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            <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/dataset/878527.rdf" xlink:actuate="onRequest">Dissolved Radium from Kolyma (Russia), Ellice (Canada), and Kodiak Island (USA) Rivers</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Charette, M. A., Bullock, E. J. (2022) Dissolved Radium from Kolyma (Russia), Ellice (Canada), and Kodiak Island (USA) Rivers. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2022-08-16 [if applicable, indicate subset used]. doi:10.26008/1912/bco-dmo.878527.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Minor Arctic Rivers - Dissolved Radium Dataset Description:  Methods and Sampling: &amp;lt;p&amp;gt;Samples were collected in the Ellice River&amp;amp;nbsp;in August and September 2017, the Kolyma River in June and September 2019, and the Buskin, Sustina, Matanuska, and Knik Rivers in September 2019 . The Ellice River is located in Nunavut, Canada, on the mainland side of the Canadian Arctic Archipelago. The Kolyma River is a major river in Siberia, draining into the East Siberian Sea and represents the largest Arctic river basin underlain by continuous permafrost. The Buskin River is located on Kodiak Island, AK, while the Sustina, Matanuska, and Knik Rivers drain into Cook Inlet near Anchorage, AK.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The samples were collected using either a bilge or well pump and the river water was passed through a 1 or 5 μm prefilter to remove suspended sediment before being filtered at &amp;amp;lt;1 L/min onto Mn-coated acrylic fiber. The fiber was rinsed with Ra-free MilliQ water to remove any salts or sediment, then partially dried.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Samples with low activities (&amp;amp;lt;0.4 dpm) were analyzed for 228Ra via 228Th ingrowth using a delayed coincidence counter (RaDeCC) (Moore, 2008), as described in Charette et al. (2015). Briefly, when 228Ra is extracted onto the Mn fiber, 228Th is extracted in parallel. Using the initial concentration of 228Th and the concentration of 228Th after 1 - 2 years, measured via RaDeCC, along with the decay constants of 228Th and 228Ra, the initial concentration of 228Ra can be calculated. Low activity samples were analyzed for 226Ra via 222Rn emanation (Key et al. 1979), as described in Charette et al. (2015). Fibers were placed in a fiber holder that was then flushed with He for 5 minutes at 250 mL/min, sealed, and left for two weeks before analysis via 222Rn ingrowth and scintillation counting. These two methods were used for low activity samples due to better method sensitivity than gamma counting (Charette et al., 2001), which was used for samples with high activities (&amp;amp;gt;0.4 dpm per sample). For this method, the fibers were ashed (880 °C, 16 h), homogenized, capped with epoxy resin, and left for &amp;amp;gt;3 weeks to obtain secular equilibrium between 226Ra and its daughter radionuclides. The samples were then counted in a well-type gamma spectrometer for 228Ra (via 228Ac at 338 keV) and 226Ra (via 214Pb at 351.9 keV) (Charette et al., 2001).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;When not specifically listed, errors are 10%.&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/825867.rdf" xlink:title="OCE-1736277" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1736277 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1736277</gmx:Anchor>
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&amp;lt;p&amp;gt;The samples were collected using either a bilge or well pump and the river water was passed through a 1 or 5 μm prefilter to remove suspended sediment before being filtered at &amp;amp;lt;1 L/min onto Mn-coated acrylic fiber. The fiber was rinsed with Ra-free MilliQ water to remove any salts or sediment, then partially dried.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Samples with low activities (&amp;amp;lt;0.4 dpm) were analyzed for 228Ra via 228Th ingrowth using a delayed coincidence counter (RaDeCC) (Moore, 2008), as described in Charette et al. (2015). Briefly, when 228Ra is extracted onto the Mn fiber, 228Th is extracted in parallel. Using the initial concentration of 228Th and the concentration of 228Th after 1 - 2 years, measured via RaDeCC, along with the decay constants of 228Th and 228Ra, the initial concentration of 228Ra can be calculated. Low activity samples were analyzed for 226Ra via 222Rn emanation (Key et al. 1979), as described in Charette et al. (2015). Fibers were placed in a fiber holder that was then flushed with He for 5 minutes at 250 mL/min, sealed, and left for two weeks before analysis via 222Rn ingrowth and scintillation counting. These two methods were used for low activity samples due to better method sensitivity than gamma counting (Charette et al., 2001), which was used for samples with high activities (&amp;amp;gt;0.4 dpm per sample). For this method, the fibers were ashed (880 °C, 16 h), homogenized, capped with epoxy resin, and left for &amp;amp;gt;3 weeks to obtain secular equilibrium between 226Ra and its daughter radionuclides. The samples were then counted in a well-type gamma spectrometer for 228Ra (via 228Ac at 338 keV) and 226Ra (via 214Pb at 351.9 keV) (Charette et al., 2001).&amp;lt;/p&amp;gt;

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References:
Giffin, C., A. Kaufman, W.S. Broecker (1963). Delayed coincidence counter for the assay of actinon and thoron. J. Geophys. Res., 68, pp. 1749-1757.
Moore, W.S., R. Arnold (1996). Measurement of 223Ra and 224Ra in coastal waters using a delayed coincidence counter. J. Geophys. Res., 101 (1996), pp. 1321-1329.
Charette, Matthew A.; Dulaiova, Henrieta; Gonneea, Meagan E.; Henderson, Paul B.; Moore, Willard S.; Scholten, Jan C.; Pham, M. K. (2012). GEOTRACES radium isotopes interlaboratory comparison experiment. Limnology and Oceanography - Methods, vol 10, pg 451.</gco:CharacterString>
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