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                <gmx:Anchor xlink:href="https://ror.org/032db5x82" xlink:title="ROR ID" xlink:actuate="onRequest">University of South Florida</gmx:Anchor>
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            <gco:CharacterString>Cite this dataset as: Breitbart, M., Buck, K., Bonnain, C., Caprara, S. (2018) 57Fe Wall Loss Experiment data collected as part of a method development study investigating the precipitation and wall loss of labeled 57Fe when added to M9 Minimal Media. Biological and Chemical Oceanography Data Management Office (BCO-DMO). (Version 1) Version Date 2018-04-05 [if applicable, indicate subset used]. doi:10.1575/1912/bco-dmo.732864.1 [access date]</gco:CharacterString>
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        <gco:CharacterString>Dataset Description: &amp;lt;p&amp;gt;This data was collected as part of a method development study investigating the precipitation and wall loss of labeled ⁵⁷Fe when added to M9 Minimal Media, which is used to grow the model bacterial species &amp;lt;em&amp;gt;Escherichia coli.&amp;lt;/em&amp;gt; The bulk media was prepared with the same components and a portion was treated with Chelex-100 to remove metals, while the other portion remained un-chelexed. Half of each treatment was spiked with labeled ⁵⁷Fe and either 0.2 μm or 0.02 μm filtered for comparison of the dissolved and soluble fractions. The ⁵⁷Fe content was monitored over four time points for one week in a shaking incubator, under the same conditions used to culture &amp;lt;em&amp;gt;E. coli&amp;lt;/em&amp;gt; for labeling experiments.&amp;lt;/p&amp;gt; Methods and Sampling: &amp;lt;p&amp;gt;Refer to Supplemental File, &amp;quot;57Fe Wall Loss Experiment diagram&amp;quot; for the steps indicated in &amp;lt;strong&amp;gt;bold&amp;lt;/strong&amp;gt;.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;All materials were soaked overnight with heating in 1.5% Citrad Citric Acid liquid cleaner in deionized water, rinsed in RO water, and soaked in 10% HCl in Milli-Q ultrapure water for one week (due to time constraints), then rinsed with MilliQ ultrapure water, let dry in an AirClean 400 work station overnight, and double-bagged in polyethylene bags (Mellett et al., 2017). M9 Minimal Media for bacterial cultures was made using Milli-Q ultrapure water, containing final concentrations of 33.7 mM Na₂HPO₄·2H₂O, 22 mM KH₂PO₄, 8.56 mM NaCl, 18.7 mM NH₄Cl, 0.1 M magnesium chloride, 0.1 M calcium chloride, 2 mg/ml Thiamine HCl in 70% EtOH, and 20% Glucose (Kutter &amp;amp;amp; Sulakvelidze, 2004). Half of the media was chelexed using Chelex-100 resin (Pai et al., 1988) that was not acid-cleaned (&amp;lt;strong&amp;gt;C&amp;lt;/strong&amp;gt;), and half remained un-chelexed (&amp;lt;strong&amp;gt;B&amp;lt;/strong&amp;gt;). Half of each treatment was spiked with 10 µM labeled ⁵⁷FeSO₄(&amp;lt;strong&amp;gt;2&amp;lt;/strong&amp;gt;) while half remained un-spiked (&amp;lt;strong&amp;gt;1&amp;lt;/strong&amp;gt;). A volume of 25 ml was then filtered through either a 0.2 µm Sterivex PVDF syringe filter for the dissolved fraction (&amp;lt;strong&amp;gt;D&amp;lt;/strong&amp;gt;), or a 0.02 µm Whatman Anatop syringe filter for the soluble fraction (&amp;lt;strong&amp;gt;S&amp;lt;/strong&amp;gt;) (Gledhill &amp;amp;amp; Buck, 2012). Samples were directly filtered into trace metal clean polycarbonate Erlenmeyer flasks, placed in a clean bag with a small opening to vent, and left shaking at 37 °C for one week. Samples of each treatment were taken initially, then after the 1st, 3rd, and 7th days (t= 00, 01, 03, 07). The samples were diluted, acidified, and analyzed using an ELEMENT XR High Resolution Inductively Coupled Plasma Mass Spectrometer (HR-ICP-MS). The limit of detection (LOD) for ⁵⁶Fe and ⁵⁷Fe were 0.3 nM and 0.012 nM, respectively (Shrivastava &amp;amp;amp; Gupta, 2011).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Problem Report:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
The original measurements of the M9 minimal media ⁵⁶Fe contamination was high, so in an attempt to lower background contamination the media was chelexed. However, the Chelex-100 resin was not rinsed with acid, so was less active for removal of metals. This resulted in higher than expected background concentrations of metals.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Three samples were contaminated with bacterial growth (as indicated by visual turbidity and confirmed using SYBR nucleic acid stain and epifluorescence microscopy) over the course of the week. On t=3, sample B2 was contaminated. By t=7, sample B1D and B1S were contaminated.&amp;lt;/p&amp;gt;</gco:CharacterString>
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        <gmx:Anchor xlink:href="http://lod.bco-dmo.org/id/award/713366.rdf" xlink:title="OCE-1722761" xlink:actuate="onRequest">Funding provided by NSF Division of Ocean Sciences (NSF OCE) Award Number: OCE-1722761 Award URL: https://www.nsf.gov/awardsearch/show-award?AWD_ID=1722761</gmx:Anchor>
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	Description: &lt;p&gt;Some samples contaminated by bacterial growth were designated as such&lt;/p&gt; 
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&amp;lt;p&amp;gt;All materials were soaked overnight with heating in 1.5% Citrad Citric Acid liquid cleaner in deionized water, rinsed in RO water, and soaked in 10% HCl in Milli-Q ultrapure water for one week (due to time constraints), then rinsed with MilliQ ultrapure water, let dry in an AirClean 400 work station overnight, and double-bagged in polyethylene bags (Mellett et al., 2017). M9 Minimal Media for bacterial cultures was made using Milli-Q ultrapure water, containing final concentrations of 33.7 mM Na₂HPO₄·2H₂O, 22 mM KH₂PO₄, 8.56 mM NaCl, 18.7 mM NH₄Cl, 0.1 M magnesium chloride, 0.1 M calcium chloride, 2 mg/ml Thiamine HCl in 70% EtOH, and 20% Glucose (Kutter &amp;amp;amp; Sulakvelidze, 2004). Half of the media was chelexed using Chelex-100 resin (Pai et al., 1988) that was not acid-cleaned (&amp;lt;strong&amp;gt;C&amp;lt;/strong&amp;gt;), and half remained un-chelexed (&amp;lt;strong&amp;gt;B&amp;lt;/strong&amp;gt;). Half of each treatment was spiked with 10 µM labeled ⁵⁷FeSO₄(&amp;lt;strong&amp;gt;2&amp;lt;/strong&amp;gt;) while half remained un-spiked (&amp;lt;strong&amp;gt;1&amp;lt;/strong&amp;gt;). A volume of 25 ml was then filtered through either a 0.2 µm Sterivex PVDF syringe filter for the dissolved fraction (&amp;lt;strong&amp;gt;D&amp;lt;/strong&amp;gt;), or a 0.02 µm Whatman Anatop syringe filter for the soluble fraction (&amp;lt;strong&amp;gt;S&amp;lt;/strong&amp;gt;) (Gledhill &amp;amp;amp; Buck, 2012). Samples were directly filtered into trace metal clean polycarbonate Erlenmeyer flasks, placed in a clean bag with a small opening to vent, and left shaking at 37 °C for one week. Samples of each treatment were taken initially, then after the 1st, 3rd, and 7th days (t= 00, 01, 03, 07). The samples were diluted, acidified, and analyzed using an ELEMENT XR High Resolution Inductively Coupled Plasma Mass Spectrometer (HR-ICP-MS). The limit of detection (LOD) for ⁵⁶Fe and ⁵⁷Fe were 0.3 nM and 0.012 nM, respectively (Shrivastava &amp;amp;amp; Gupta, 2011).&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;&amp;lt;strong&amp;gt;Problem Report:&amp;lt;/strong&amp;gt;&amp;lt;br /&amp;gt;
The original measurements of the M9 minimal media ⁵⁶Fe contamination was high, so in an attempt to lower background contamination the media was chelexed. However, the Chelex-100 resin was not rinsed with acid, so was less active for removal of metals. This resulted in higher than expected background concentrations of metals.&amp;lt;/p&amp;gt;

&amp;lt;p&amp;gt;Three samples were contaminated with bacterial growth (as indicated by visual turbidity and confirmed using SYBR nucleic acid stain and epifluorescence microscopy) over the course of the week. On t=3, sample B2 was contaminated. By t=7, sample B1D and B1S were contaminated.&amp;lt;/p&amp;gt;</gco:CharacterString>
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