Characterization of chromium species in urban runoff

Research output: Contribution to journalJournal articleResearchpeer-review

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Characterization of chromium species in urban runoff. / Cederkvist, Karin; Jensen, Marina Bergen; Holm, Peter Engelund.

In: Journal of Environmental Quality, Vol. 42, No. 1, 2013, p. 111-117.

Research output: Contribution to journalJournal articleResearchpeer-review

Harvard

Cederkvist, K, Jensen, MB & Holm, PE 2013, 'Characterization of chromium species in urban runoff', Journal of Environmental Quality, vol. 42, no. 1, pp. 111-117. https://doi.org/10.2134/jeq2012.0182

APA

Cederkvist, K., Jensen, M. B., & Holm, P. E. (2013). Characterization of chromium species in urban runoff. Journal of Environmental Quality, 42(1), 111-117. https://doi.org/10.2134/jeq2012.0182

Vancouver

Cederkvist K, Jensen MB, Holm PE. Characterization of chromium species in urban runoff. Journal of Environmental Quality. 2013;42(1):111-117. https://doi.org/10.2134/jeq2012.0182

Author

Cederkvist, Karin ; Jensen, Marina Bergen ; Holm, Peter Engelund. / Characterization of chromium species in urban runoff. In: Journal of Environmental Quality. 2013 ; Vol. 42, No. 1. pp. 111-117.

Bibtex

@article{447bf7dc319d4f5a96d7400dcd75a5e4,
title = "Characterization of chromium species in urban runoff",
abstract = "Little is known about the presence of the element Cr in its toxic hexavalent form Cr(VI) in stormwater runoff from urban areas. Most studies report only total Cr concentration, i.e., including also the nontoxic Cr(III) molecular form. The objective of this study was to evaluate a field method based on cation-exchange for characterization of Cr species in urban stormwater runoff and soil leachate. We used a 0.05 mol L-1 Na and Ca solution and a soil leachate as matrices and spiked these with Cr(III), Cr(VI), or both in the concentration range of 1 to 100 mu g L-1. We then filtered the test samples through cation-exchange cartridges. In the Na-Ca salt matrix, the Cr(III) was retained 100% and recovery values of Cr(VI) were 86 to 100 Furthermore, in such a matrix, each cartridge could be reused at least nine times without a drop in retention of Cr(III) or recovery of Cr(VI). In a soil leachate matrix, the method appeared less applicable. Apparently Cr(III) forms complexes with dissolved organic matter, allowing it to bypass the cartridge, resulting in incomplete Cr(III) retention and thus incomplete speciation. The complexes are formed rapidly after spiking, thus changes in the Cr-species distribution are likely to occur within a few hours when fresh samples are stored. Furthermore, we concluded that Cr(III) at neutral pH in pure solution or complexed with dissolved organic C can sorb irreversibly to polyethylene and polypropylene containers. Our findings show that there is still a need for a method that can be applied to urban runoff in the field. Furthermore, cartridge speciation methods should ideally be tested before being applied on solutions containing organic matter.",
author = "Karin Cederkvist and Jensen, {Marina Bergen} and Holm, {Peter Engelund}",
year = "2013",
doi = "10.2134/jeq2012.0182",
language = "English",
volume = "42",
pages = "111--117",
journal = "Journal of Environmental Quality",
issn = "0047-2425",
publisher = "American Society of Agronomy",
number = "1",

}

RIS

TY - JOUR

T1 - Characterization of chromium species in urban runoff

AU - Cederkvist, Karin

AU - Jensen, Marina Bergen

AU - Holm, Peter Engelund

PY - 2013

Y1 - 2013

N2 - Little is known about the presence of the element Cr in its toxic hexavalent form Cr(VI) in stormwater runoff from urban areas. Most studies report only total Cr concentration, i.e., including also the nontoxic Cr(III) molecular form. The objective of this study was to evaluate a field method based on cation-exchange for characterization of Cr species in urban stormwater runoff and soil leachate. We used a 0.05 mol L-1 Na and Ca solution and a soil leachate as matrices and spiked these with Cr(III), Cr(VI), or both in the concentration range of 1 to 100 mu g L-1. We then filtered the test samples through cation-exchange cartridges. In the Na-Ca salt matrix, the Cr(III) was retained 100% and recovery values of Cr(VI) were 86 to 100 Furthermore, in such a matrix, each cartridge could be reused at least nine times without a drop in retention of Cr(III) or recovery of Cr(VI). In a soil leachate matrix, the method appeared less applicable. Apparently Cr(III) forms complexes with dissolved organic matter, allowing it to bypass the cartridge, resulting in incomplete Cr(III) retention and thus incomplete speciation. The complexes are formed rapidly after spiking, thus changes in the Cr-species distribution are likely to occur within a few hours when fresh samples are stored. Furthermore, we concluded that Cr(III) at neutral pH in pure solution or complexed with dissolved organic C can sorb irreversibly to polyethylene and polypropylene containers. Our findings show that there is still a need for a method that can be applied to urban runoff in the field. Furthermore, cartridge speciation methods should ideally be tested before being applied on solutions containing organic matter.

AB - Little is known about the presence of the element Cr in its toxic hexavalent form Cr(VI) in stormwater runoff from urban areas. Most studies report only total Cr concentration, i.e., including also the nontoxic Cr(III) molecular form. The objective of this study was to evaluate a field method based on cation-exchange for characterization of Cr species in urban stormwater runoff and soil leachate. We used a 0.05 mol L-1 Na and Ca solution and a soil leachate as matrices and spiked these with Cr(III), Cr(VI), or both in the concentration range of 1 to 100 mu g L-1. We then filtered the test samples through cation-exchange cartridges. In the Na-Ca salt matrix, the Cr(III) was retained 100% and recovery values of Cr(VI) were 86 to 100 Furthermore, in such a matrix, each cartridge could be reused at least nine times without a drop in retention of Cr(III) or recovery of Cr(VI). In a soil leachate matrix, the method appeared less applicable. Apparently Cr(III) forms complexes with dissolved organic matter, allowing it to bypass the cartridge, resulting in incomplete Cr(III) retention and thus incomplete speciation. The complexes are formed rapidly after spiking, thus changes in the Cr-species distribution are likely to occur within a few hours when fresh samples are stored. Furthermore, we concluded that Cr(III) at neutral pH in pure solution or complexed with dissolved organic C can sorb irreversibly to polyethylene and polypropylene containers. Our findings show that there is still a need for a method that can be applied to urban runoff in the field. Furthermore, cartridge speciation methods should ideally be tested before being applied on solutions containing organic matter.

U2 - 10.2134/jeq2012.0182

DO - 10.2134/jeq2012.0182

M3 - Journal article

C2 - 23673745

VL - 42

SP - 111

EP - 117

JO - Journal of Environmental Quality

JF - Journal of Environmental Quality

SN - 0047-2425

IS - 1

ER -

ID: 117985024