Assessing the Permanence of Blue Carbon Sinks

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Assessing the Permanence of Blue Carbon Sinks with Rising Sea Levels Gail L. Chmura and Dante D. Torio Department of Geography, McGill University and Global Environmental and Climate Change Centre Montreal, Quebec, Canada E mail: gail.chmura@mcgill.ca

Over millenia salt marshes & mangroves have vertically accumulated soil and, at the same time, expanded laterally both seaward and inland. Redfield 1972

For decades we have known that salt marshes & mangroves vertically accumulated soil and at the same time expanded laterally both seaward and inland. Marsh surface meters from inland marsh edge ~1,600 years ago ~3,000 years ago Redfield 1972 Shaw & Ceman, 1999 Marsh climbed 5.5 m and migrated 65 m inland in ~1,400 years Rate of vertical accretion ~4 mm/yr Rate of lateral accretion ~5 cm/yr on an 8.5% slope

This was possible under past, slower rates, but vegetation on the seaward edge may not be able to tolerate increased periods of submergence associated with higher rates of rise resulting in loss of the active carbon sink there. Redfield 1972 Predictions of increased sea level in 100 years: 40 cm from paleo example 59 cm IPCC : Bindoff et al. 2007 190 cm Vermeer & Rahmstorf 2009 224 cm Grinsted et al. 2010

Sustainability of tidal marshes and mangroves may require that they shift inland with rising sea level. This only will be possible if inland barriers do not pose a coastal squeeze elevation increase future present lateral accretion terrestrial soil barrier future present terrestrial soil

The narrow vertical elevation range of tidal wetlands requires that elevation models used to predict response to sea level rise have fine vertical resolution... Tidal amplitudes and elevation range of vegetation in selected salt marshes elevation range of vegetation country coast tidal amplitude (m) (m) source Italy Venice Lagoon 0.7 0.2 Silvestri et al. 2005 USA Palo Alto, California 2.6 1.2 Hinde 1954 Spain Ortigueira & Ldrido Rivers 3.6 2.4 Sánchez et al. 1996 Canada Bay of Fundy 6.0 >3.0 Chmura et al. 1997 Contour intervals of topographic maps are 3 10 m Vertical resolution of LIDAR can be as fine as 0.05 m

LIDAR (Light Detection and Ranging Systems) How it works: Pulses sent down from a laser mounted in a plane...along with a GPS, an inertial measurement unit, and a computer Receiver unit in the plane collects the returning energy A series of filters must be employed to isolate the vegetation surface from the ground surface Contract a specialized firm to fly and collect the LIDAR, and tell them to fly at LOW TIDE! Post processing can be contracted to the same firm or done by research collaborators (recommended involve them from the beginning)

Comparison of costs of obtaining Lidar data vs. collecting field data with a real time kinematic Geographical Positioning System (RTK GPS), based upon US $ in 2005 (Rogers et al. 2007). Type Cost/Acre Points/Acre Cost/Point Lidar $2.34 1396 $0.00 RTK GPS $287.00 62.69 $5.44 Dante using RTK GPS The RTK GPS is labour intensive, requires specialized equipment and post processing to relate field data to an appropriate datum.

Here Dante has used LIDAR to create a digital elevation model & predict future tidal floodplains under varied scenarios of sea level rise. This is useful for many types of planning.

0 20 0.5 m 1 m % Coastal Squeeze (increasing threat) 20 40 40 60 60 80 80 100 1.5 m 2 m 2.5 m Combined with remotely sensed data, that reveals characteristics such as impervious surfaces, we can determine how intensity of squeeze will vary around a wetland under different sea level rise scenarios. Dante has incorporated measurements of slope and imperviousness (proxy for development) to create a Coastal Squeeze Index that can be applied to any tidal wetland.

With LIDAR available we not only can assess the permanence of a blue carbon sink under varied sea level threats, but use the Coastal Squeeze Index to compare sites and prioritize targets for preservation, restoration, and best investments in carbon offsets. Coastal Squeeze Index Increasing Threat 0.4 0.3 0.3 0.2 0.2 0.1 0.1 0.0 Wells Marsh KNP Marsh Portland Marsh 0 50 100 150 200 250 Sea Level Increase (cm) The LIDAR digital elevation model can also be used to assess loss at the seaward edge if we know local accretion rates.

Only LIDAR has the required resolution It is expensive, but valuable for many planning purposes to: Assess flooding risk Assess increased exposure to coastal erosion Determine which portions of infrastructure and which sectors of coastal communities are threatened Reach stakeholders, as mapping scale can fit property boundaries

Thank you! Questions? (This is the techy half of the team, Dante Torio.)