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<br /> <br />Hyporheic zones also serve as sites for nutrient <br />uptake, A study of a coastal mountain stream in northern <br />California indicated that transport of dissolved oxygen, <br />dissolved carbon, and dissolved nitrogen in stream water into <br />the hyporheic zone stimulated uptake of nitrogen by microbes <br />and algae attached to sediment. A model simulation of <br />nitrogen uptake (Figure F-2) indicated that both the physical <br />process of water exchange between the stream and the <br />hyporheic zone and the biological uptake of nitrate in the <br />hyporheic zone affected the concentration of dissolved <br />nitrogen in the stream, <br /> <br /> 225 <br />:i <br />" 200 <br />W <br />oo <br />f-oo . <br />"'w <br />zt: 175 ~ <br />-~ <br />Zoo '2 <br />~~ 150 Eo <br />"'" "0 <br /> E.,;:; <br />t:~ 125 _0 <br />000 <br />Zoo g.:~ <br />~el '0 <br />z~ 100 . <br />Ou E <br />u- <br />Z:> 75 ;;: <br />Wz I <br />el- <br />0 50 <br />oo <br />f- <br />Z <br /> <br />Without uptake <br />J-- <br />-- <br />"..'" With storage and <br />- I <br /> <br />Without storage <br />I <br /> <br /> <br />o Data <br />------ } Model simulations <br /> <br />25 <br />1000 1400 <br /> <br />2200 0200 0600 <br />TIME OF DAY <br /> <br />Figure F-2. Nitrate injected into Little Lost Man Greek in <br />northern Gaiiiomia was stored and taken up by aigae and <br />microbes in the hyporheic zone, (Modified from Kim, 8,K.A., <br />Jackman, AP" and Triska, F,J" 1992, Modeiing biotic uptake <br />by periphyton and transient hyporheic storage of nitrate in a <br />natural stream: Water Resources Research, v, 28, no,10, <br />p, 2743-2752.) <br /> <br />1800 <br /> <br />1000 1400 <br /> <br /> <br />Little Lost Man Creek, California. (Photograph by <br />Judson Harvey.) <br /> <br />" <br /> <br /> <br />The importance of biogeochemical processes that take <br />place at the interface of ground water and surface water in <br />improving water quality for human consumption is shown by <br />the following example, Decreasing metal concentrations <br />(Figure F-3) in drinking-water wells adjacent to the River Glatt <br />in Switzerland was attributed to the interaction of the river with <br />subsurface water. The improvement in ground-water quality <br />started with improved sewage-treatment plants, which <br />lowered phosphate in the river, Lower phosphate concentra- <br />tions lowered the amount of algal production in the river, <br />which decreased the amount of dissolved organic carbon <br />flowing into the riverbanks, These factors led to a decrease in <br />the bacteria-caused dissolution of manganese and cadmium <br />that were present as coatings on sediment in the aquifer, The <br />result was substantially lower dissolved metal concentrations <br />in ground water adjacent to the river, which resulted in an <br />unexpected improvement in the quality of drinking water. <br /> <br />60 <br /> <br />Phosphate <br /> <br /> <br />40 <br /> <br />~ <br /> <br />... .,. <br /> <br />oo <br />w <br />~ 20 <br /> <br />....-.... <br /> <br />oo <br />w <br />"- 0 <br />~ Manganese <br />o 6 <br />:> <br />o <br />oo 4 <br />U <br />~ <br /> <br />2 <br /> <br />I <br /> <br />~ <br /> <br /> <br /> 0 <br /> Cadmium <br /> 6 J <br />'" <br />Woo <br />6 ~4 / <br />:>" <br />~ffi2 <br />,,"- <br />Z <br /> 0 <br /> 79 80 83 84 8' 86 87 88 8. 90 " .2 <br /> YEAR <br /> <br /> <br />Figure F-3. A decline in manganese and cadmium concen- <br />trations after 1990 in drinking-water wells near the River Glatt <br />in Switzerland was attributed to decreased phosphate in the <br />river and hydrologic and biogeochemical interactions between <br />river water and ground water, (Modified from von Gunten, <br />H,R" and Lienert, Gh" 1993, Decreased metai concentrations <br />in ground water caused by controls on phosphate emissions: <br />Nature, v, 364, p, 220-222,) (Reprinted with permission from <br />Nature, Macmiifan Magazines Limited,) <br /> <br />29 <br />