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Last modified
7/14/2009 5:02:31 PM
Creation date
5/20/2009 5:13:34 PM
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UCREFRP
UCREFRP Catalog Number
7821
Author
Hamilton, S. J., et al.
Title
Evaluation Of Toxicity To Larval Razorback Sucker Of Selenium-Laden Food Organisms From Ouray NWR On The Green River, Utah.
USFW Year
1996.
USFW - Doc Type
\
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<br />feeding study, all live fish were measured for total length and a pooled weight determined <br />(fish were too small for measurement of individual weight) in the tests with 5- and to-day <br />old larvae, but weighed individually in the test with 24-day old larvae. <br /> <br />Inorganic analyses <br /> <br />Water samples were collected weekly at the six sites for residue analysis of selenium <br />and other inorganics. Water was filtered through a 0.45 ILm polycarbonate filter and 200 ml <br />was preserved with 2 ml ultrapure RCI and stored frozen. Concentrations of selenium in <br />water samples were determined with a Perkin-Elmer model 2280 atomic absorption <br />spectrophotometer equipped with a model MRS-tO hydride generator. The <br />spectrophotometer was standardized with National Institute of Standards and Technology <br />(NIST) standard reference material 3149 (water). Samples were digested using a persulfate <br />digestion technique and total selenium determined by a modification of the method of Presser <br />and Barnes (1984). The limit of detection (LOD) ranged from 0.4 to 2.4 Jlg/L, the <br />procedure blanks had background equivalent concentrations less than the LOD (indicates no <br />contamination from reagents or sample handling), the percent relative standard deviation <br />(triplicate sample preparation and analysis) was 5.4% (indicates consistent sample handling <br />during preparation, digestion, and analysis), and recovery of selenium was within <br />recommended ranges in National Bureau of Standards (NBS) reference material 1643b water <br />(8.2-11.2 ILg/L) and NIST standard reference material 3149 (8.99-11.01ILg/L) (indicates the <br />digestion and analysis procedure accurately measured selenium concentrations). The digested <br />sample spike solutions had a mean percent recovery of 98 % (indicates the digestion <br />procedure did not alter the amount of spiked selenium in the sample, i.e., suggests no loss of <br />selenium in water samples during digestion procedure). Field spiked samples had a mean <br />percent recovery of 90% (indicates sample vessels and storage did not alter the amount of <br />selenium in the samples). Spiked samples analyzed for matrix suppression or enhancement <br />had mean selenium recoveries of 99% (indicates no interference from other water <br />components) . <br /> <br />A second set of 200 ml water samples was filtered and preserved with 2 ml ultrapure <br />HN03 and stored frozen. These samples were analyzed by inductively-coupled argon plasma <br />(I CAP) analysis for 32 elements at the Environmental Trace Substances Research Center, <br />Columbia, MO. The procedure blank had background equivalent concentrations less than the <br />LOD for all elements except calcium and thallium, the mean percent relative standard <br />deviation (duplicate sample preparation and analysis) was 1.3 %, the mean spike recovery was <br />97 %, and the recovery of trace elements in Environmental Resources Associates reference <br />water ERA9947TM was within recommended ranges. The estimated limit of detections <br />[mg/L; mean (standard error)] were: Ag 0.009 (0.001), Al 0.02 (0), As 0.03 (0), B 0.009 <br />(0.001), Ba 0.0006 (0.0001), Be 0.0002 (0), Bi 0.02 (0), Ca 0.06 (0.01), Cd 0.002 (0), Co <br />0.004 (0), Cr 0.007 (0), Cu 0.003 (0), Fe 0.007 (0), K 0.3 (0), Li 0.001 (0), Mg 0.01 (0), <br />Mn 0.001 (0), Mo 0.006 (0.001), Na 0.08 (0), Ni 0.007 (0), P 0.06 (0.01), Pb 0.03 (0), Sb <br />0.04 (0), Se 0.03 (0), Si 0.04 (0), Sn 0.03 (0), Sr 0.0008 (0), Ti 0.0009 (0), TI 0.08 (0), V <br />0.002 (0), Zn 0.002 (0), and Zr 0.003 (0). <br /> <br />15 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />
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