The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake

<p><p>I investigated the usefulness of phytoplankton for the removal of surface water contaminants. Three experiments, consisting of nine large mesocosms (92.2 m<sup>3</sup>) were suspended in the flooded DJX uranium pit at Cluff Lake (Saskatchewan, Canada), and filled with c...

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Bibliographic Details
Main Author: Dessouki, Tarik C.E.
Other Authors: Neal, Brian R.
Format: Others
Language:en
Published: University of Saskatchewan 2012
Subjects:
Online Access:http://library.usask.ca/theses/available/etd-05282012-111234/
id ndltd-USASK-oai-usask.ca-etd-05282012-111234
record_format oai_dc
collection NDLTD
language en
format Others
sources NDLTD
topic Open-pit
Metals
Uranium
Pit-lakes
Contaminants
Nutrients
Phosphorus
Nitrogen
Phytoplankton
Mining
Bioremediation
Sedimentation
spellingShingle Open-pit
Metals
Uranium
Pit-lakes
Contaminants
Nutrients
Phosphorus
Nitrogen
Phytoplankton
Mining
Bioremediation
Sedimentation
Dessouki, Tarik C.E.
The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake
description <p><p>I investigated the usefulness of phytoplankton for the removal of surface water contaminants. Three experiments, consisting of nine large mesocosms (92.2 m<sup>3</sup>) were suspended in the flooded DJX uranium pit at Cluff Lake (Saskatchewan, Canada), and filled with contaminated mine water. During the summer of 2003, each mesocosm was fertilized with a different amount of phosphorus throughout the 35 day experiment to stimulate phytoplankton growth, and to create a range in phosphorus load (g) to examine how contaminants may be affected by different nutrient regimes. Algal growth was rapid in fertilized mesocosms as demonstrated by chlorophyll a profiles. As phosphorus loads increased there were significant declines in the surface water concentrations of As, Co, Cu, Mn, Ni, and Zn. This decline was near significant for uranium. The surface water concentrations of Ra<sup>226</sup>, Mo, and Se showed no relationship to phosphorus load. Contaminant concentrations in sediment traps suspended at the bottom of each mesocosm generally showed the opposite trend to that observed in the surface water, with most contaminants (As, Co, Cu, Mn, Ni, Ra<sup>226</sup>, U, and Zn) exhibiting a significant positive relationship (<i>P</i> < 0.05) with phosphorus load. Sediment trap concentration of Se and Mo did not respond to nutrient treatments.</p> <p>Similar experiments were repeated during the mid- and late-summer of 2004, with 5 mesocosms being fertilized with phosphorus, and another 4 with both phosphorus and ammonium to create different nutrient gradients. Results from these experiments were much more variable than those seen in the experiment conducted in 2003, and small samples (<i>n</i> = 5 for phosphorus treatments and <i>n</i> = 4 for both phosphorus and ammonium treatments) yielded insufficient statistical power to effectively determine statistically significant trends. However, contaminant sedimentation tended to respond to phosphorus treatments in a similar manner as results from 2003; phosphorus-with-ammonium treatments had little positive effect on contaminant sedimentation rates.</p> <p>My results suggest that phytoremediation has the potential to lower many surface water contaminants through the sedimentation of phytoplankton. Based on our results from 2003, we estimate that the Saskatchewan Surface Water Quality Objectives (SSWQO) for the DJX pit would be met in approximately 45 weeks for Co, 65 weeks for Ni, 15 weeks for U, and 5 weeks for Zn if treated using phytoremediation.</p><p>Note:</p><p>Appendix A content (pages 92-95) contains copyrighted material which has been removed. It can be viewed in the original thesis upon request.</p>
author2 Neal, Brian R.
author_facet Neal, Brian R.
Dessouki, Tarik C.E.
author Dessouki, Tarik C.E.
author_sort Dessouki, Tarik C.E.
title The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake
title_short The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake
title_full The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake
title_fullStr The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake
title_full_unstemmed The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake
title_sort effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake
publisher University of Saskatchewan
publishDate 2012
url http://library.usask.ca/theses/available/etd-05282012-111234/
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spelling ndltd-USASK-oai-usask.ca-etd-05282012-1112342013-01-08T16:35:21Z The effects of nutrient additions on the sedimentation of surface water contaminants in a uranium mined pit-lake Dessouki, Tarik C.E. Open-pit Metals Uranium Pit-lakes Contaminants Nutrients Phosphorus Nitrogen Phytoplankton Mining Bioremediation Sedimentation <p><p>I investigated the usefulness of phytoplankton for the removal of surface water contaminants. Three experiments, consisting of nine large mesocosms (92.2 m<sup>3</sup>) were suspended in the flooded DJX uranium pit at Cluff Lake (Saskatchewan, Canada), and filled with contaminated mine water. During the summer of 2003, each mesocosm was fertilized with a different amount of phosphorus throughout the 35 day experiment to stimulate phytoplankton growth, and to create a range in phosphorus load (g) to examine how contaminants may be affected by different nutrient regimes. Algal growth was rapid in fertilized mesocosms as demonstrated by chlorophyll a profiles. As phosphorus loads increased there were significant declines in the surface water concentrations of As, Co, Cu, Mn, Ni, and Zn. This decline was near significant for uranium. The surface water concentrations of Ra<sup>226</sup>, Mo, and Se showed no relationship to phosphorus load. Contaminant concentrations in sediment traps suspended at the bottom of each mesocosm generally showed the opposite trend to that observed in the surface water, with most contaminants (As, Co, Cu, Mn, Ni, Ra<sup>226</sup>, U, and Zn) exhibiting a significant positive relationship (<i>P</i> < 0.05) with phosphorus load. Sediment trap concentration of Se and Mo did not respond to nutrient treatments.</p> <p>Similar experiments were repeated during the mid- and late-summer of 2004, with 5 mesocosms being fertilized with phosphorus, and another 4 with both phosphorus and ammonium to create different nutrient gradients. Results from these experiments were much more variable than those seen in the experiment conducted in 2003, and small samples (<i>n</i> = 5 for phosphorus treatments and <i>n</i> = 4 for both phosphorus and ammonium treatments) yielded insufficient statistical power to effectively determine statistically significant trends. However, contaminant sedimentation tended to respond to phosphorus treatments in a similar manner as results from 2003; phosphorus-with-ammonium treatments had little positive effect on contaminant sedimentation rates.</p> <p>My results suggest that phytoremediation has the potential to lower many surface water contaminants through the sedimentation of phytoplankton. Based on our results from 2003, we estimate that the Saskatchewan Surface Water Quality Objectives (SSWQO) for the DJX pit would be met in approximately 45 weeks for Co, 65 weeks for Ni, 15 weeks for U, and 5 weeks for Zn if treated using phytoremediation.</p><p>Note:</p><p>Appendix A content (pages 92-95) contains copyrighted material which has been removed. It can be viewed in the original thesis upon request.</p> Neal, Brian R. Sheard, J.W. Hudson, Jeffrey James University of Saskatchewan 2012-05-28 text application/pdf http://library.usask.ca/theses/available/etd-05282012-111234/ http://library.usask.ca/theses/available/etd-05282012-111234/ en unrestricted I hereby certify that, if appropriate, I have obtained and attached hereto a written permission statement from the owner(s) of each third party copyrighted matter to be included in my thesis, dissertation, or project report, allowing distribution as specified below. I certify that the version I submitted is the same as that approved by my advisory committee. I hereby grant to University of Saskatchewan or its agents the non-exclusive license to archive and make accessible, under the conditions specified below, my thesis, dissertation, or project report in whole or in part in all forms of media, now or hereafter known. I retain all other ownership rights to the copyright of the thesis, dissertation or project report. I also retain the right to use in future works (such as articles or books) all or part of this thesis, dissertation, or project report.