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Selenium Removal and Mass Balance in a Constructed Flow-Through Wetland System

S. Gao*,a, K. K. Tanjia, Z. Q. Linb,c, N. Terryb and D. W. Petersa,d

a Dep. of Land, Air and Water Resources, Univ. of California, One Shields Ave., Davis, CA 95616
b Dep. of Plant and Microbial Biology, Univ. of California, 111 Koshland Hall, Berkeley, CA 94720
c Dep. of Biological Sciences & Environmental Sciences Program, Southern Illinois Univ., Edwardsville, IL 62026-1651
d U.C. Hansen Agricultural Learning Center, 14292 W. Telegraph Rd., Santa Paula, CA 93060



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Fig. 1. Schematic diagram of the layout of the Tulare Lake Drainage District (TLDD) flow-through wetland system.

 


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Fig. 2. Sketch of the comprehensive sampling in wetland cells for mass balance, 20–22 Sept. 2000.

 


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Fig. 3. Average annual residence times. Error bars are standard deviations from weekly measurements. BUL, sturdy bulrush; BAL, baltic rush; CORD, smooth cordgrass; RAB, rabbitfoot grass; SALT, saltgrass; CAT, cattail; B–W–B, bulrush–widgeon grass–bulrush; T–W–C, tule–widgeon grass–cattail.

 


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Fig. 4. Average annual Se concentration in inflow and outflow waters. Error bars are standard deviations from weekly measurements. BUL, sturdy bulrush; BAL, baltic rush; CORD, smooth cordgrass; RAB, rabbitfoot grass; SALT, saltgrass; CAT, cattail; B–W–B, bulrush–widgeon grass–bulrush; T–W–C, tule–widgeon grass–cattail.

 


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Fig. 5. Selenium concentration ratio and mass ratio of outflow to inflow in 2000. Error bars are standard deviations from weekly measurements. BUL, sturdy bulrush; BAL, baltic rush; CORD, smooth cordgrass; RAB, rabbitfoot grass; SALT, saltgrass; CAT, cattail; B–W–B, bulrush–widgeon grass–bulrush; T–W–C, tule–widgeon grass–cattail.

 


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Fig. 6. Selenium speciation in inflow and outflow waters in 2000. Error bars are standard deviations of four seasonal measurements during the year. BUL, sturdy bulrush; BAL, baltic rush; CORD, smooth cordgrass; RAB, rabbitfoot grass; SALT, saltgrass; CAT, cattail; B–W–B, bulrush–widgeon grass–bulrush; T–W–C, tule–widgeon grass–cattail.

 


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Fig. 7. Selenium concentration in sediments in 2000. Values at depth of 0 cm represent Se concentration in the fine organic detrital layer. Error bars are standard deviations of several sampling locations shown in Fig. 2. BUL, sturdy bulrush; BAL, baltic rush; CORD, smooth cordgrass; RAB, rabbitfoot grass; SALT, saltgrass; CAT, cattail; B–W–B, bulrush–widgeon grass–bulrush; T–W–C, tule–widgeon grass–cattail.

 


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Fig. 8. Selenium concentration in fallen liter, organic detrital layer, and surface sediment (0–5 cm) in September 2000. Error bars are standard deviations of several sampling locations shown in Fig. 2. BUL, sturdy bulrush; BAL, baltic rush; CORD, smooth cordgrass; RAB, rabbitfoot grass; SALT, saltgrass; CAT, cattail; B–W–B, bulrush–widgeon grass–bulrush; T–W–C, tule–widgeon grass–cattail.

 


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Fig. 9. Mass of Se accumulated in the 0- to 20-cm sediment, detrital layer, and fallen litter in September 2000. BUL, sturdy bulrush; BAL, baltic rush; CORD, smooth cordgrass; RAB, rabbitfoot grass; SALT, saltgrass; CAT, cattail; B–W–B, bulrush–widgeon grass–bulrush; T–W–C, tule–widgeon grass–cattail.

 


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Fig. 10. Selenium mass balance in the Tulare Lake Drainage District (TLDD) flow-through wetland after four years of operation.

 





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