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Yanxu Zhang ([email protected]) 1 , Daniel J. Jacob 1 , Stephanie Dutkiewitcz 2 , Helen M. Amos 1 , Michael S. Long 1 , Elsie M. Sunderland 1 1 School of Engineering and Applied Sciences, Harvard University; 2 Department of Earth, Atmospheric and Planetary Sciences, Massachusetts Institute of Technology Effects of ocean biogeochemistry on the fate of riverine mercury in the Arctic and global oceans 1. Introduction 3. Model Evaluation 2. Model Description 4. Reactivity of riverine Hg Rivers discharge 28 ± 13 Mmol a -1 of Hg to the ocean, comparable to inputs from global atmospheric deposition (10 - 29 Mmol a -1 ). Differences in the geochemical forms of Hg affect removal from the water column, redox processes, and bioavailability for methylation. Large spatial heterogeneity exists for riverine Hg discharge and its transport in the ocean. We use a 3-D model for oceanic Hg to investigate how ocean transport and interactions between Hg and natural organic matter affect the fate of river-derived Hg. We determine if the large observed summertime evasion from the Arctic Ocean can be reconciled with a smaller riverine source. References Amos H. M. et al., Global biogeochemical implications of mercury discharges from rivers and sediment burial, ES&T, 48 (16), 9514-9522, 2014. Dutkiewicz S. et al., Modeling the coupling of ocean ecology and biogeochemistry, GBC, 23, GB4017, doi: 10.1029/2008GB003405, 2009. Zhang Y. et al., Six centuries of changing oceanic mercury, GBC, doi:10.1002/2014GB004939, 2014. Blair N. E. and Aller R. C., The fate of terrestrial organic carbon in the marine environment, Ann Rev Mar Sci, 4, 401-423, 2012. Walsh J. P. and Nittrouer C. A., Understanding fine-grained river-sediment dispersal on continental margins, Mar Geo, 263 (1-4), 34-45, 2009. Dastoor A. P. and Durnford D. A., Arctic ocean: is it a sink or a source of atmospheric mercury? ES&T, 48, 1707-1717, 2014. 6.4% 1.6% 20% 72% Refractory Desorbing 40% 47% 13% Reversible Equilibrium Export to open ocean Evasion in coastal ocean Burial in shelves Burial in estuaries 6. Fate of Hg from Arctic rivers 0 0.2 0.4 0.6 0.8 1 2 3 4 5 6 7 8 9 10 5. River signal in the ocean 0.001 0.01 0.1 1 10 Sinking particles remineralization Euphotic zone Subsurface water k 1 k 3 k d k d Hg 0 Hg II Atmosphere Br oxida,on Hg 0 Hg II Hg 0 Hg II Hg P labile F dep +F river F evasion k 2 Photo8reduc,on k dark Hg P labile sedimentation k 4 k 3 k 4 Hg P refractory Hg P refractory k r k r F river A new oceanic Hg simulation with the MITgcm. 36 km resolution and 50 vertical layers for the Arctic Ocean. ×1° resolution and 23 vertical levels elsewhere. Coupled with the biogeochemical cycle of organic carbon and associated marine plankton ecosystem (the DARWIN project; Dutkiewicz et al., 2009). Present-day river inputs based on Amos et al. (2014). Hg II : 0.87±0.29 Mmol a -1 , Hg P : 27±13 Mmol a -1 . Fraction of Hg P refractory depends on suspended load (Blair and Aller, 2012). Three forms of Hg: elemental Hg (Hg 0 ), divalent Hg (Hg II ) and particle-bound Hg (Hg P ). Divide Hg P into labile and refractory pools. Hg biogeochemistry following Zhang et al. (2014). Burial of riverine particles in estuarine sediments using the typology system developed by Walsh and Nittrouer (2009). Different fractions (10-60%) of sediment exported beyond the estuarine environment. The model reasonably reproduces observed spatial patterns of surface ocean total Hg concentrations. The fate of riverine Hg is highly sensitive to the fraction of the Hg P pool that is specified as refractory in nature. Mid- and low-latitude riverine Hg P is dominant by refractory pool, otherwise, too high evasion unsupported by observations. Hg P from Arctic rivers is more labile because of the much lower suspended load and faster remineralization. Sea-ice melting is accelerated by the heat of freshwater discharge originated from melting snow over land in May and June. Piston velocity is increased over ocean partially covered by sea ice due to enhanced shear-stress and convection driven turbulence. 0.23 Mmol a -1 of Hg is needed from circumpolar rivers to reproduce atmospheric observations. Close to the upper limit by Amos et al. (2014) (0.1 ± 0.06 Mmol a -1 ), and the estimate by Dastoor and Durnford (2014) (0.25 Mmol a -1 ) based on Hg:DOC ratios. The two largest contributors: Yellow and Yangtze Rivers (33% of global total). Little (2.6%) is exported due to blockage of landmass. Reach of river plumes is enhanced by the Gulf Stream and the Kuroshio (e.g. 25% is exported from North American rivers). Hg from Arctic rivers preferentially accumulates in the coastal regions. pM pM
Transcript
Page 1: Effects of ocean biogeochemistry on the fate of …bgc.seas.harvard.edu/assets/zhang_icmgp2015.pdf• A new oceanic Hg simulation with the MITgcm. ! • 36 km resolution and 50 vertical

Yanxu Zhang ([email protected])1, Daniel J. Jacob1, Stephanie Dutkiewitcz2, Helen M. Amos1, Michael S. Long1, Elsie M. Sunderland1!1School of Engineering and Applied Sciences, Harvard University; 2Department of Earth, Atmospheric and Planetary Sciences, Massachusetts Institute of Technology !

Effects of ocean biogeochemistry on the fate of riverine mercury in the Arctic and global oceans !

1. Introduction! 3. Model Evaluation!

2. Model Description!

4. Reactivity of riverine Hg !

•  Rivers discharge 28 ± 13 Mmol a-1 of Hg to the ocean, comparable to inputs from global atmospheric deposition (10 - 29 Mmol a-1).

•  Differences in the geochemical forms of Hg affect removal from the water column, redox processes, and bioavailability for methylation.

•  Large spatial heterogeneity exists for riverine Hg discharge and its transport in the ocean.

•  We use a 3-D model for oceanic Hg to investigate how ocean transport and interactions between Hg and natural organic matter affect the fate of river-derived Hg.

•  We determine if the large observed summertime evasion from the Arctic Ocean can be reconciled with a smaller riverine source.

Corresponding to: [email protected] !

References!

•  Amos H. M. et al., Global biogeochemical implications of mercury discharges from rivers and sediment burial, ES&T, 48 (16), 9514-9522, 2014.

•  Dutkiewicz S. et al., Modeling the coupling of ocean ecology and biogeochemistry, GBC, 23, GB4017, doi:10.1029/2008GB003405, 2009.

•  Zhang Y. et al., Six centuries of changing oceanic mercury, GBC, doi:10.1002/2014GB004939, 2014. •  Blair N. E. and Aller R. C., The fate of terrestrial organic carbon in the marine environment, Ann Rev Mar Sci,

4, 401-423, 2012. •  Walsh J. P. and Nittrouer C. A., Understanding fine-grained river-sediment dispersal on continental margins,

Mar Geo, 263 (1-4), 34-45, 2009. •  Dastoor A. P. and Durnford D. A., Arctic ocean: is it a sink or a source of atmospheric mercury? ES&T, 48,

1707-1717, 2014.

6.4%1.6%

20%

72%

Refractory Desorbing

40%

47%

13%

Reversible Equilibrium

Export to open oceanEvasion in coastal oceanBurial in shelvesBurial in estuaries

6. Fate of Hg from Arctic rivers!

0 0.2 0.4 0.6 0.8 1 2 3 4 5 6 7 8 910

5. River signal in the ocean!

0.001 0.01 0.1 1 10

Sinking particles

remineralization Euphotic zone

Subsurface water

k1#

k3#kd#

kd#

Hg0 HgII

Atmosphere

Br#oxida,on#

Hg0 HgII

Hg0 HgII

HgP labile

Fdep#+#Friver#Fevasion#

k2#

Photo8reduc,on#

kdark#

HgP labile sedimentation

k4#

k3#k4#

HgP refractory

HgP refractory

kr#

kr#

Friver#

•  A new oceanic Hg simulation with the MITgcm. •  36 km resolution and 50 vertical layers for the Arctic Ocean. •  1°×1° resolution and 23 vertical levels elsewhere.

•  Coupled with the biogeochemical cycle of organic carbon and associated marine plankton ecosystem (the DARWIN project; Dutkiewicz et al., 2009).

•  Present-day river inputs based on Amos et al. (2014).

•  HgII: 0.87±0.29 Mmol a-1, HgP: 27±13 Mmol a-1.

•  Fraction of HgPrefractory

depends on suspended load (Blair and Aller, 2012).

•  Three forms of Hg: elemental Hg (Hg0), divalent Hg (HgII) and particle-bound Hg (HgP).

•  Divide HgP into labile and refractory pools.

•  Hg biogeochemistry following Zhang et al. (2014).

•  Burial of riverine particles in estuarine sediments using the typology system developed by Walsh and Nittrouer (2009).

•  Different fractions (10-60%) of sediment exported beyond the estuarine environment.

•  The model reasonably reproduces observed spatial patterns of surface ocean total Hg concentrations.

•  The fate of riverine Hg is highly sensitive to the fraction of the HgP pool that is specified as refractory in nature.

•  Mid- and low-latitude riverine HgP is dominant by refractory pool, otherwise, too high evasion unsupported by observations.

•  HgP from Arctic rivers is more labile because of the much lower suspended load and faster remineralization.

•  Sea-ice melting is accelerated by the heat of freshwater discharge originated from melting snow over land in May and June.

•  Piston velocity is increased over ocean partially covered by sea ice due to enhanced shear-stress and convection driven turbulence.

•  0.23 Mmol a-1 of Hg is needed from circumpolar rivers to reproduce atmospheric observations. Close to the upper limit by Amos et al. (2014) (0.1 ± 0.06 Mmol a-1), and the estimate by Dastoor and Durnford (2014) (0.25 Mmol a-1) based on Hg:DOC ratios.

•  The two largest contributors: Yellow and Yangtze Rivers (33% of global total). Little (2.6%) is exported due to blockage of landmass.

•  Reach of river plumes is enhanced by the Gulf Stream and the Kuroshio (e.g. 25% is exported from North American rivers).

•  Hg from Arctic rivers preferentially accumulates in the coastal regions.

pM

pM

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