CO 2 level) N um ber 30 20 10 0 60 70 80 90 100 110 120 130 140 150 Average size decreases as CO 2 increases, but even the high-co 2 treatments include some large individuals. 50 40 1200 ppm v 90.8 +/- 12.1 mm Suggests possibility of selection for CO 2 tolerance: N um ber 30 20 10 0 Natural selection (in the field) likely to be too slow. (rate of CO 2 increase) N um ber 50 40 30 20 10 60 70 80 90 100 110 120 130 140 150 2200 ppm v 86.0 +/- 11.9 mm Active selection (in hatcheries) may help commercial species. (but not whole ecosystems) 0 60 70 80 90 100 110 120 130 140 150 Shell length (mm) Most fundamental solutions are to cut CO 2 emissions, and reduce nutrient pollution! McCorkle and Cohen (WHOI), Milke and Widman (NOAA/NMFS)
The variability is not just seasonal. WBNERR dissolved oxygen data show strong daily cycles. Since [O 2 ] and ph are linked, this suggests that we re missing a lot with only monthly sample resolution for carbonate chemistry. WBNERR continuous monitoring system oxygen data Discrete sample date 13 August 2009
Automated in situ ph and DIC analyses show daily cycles as large as the season cycles. (Martin, Sayles, McCorkle, & Weidman) pco2 Ω DIC ph Shading shows daylight We ve missed a lot with monthly sample resolution for carbonate chemistry! What factors are most important to the health of the bay, or its shellfish? Minimum values (ph, O 2 ); sustained values; variability
Rising atmospheric CO 2 due to human activities IPCC 2001 Today s atmosphere (~ 400 ppmv) is already 35 % (~120 ppmv) higher than pre-industrial pco 2. The current rate of CO 2 increase is much faster than natural rates.