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        <gco:CharacterString>Water-column total Th-234 the 2013 U.S. GEOTRACES EPZT cruise. Dataset Description: &amp;lt;p&amp;gt;Water-column total Th-234 with 4 L method from the 2013 U.S. GEOTRACES EPZT cruise.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;U-238 from U-salinity relationship was also determined but not reported in this dataset. These data can be made available upon request from the PI and/or dataset contact. Methods are described below.&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Sampling details:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
Super stations: approximately 28 discrete total Th-234 samples were collected throughout the water column, a minimum of 12 depths were chosen in the upper 1000 m.&amp;lt;br /&amp;gt;
Full stations: approximately 20 discrete total Th-234 samples were collected throughout the water column, a minimum of 12 depths were chosen in the upper 1000 m.&amp;lt;br /&amp;gt;
Hemi station: 16 discrete total Th-234 samples were collected from the upper 3000 m.&amp;lt;br /&amp;gt;
Demi and Shelf stations: 12 discrete total Th-234 samples were collected, at shelf stations depths spanned the entire water column, at demis the upper 1000 m was sampled.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The shipboard procedures follow Pike et al. (2005).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Thorium-234:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
Thorium-234 was determined by the widely-adopted 4 L method. Generally, shallow (&amp;amp;lt; 1000 m) samples were collected from the ODF Rosette and deep samples (&amp;amp;gt;1000 m) were collected from niskin bottles hung above in situ pumps. Data are decay corrected to the mid-point time between when bottles 1 and 12 were fired for shallow casts, when the messenger was dropped for deep casts, and the time of collection for underway samples. All underway samples were collected directly from the ship’s underway system in the aft ODF wet lab (denoted as bottle 99, cast 0, depth 3 m). All data have been recovery-corrected using the Th-230/Th-229 recovery method (see references below) to account for any loss of sample material during processing. All samples were analyzed using RISO Laboratory Anti-coincidence Beta Counters, using a helium/1% butane mixture. Overall method efficiency was determined by minimizing the percent difference between mean U-238 and Th-234 values for samples from &amp;amp;gt;1000 m to &amp;amp;gt; 500 m from the bottom (45.72 %). Only stations 6 through 16 and 23 through 36 were used to determine method efficiency so as not to include samples with potential coastal or hydrothermal influences.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Uranium-238:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
Value and uncertainty from equation derived in Owens et al. (2011)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;U-238 (dpm/L) = (Salinity * 0.0786) – 0.315&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Salinity was measured on board the ship by the Scripps Ocean Data Facility (ODF).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;For more information on methods and intercalibration procedures, refer to the &amp;lt;a href=&amp;quot;https://datadocs.bco-dmo.org/docs/302/geotraces/GEOTRACES_EPZT/buesseler/data_docs/0000-0001-7362-8796-TN303-multiple-param-intercal-report.pdf&amp;quot; target=&amp;quot;_blank&amp;quot;&amp;gt;GEOTRACES Intercalibration Report&amp;lt;/a&amp;gt;&amp;amp;nbsp;(PDF) Supplemental File.&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/643215.rdf" xlink:title="OCE-1232669" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1232669 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1232669</gmx:Anchor>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/643216.rdf" xlink:title="OCE-1231211" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1231211 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1231211</gmx:Anchor>
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* To evaluate the sources, sinks, and internal cycling of these species and thereby characterize more completely the physical, chemical and biological processes regulating their distributions, and the sensitivity of these processes to global change; and
* To understand the processes that control the concentrations of geochemical species used for proxies of the past environment, both in the water column and in the substrates that reflect the water column.

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                            <gco:CharacterString>&lt;p&gt;&lt;strong&gt;From the NSF Award Abstract&lt;/strong&gt;&lt;br /&gt;
The mission of the International GEOTRACES Program (&lt;a href=&quot;https://www.geotraces.org/&quot; target=&quot;_blank&quot;&gt;https://www.geotraces.org/&lt;/a&gt;), of which the U.S. chemical oceanography research community is a founding member, is &quot;to identify processes and quantify fluxes that control the distributions of key trace elements and isotopes in the ocean, and to establish the sensitivity of these distributions to changing environmental conditions&quot; (GEOTRACES Science Plan, 2006). In the United States, ocean chemists are currently in the process of organizing a zonal transect in the eastern tropical South Pacific (ETSP) from Peru to Tahiti as the second cruise of the U.S.GEOTRACES Program. This Pacific section includes a large area characterized by high rates of primary production and particle export in the eastern boundary associated with the Peru Upwelling, a large oxygen minimum zone that is a major global sink for fixed nitrogen, and a large hydrothermal plume arising from the East Pacific Rise. This particular section was selected as a result of open planning workshops in 2007 and 2008, with a final recommendation made by the U.S.GEOTRACES Steering Committee in 2009. It is the first part of a two-stage plan that will include a meridional section of the Pacific from Tahiti to Alaska as a subsequent expedition.&lt;/p&gt;
&lt;p&gt;This award provides funding for management of the U.S.GEOTRACES Pacific campaign to a team of scientists from the University of Southern California, Old Dominion University, and the Woods Hole Oceanographic Institution. The three co-leaders will provide mission leadership, essential support services, and management structure for acquiring the trace elements and isotopes samples listed as core parameters in the International GEOTRACES Science Plan, plus hydrographic and nutrient data needed by participating investigators. With this support from NSF, the management team will (1) plan and coordinate the 52-day Pacific research cruise described above; (2) obtain representative samples for a wide variety of trace metals of interest using conventional CTD/rosette and GEOTRACES Sampling Systems; (3) acquire conventional JGOFS/WOCE-quality hydrographic data (CTD, transmissometer, fluorometer, oxygen sensor, etc) along with discrete samples for salinity, dissolved oxygen (to 1 uM detection limits), plant pigments, redox tracers such as ammonium and nitrite, and dissolved nutrients at micro- and nanomolar levels; (4) ensure that proper QA/QC protocols are followed and reported, as well as fulfilling all GEOTRACES Intercalibration protocols; (5) prepare and deliver all hydrographic-type data to the GEOTRACES Data Center (and US data centers); and (6) coordinate cruise communications between all participating investigators, including preparation of a hydrographic report/publication.&lt;/p&gt;
&lt;p&gt;Broader Impacts: The project is part of an international collaborative program that has forged strong partnerships in the intercalibration and implementation phases that are unprecedented in chemical oceanography. The science product of these collective missions will enhance our ability to understand how to interpret the chemical composition of the ocean, and interpret how climate change will affect ocean chemistry. Partnerships include contributions to the infrastructure of developing nations with overlapping interests in the study area, in this case Peru. There is a strong educational component to the program, with many Ph.D. students carrying out thesis research within the program.&lt;/p&gt;
&lt;p&gt;&lt;em&gt;Figure 1. The 2013 GEOTRACES EPZT Cruise Track. [click on the image to view a larger version]&lt;/em&gt;&lt;br /&gt;
&lt;a href=&quot;http://dmoserv3.whoi.edu/data_docs/GEOTRACES/EPZT/GEOTRACES_EPZT_TN303_CruiseTrack.png&quot; target=&quot;_blank&quot;&gt;&lt;img alt=&quot;&quot; src=&quot;https://datadocs.bco-dmo.org/d3/data_docs/GEOTRACES/EPZT/GEOTRACES_EPZT_TN303_CruiseTrack.png&quot; /&gt;&lt;/a&gt;&lt;/p&gt;</gco:CharacterString>
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Super stations: approximately 28 discrete total Th-234 samples were collected throughout the water column, a minimum of 12 depths were chosen in the upper 1000 m.&amp;lt;br /&amp;gt;
Full stations: approximately 20 discrete total Th-234 samples were collected throughout the water column, a minimum of 12 depths were chosen in the upper 1000 m.&amp;lt;br /&amp;gt;
Hemi station: 16 discrete total Th-234 samples were collected from the upper 3000 m.&amp;lt;br /&amp;gt;
Demi and Shelf stations: 12 discrete total Th-234 samples were collected, at shelf stations depths spanned the entire water column, at demis the upper 1000 m was sampled.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;The shipboard procedures follow Pike et al. (2005).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Thorium-234:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
Thorium-234 was determined by the widely-adopted 4 L method. Generally, shallow (&amp;amp;lt; 1000 m) samples were collected from the ODF Rosette and deep samples (&amp;amp;gt;1000 m) were collected from niskin bottles hung above in situ pumps. Data are decay corrected to the mid-point time between when bottles 1 and 12 were fired for shallow casts, when the messenger was dropped for deep casts, and the time of collection for underway samples. All underway samples were collected directly from the ship’s underway system in the aft ODF wet lab (denoted as bottle 99, cast 0, depth 3 m). All data have been recovery-corrected using the Th-230/Th-229 recovery method (see references below) to account for any loss of sample material during processing. All samples were analyzed using RISO Laboratory Anti-coincidence Beta Counters, using a helium/1% butane mixture. Overall method efficiency was determined by minimizing the percent difference between mean U-238 and Th-234 values for samples from &amp;amp;gt;1000 m to &amp;amp;gt; 500 m from the bottom (45.72 %). Only stations 6 through 16 and 23 through 36 were used to determine method efficiency so as not to include samples with potential coastal or hydrothermal influences.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Uranium-238:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
Value and uncertainty from equation derived in Owens et al. (2011)&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;U-238 (dpm/L) = (Salinity * 0.0786) – 0.315&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Salinity was measured on board the ship by the Scripps Ocean Data Facility (ODF).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;For more information on methods and intercalibration procedures, refer to the &amp;lt;a href=&amp;quot;https://datadocs.bco-dmo.org/docs/302/geotraces/GEOTRACES_EPZT/buesseler/data_docs/0000-0001-7362-8796-TN303-multiple-param-intercal-report.pdf&amp;quot; target=&amp;quot;_blank&amp;quot;&amp;gt;GEOTRACES Intercalibration Report&amp;lt;/a&amp;gt;&amp;amp;nbsp;(PDF) Supplemental File.&amp;lt;/p&amp;gt;</gco:CharacterString>
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                <gco:CharacterString>&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Detection Limits:&amp;lt;/strong&amp;gt; Limits of detection are not reported because they are not applicable to the Th-234 beta counting method. A 'non-detect' for Th-234 or a case where there is no Th-234 present (initially or after 6 months of decay) will still result in a measurable amount of background radioactivity due to the beta decay of long-lived natural radionuclides that are also carried by the Mn precipitate used in the shipboard sample processing. These background values are utilized and therefore, they are not reported as non-detections of Th-234.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Uncertainty:&amp;lt;/strong&amp;gt; At the start and conclusion of each cruise, high activity U-238 standards and background counts (empty detectors) were measured to confirm correct operation of the RISØ detectors and to determine detector to detector variability. The reported uncertainty on each total Th-234 measurement represents the propagated counting uncertainty, volume (pipettes) and weighing (scales) uncertainties, and detector to detector normalization. Counting uncertainty is generally the largest source of uncertainty so whenever possible samples were counted until errors were below 5%.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Inter-calibration Efforts:&amp;lt;/strong&amp;gt; Results from the GEOTRACES Th-234 inter-calibration efforts are published in Maiti et al. (2012). Fifteen labs participated in two cruises that centered on particulate, total and dissolved Th-234 inter-calibration. Total Th-234 was assessed on the 2009 GEOTRACES inter-calibration cruise. A short excerpt from Maiti et al. (2012) is included below that summarized the results and recommendations for total Th-234 shipboard analyses:&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;em&amp;gt;'Total 234Th inter-calibration results for deep water samples showed good agreement amongst laboratories. The mean 234Th activity of 2.433 ± 0.035 dpm L-1 for all laboratories was also found to be in very good agreement with the salinity derived expected 234Th activity of 2.442 ± 0.0003 dpm L-1, assuming secular equilibrium. However in comparison, the 234Th activities from SBB [Santa Barbara Basin] surface water had much more variability because of lower initial activity and large ingrowth corrections from 238U. It is thus recommended to keep the time between collection and filtering to a minimum in order to keep in-growth corrections to a minimum. This also reduces the error associated with the uncertainties in both salinity measurements and the 238U-salinity relationship as the error is propagated when ingrowth corrections are made.'&amp;lt;/em&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Because of the short half-life of Th-234 (~24 days), the nature of radionuclide analyses, and the recommendations stated above, inter-calibration between multiple labs was not possible during the 59-day GP16 cruise. Therefore, internal quality control was a priority and addressed in the following ways. First, five replicate deep water samples were analyzed to determine the degree of reproducibility. These samples were collected from the same niskin bottle and processed simultaneously. The results of this analysis are incorporated into the sample measurement uncertainty. Second, the shallow, intermediate, and deep pump casts were made to overlap to provide some means of assessing cast to cast differences and reproducibility. While conditions can change during the duration of a pump cast (~4 hours) as well as from one cast to the next, noticeable differences (larger than expected for natural variability) in overlapping casts were only observed at one station during GP16. This suggested a high degree of reproducibility was achieved for mid-water column total Th-234. Third, all filters measured for total Th-234 were counted twice aboard ship (second count within a few days of the first) and immediately compared to salinity-derived U-238 values. Any abnormal deviations were flagged (&amp;amp;gt;10% between counting results) and the filter was run a third time if necessary. These two counts were averaged for each sample to get a final 'total Th-234' for that depth and location. Lastly, the same internal uranium standards were used by the Buesseler lab during the NAZT and EPZT GEOTRACES cruises and will continue to be used on future cruises. These standards provide a consistent means for calibration and comparison.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Problem reporting:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
Data were flagged using the SeaDataNet quality flag scheme. For more information on SeaDataNet flags, see: &amp;lt;a href=&amp;quot;https://www.geotraces.org/geotraces-quality-flag-policy/&amp;quot; target=&amp;quot;_blank&amp;quot;&amp;gt;https://www.geotraces.org/geotraces-quality-flag-policy/&amp;lt;/a&amp;gt; and &amp;lt;a href=&amp;quot;https://www.seadatanet.org/Standards/Data-Quality-Control&amp;quot; target=&amp;quot;_blank&amp;quot;&amp;gt;https://www.seadatanet.org/Standards/Data-Quality-Control&amp;lt;/a&amp;gt;&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;SeaDataNet quality flag definitions:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
0 = No quality control;&amp;lt;br /&amp;gt;
1 = Good value;&amp;lt;br /&amp;gt;
2 = Probably good value;&amp;lt;br /&amp;gt;
3 = Probably bad value;&amp;lt;br /&amp;gt;
4 = Bad value;&amp;lt;br /&amp;gt;
5 = Changed value;&amp;lt;br /&amp;gt;
6 = Value below detection;&amp;lt;br /&amp;gt;
7 = Value in excess;&amp;lt;br /&amp;gt;
8 = Interpolated value;&amp;lt;br /&amp;gt;
9 = Missing value;&amp;lt;br /&amp;gt;
A = Value phenomenon uncertain.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Two samples were marked as 'bad values' due to issues encountered during sample filtration. Because of the obvious poor quality of these data, the total Thorium-234 values were not included. A few samples were denoted as 'probably good' because of a pipetting issue affecting individual sample recovery calculations. Average recoveries for the surrounding water column depths were used for these samples. Accordingly, uncertainty values were increased for these samples.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;BCO-DMO Processing:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
- renamed fields:&amp;lt;br /&amp;gt;
- added date/time fields in ISO8601 format;&amp;lt;br /&amp;gt;
- replaced blanks (missing data) with 'nd' ('no data');&amp;lt;br /&amp;gt;
- 11 June 2020: replaced with GEOTRACES DOoR-formatted/IDP version.&amp;lt;/p&amp;gt;</gco:CharacterString>
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