Why the Strait of Georgia is not a Dead Zone. Sophie Johannessen, Diane Masson and Rob Macdonald DFO Institute of Ocean Sciences, Sidney, B.C.

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Why the Strait of Georgia is not a Dead Zone Sophie Johannessen, Diane Masson and Rob Macdonald DFO Institute of Ocean Sciences, Sidney, B.C.

Google Earth has awarded the Strait of Georgia a dead fish. Based on Diaz classification: Eutrophic, hypoxic, dead zone http://www.vims.edu/research/topics/dead_zones/

Nutrient concentrations are high in the Strait, but not due to local human activities. Sutton et al., in press, Biogeosciences

Dissolved oxygen is declining in coastal seas around the world. -imported from open ocean -warming -local discharge of wastewater / agricultural runoff (eutrophication)

O 2 has declined in the Strait of Georgia since the 1970s. [O2] (ml/l) SOUTH May/June 200m-bottom 6 4 2 0 1950 1970 1990 2010 SOUTH August 200m-bottom [O2] (ml/l) 4 2 0 1950 1970 1990 2010 Oxygen was sometimes lower 1951-1970 than in 1980s

Thresholds of Tolerance Johannessen & Macdonald, 2009, Climate Research Adapted from: Vaquer-Sunyer & Duarte 2008. PNAS and Gilbert et al. 2007 le Naturaliste Canadien

0 100 Seasonal oxygen profiles (2001-2009) Deep Juan de Fuca Strait hypoxic seasonally Deep SoG approaches hypoxia oxygen (ml/l) 0 2 4 6 8 0 2 4 6 8 SoG North SoG South Depth (m) 200 300 0 100 200 Har o Strai t JdeF 300 [O 2 ] conversion: 1 ml/l = 45 mmol/l

Assess seasonal and short-term variability in oxygen Using moorings Fraser River Haro Strait Moorings

Moorings 2008-2012 50 m 51.6 m 53.2 m 150 m bottom +50 m bottom +12.6 m bottom +10 m 310 m sediment traps fluorometer Seabird CTD RCM current meter Sonde O 2 ADCP RCM current meter RBR O 2 and ph Anchor (train wheel)

The concentration of oxygen at 300m at the northern and southern moorings, April 2009 November 2011 [oxygen] (ml/l) 6 4 2 renewal (May) 2009 2010 2011 renewal (Aug.) Oxygen drawdown in situ (oxidation ~ -0.5 ml/l)) north south renewal (May) renewal (Aug.) 0 followed by a diffusive m j j a mixing: s o n d eddy j f m a m j j a s coeff. 1.1 x10-3 m 2 s -1 Masson, 2002, ECSS o n d j f m a m j j a s o n Johannessen et al., in press, Limnology and Oceanography

Why the Strait of Georgia is different from the Gulf of Mexico Johannessen et al., in press, Limnology and Oceanography Figure 8

Possible explanations for O 2 decline Increased O 2 Drawdown within the Strait of Georgia Higher influx from coast due to wastewater, pulp mills etc. Higher Productivity (respiration) Higher proportion fluxes to bottom (grazing mismatch) Enhanced O 2 drawdown at bottom of SofG because of warming/microbial activity (benthic demand) Decreased O 2 in incoming water Increased T Decreased mixing in Haro Strait O 2 decline in upwelled source water

Is the flux of organic C into the Strait increasing? An increase of about 40g C/m 2 /year required over 40 years at 200m depth Municipal wastewater: ~ 2 gc/m 2 /year total at the surface Pulp mills reduced biochemical O 2 demand by 88% over 1990s Increased organic C flux from local discharges cannot explain the decline in O 2.

Primary production and remineralization Primary production: ~ 280 gc/m 2 /year (Harrison et al., 1983) at the surface. But ~96% organic matter remineralized before reaches bottom An increase of 40 gcm -2 yr -1 at 300 m implies an increase of ~1000 gcm -2 yr -1 Increased primary production inside the Strait of Georgia cannot explain the decline in O 2.

The concentration of oxygen in upwelled water at 125 m at the mouth of Juan de Fuca Strait (in summer) has decreased at 0.02 ml/l / year since 1978. Crawford & Peña, 2013 Atmosphere-Ocean.

The concentration of oxygen in upwelled water at 125 m at the mouth of Juan de Fuca Strait (in summer) Extremely low O 2 : Leverage almost gone Crawford & Peña, 2013 Atmosphere-Ocean.

Model: Anoxic Juan de Fuca inflow would reduce deep SoG O 2 to ~ 2 ml/l 100 200 300 5 Depth (m) 400 100 200 0 100 200 300 400 4 O 2 (mll -1 ) 3 2 1 0 300 400 0 100 200 300 400 Distance from mouth of Juan de Fuca (km) Johannessen, Masson and Macdonald, submitted Figure 7

Conclusions 1. Deep-water renewal, tidal mixing and diffusion largely govern the concentration of oxygen in the deep Strait. (balance with remineralization) 2. Dissolved oxygen is declining in the deep Strait of Georgia, due to decline in upwelled source water, and is approaching biological tolerance thresholds. 3. Even if source water becomes anoxic, the deep Strait of Georgia likely will not because of mixing in Haro Strait. The Strait of Georgia is not a Dead Zone and is unlikely to become one.

Field and lab Cynthia Wright Mary O Brien Linda White Tom Juhasz Darren Tuele Dave Spear Lucius Perreault Ian Belliveau Acknowledgements Peter Chandler Vera Pospelova Pamela Dinn Nina Nemcek Melissa Hennekes Modelling John Morrison Figures/Interp. Jill Sutton Olivier Riche Rich Pawlowicz Trish Kimber Data VENUS The officers and crew of the CCGS Vector; the community who collected long-term data Funding: Metro Vancouver Ambient Monitoring Program and DFO Strait of Georgia Ecosystem Research Initiative