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Smithsonian at the Poles: Contributions to International Polar

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274 SMITHSONIAN AT THE POLES / DUNTON, SCHONBERG, AND FUNK<br />

Physiochemical Parameters<br />

Temper<strong>at</strong>ure ( o C), salinity (‰), dissolved oxygen (%<br />

and mg L �1 ) pH, and w<strong>at</strong>er depth (m), were measured<br />

using a YSI D<strong>at</strong>a Sonde (YSI Inc., Yellow Springs, Ohio,<br />

USA).<br />

PERMANENT SITES<br />

Underw<strong>at</strong>er Irradiance<br />

In addition <strong>to</strong> <strong>the</strong> synoptic sampling, we established<br />

eight permanent sites for collection of long-term d<strong>at</strong>a.<br />

Continuous underw<strong>at</strong>er PAR measurements were collected<br />

<strong>at</strong> three sampling sites (DS-11, E-1, and W-1) in<br />

<strong>the</strong> Boulder P<strong>at</strong>ch study area (Figure 2) and terrestrial<br />

PAR measurements <strong>at</strong> one coastal loc<strong>at</strong>ion (Endicott Island).<br />

These sites have been <strong>the</strong> focus of previous longterm<br />

moni<strong>to</strong>ring efforts; measurements of PAR and<br />

kelp growth are reported in published liter<strong>at</strong>ure (Dun<strong>to</strong>n,<br />

1990). Site DS-11, established as a reference site,<br />

has been a primary research site for <strong>the</strong> Boulder P<strong>at</strong>ch<br />

since 1978. This site lies well outside <strong>the</strong> area most likely<br />

impacted by sediment plumes origin<strong>at</strong>ing from <strong>the</strong> pro-<br />

FIGURE 2. The project study area. The indic<strong>at</strong>ed sites are his<strong>to</strong>rical<br />

Boulder P<strong>at</strong>ch st<strong>at</strong>ions th<strong>at</strong> have been visited repe<strong>at</strong>edly since 1984.<br />

During summers 2004, 2005, and 2006, long-term light was measured<br />

<strong>at</strong> sites DS-11, E-1, and W-1; kelp blade length d<strong>at</strong>a were also<br />

collected <strong>at</strong> <strong>the</strong>se sites.<br />

posed Liberty Project, including construction of a buried<br />

pipeline and S<strong>to</strong>ckpile Zone 1 (Ban et al., 1999). All three<br />

Boulder P<strong>at</strong>ch sites are loc<strong>at</strong>ed on seabed characterized<br />

by �25% rock cover. Sites were chosen based on ei<strong>the</strong>r<br />

<strong>the</strong>ir sou<strong>the</strong>rn-most loc<strong>at</strong>ion in <strong>the</strong> Boulder P<strong>at</strong>ch (W-1,<br />

E-1), existence of his<strong>to</strong>rical PAR d<strong>at</strong>a (W-1, E-1, and DS-<br />

11), and <strong>the</strong>ir likelihood of being impacted by oil and gas<br />

development through dredging activities associ<strong>at</strong>ed with<br />

pipeline or island construction.<br />

Underw<strong>at</strong>er d<strong>at</strong>a were collected using LI-193SA spherical<br />

quantum sensor (for scalar measurements) connected<br />

<strong>to</strong> a LI-1000 d<strong>at</strong>alogger (LI-COR Inc., Lincoln, Nebraska,<br />

USA) <strong>at</strong> each site. Sensors were mounted on PVC poles and<br />

positioned just above <strong>the</strong> kelp canopy <strong>to</strong> prevent fouling<br />

or shading by kelp fronds. Instantaneous PAR measurements<br />

were taken <strong>at</strong> 1 min intervals and integr<strong>at</strong>ed over<br />

1 h periods. Coincident surface PAR measurements were<br />

taken with LI-190SA terrestrial cosine sensor connected <strong>to</strong><br />

LI-1000 d<strong>at</strong>alogger loc<strong>at</strong>ed on Endicott Island.<br />

Kelp Elong<strong>at</strong>ion<br />

At each of <strong>the</strong> nine dive sites (depth range 5– 7 m)<br />

within <strong>the</strong> Boulder P<strong>at</strong>ch (DS-11, Brower-1, E-1, E-2, E-3,<br />

L-1, L-2, W-1, and W-3), SCUBA divers collected 15– 30<br />

individual specimens of Laminaria solidungula <strong>at</strong>tached<br />

<strong>to</strong> large cobbles and boulders in summers 2004, 2005,<br />

and 2006. Samples were placed in pre-labeled black bags,<br />

transported <strong>to</strong> Endicott, and processed. Blade segments<br />

from every specimen, which corresponded <strong>to</strong> one year’s<br />

growth (Dun<strong>to</strong>n, 1985), were measured and recorded <strong>to</strong><br />

produce a recent (3– 4 yr) growth record of linear blade<br />

expansion <strong>at</strong> each site. Blades measured in summer refl ect<br />

growth during both <strong>the</strong> present and previous calendar<br />

year since more than 90% of a kelp’s frond expansion occurs<br />

between November and June under nearly complete<br />

darkness (Dun<strong>to</strong>n and Schell, 1986). Linear growth in L.<br />

solidungula from <strong>the</strong> Boulder P<strong>at</strong>ch is heavily dependent<br />

on pho<strong>to</strong>syn<strong>the</strong>tic carbon reserves th<strong>at</strong> accumul<strong>at</strong>e during<br />

<strong>the</strong> previous summer in proportion <strong>to</strong> <strong>the</strong> underw<strong>at</strong>er light<br />

environment. A growth year (GWYR) is dict<strong>at</strong>ed by <strong>the</strong><br />

form<strong>at</strong>ion of a new blade segment, which begins in mid-<br />

November every year and is defi ned by <strong>the</strong> summer th<strong>at</strong><br />

precedes new blade form<strong>at</strong>ion (e.g., basal blade growth<br />

measured in summer 2007 depicts GWYR 2006).<br />

Kelp Biomass<br />

Frond lengths of Laminaria solidungula plants were<br />

measured <strong>at</strong> W-3, E-1, E-3, and DS-11 along four 25 m

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