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dc.contributor.authorTrostle, Kyle D.
dc.contributor.authorRay Runyon, J.
dc.contributor.authorPohlmann, Michael A.
dc.contributor.authorRedfield, Shelby E.
dc.contributor.authorPelletier, Jon
dc.contributor.authorMcIntosh, Jennifer
dc.contributor.authorChorover, Jon
dc.date.accessioned2017-02-09T16:39:13Z
dc.date.available2017-02-09T16:39:13Z
dc.date.issued2016-10
dc.identifier.citationColloids and organic matter complexation control trace metal concentration-discharge relationships in Marshall Gulch stream waters 2016, 52 (10):7931 Water Resources Researchen
dc.identifier.issn00431397
dc.identifier.doi10.1002/2016WR019072
dc.identifier.urihttp://hdl.handle.net/10150/622503
dc.description.abstractThis study combined concentration-discharge analyses (filtration at 0.45 m), cascade filtrations (at 1.2, 0.4, and 0.025 m) and asymmetrical flow field flow fractionation (AF4) to probe the influence of colloidal carriers (dissolved organic matter and inorganic nanoparticles) on observed concentration-discharge relationships for trace metals in a 155 ha forested catchment of the Santa Catalina Mountains Critical Zone Observatory (SCM CZO), Arizona. Many major elements (Na, Mg, Si, K, Ca) show no colloidal influence, and concentration-discharge relationships for these species are explained by previous work. However, the majority of trace metals (Al, Ti, V, Mn, Fe, Cu, Y, REE, U) show at least some influence of colloids on chemistry when filtered at the standard 0.45 m cutoff. Concentration-discharge slopes of trace metals with modest colloidal influence are shallow (approximate to 0.3) similar to that measured for dissolved organic carbon (DOC, 0.24), whereas elements with greater colloidal influence have steeper concentration-discharge slopes approaching that of Al (0.76), the element with the largest colloidal influence in this study (on average 68%). These findings are further supported by AF4 measurements that show distinct and resolvable pools of low hydrodynamic diameter DOC-sized material coexistent with larger diameter inorganic colloids, and the ratio of these carriers changes systematically with discharge because the DOC pool has a concentration-discharge relationship with shallower slope than the inorganic colloidal pool. Together these data sets illustrate that positive concentration-discharge slopes of trace metals in stream waters may be explained as the relative partitioning of trace metals between DOC and inorganic colloids, with contributions of the latter likely increasing as a result of increased prevalence of macropore flow.
dc.description.sponsorshipU.S. National Science Foundation [EAR-1331408]; Catalina-Jemez Critical Zone Observatory; Research Experience for Undergraduates (REU) program at Biosphere [2]; [EAR-1263251]en
dc.language.isoenen
dc.publisherAMER GEOPHYSICAL UNIONen
dc.relation.urlhttp://doi.wiley.com/10.1002/2016WR019072en
dc.rights© 2016. American Geophysical Union. All Rights Reserved.en
dc.rights.urihttp://rightsstatements.org/vocab/InC/1.0/
dc.subjectC-Q relationshipsen
dc.subjecttrace metalsen
dc.subjectcolloidsen
dc.subjectDOC complexationen
dc.titleColloids and organic matter complexation control trace metal concentration-discharge relationships in Marshall Gulch stream watersen
dc.typeArticleen
dc.contributor.departmentUniv Arizona, Dept Geoscien
dc.contributor.departmentUniv Arizona, Dept Hydrol & Atmospher Scien
dc.identifier.journalWater Resources Researchen
dc.description.noteFirst published: 18 October 2016; 6 month embargo.en
dc.description.collectioninformationThis item from the UA Faculty Publications collection is made available by the University of Arizona with support from the University of Arizona Libraries. If you have questions, please contact us at repository@u.library.arizona.edu.en
dc.eprint.versionFinal published versionen
dc.contributor.institutionDepartment of Soil, Water and Environmental Science; University of Arizona; Tucson Arizona USA
dc.contributor.institutionDepartment of Soil, Water and Environmental Science; University of Arizona; Tucson Arizona USA
dc.contributor.institutionDepartment of Soil, Water and Environmental Science; University of Arizona; Tucson Arizona USA
dc.contributor.institutionDepartment of Molecular Biology and Biochemistry; Middlebury College; Middlebury Vermont USA
dc.contributor.institutionDepartment of Geosciences; University of Arizona; Tucson Arizona USA
dc.contributor.institutionDepartment of Hydrology and Atmospheric Sciences; University of Arizona; Tucson Arizona USA
dc.contributor.institutionDepartment of Soil, Water and Environmental Science; University of Arizona; Tucson Arizona USA
refterms.dateFOA2017-04-19T00:00:00Z
html.description.abstractThis study combined concentration-discharge analyses (filtration at 0.45 m), cascade filtrations (at 1.2, 0.4, and 0.025 m) and asymmetrical flow field flow fractionation (AF4) to probe the influence of colloidal carriers (dissolved organic matter and inorganic nanoparticles) on observed concentration-discharge relationships for trace metals in a 155 ha forested catchment of the Santa Catalina Mountains Critical Zone Observatory (SCM CZO), Arizona. Many major elements (Na, Mg, Si, K, Ca) show no colloidal influence, and concentration-discharge relationships for these species are explained by previous work. However, the majority of trace metals (Al, Ti, V, Mn, Fe, Cu, Y, REE, U) show at least some influence of colloids on chemistry when filtered at the standard 0.45 m cutoff. Concentration-discharge slopes of trace metals with modest colloidal influence are shallow (approximate to 0.3) similar to that measured for dissolved organic carbon (DOC, 0.24), whereas elements with greater colloidal influence have steeper concentration-discharge slopes approaching that of Al (0.76), the element with the largest colloidal influence in this study (on average 68%). These findings are further supported by AF4 measurements that show distinct and resolvable pools of low hydrodynamic diameter DOC-sized material coexistent with larger diameter inorganic colloids, and the ratio of these carriers changes systematically with discharge because the DOC pool has a concentration-discharge relationship with shallower slope than the inorganic colloidal pool. Together these data sets illustrate that positive concentration-discharge slopes of trace metals in stream waters may be explained as the relative partitioning of trace metals between DOC and inorganic colloids, with contributions of the latter likely increasing as a result of increased prevalence of macropore flow.


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