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<br /> <br />Many streams are contaminated, Therefore, <br />the need to determine the extent of the chemical <br />reactions that take place in the hyporheic <br />zone is widespread because of the concern that <br />the contaminated stream water will contaminate <br />shallow ground water (see Box G), Streams offer <br />good examples of how interconnections between <br />ground water and surface water affect chemical <br />processes, Rough channel bottoms cause stream <br />water to enter the streambed and to mix with <br />ground water in the hyporheic zone, This mixing <br />establishes sharp changes in chemical concentra- <br />tions in the hyporheic zone, <br />A zone of enhanced biogeochemical activity <br />usually develops in shallow ground water as a <br />result of the flow of oxygen-rich surface water into <br />the subsurface environment, where bacteria and <br />geochemically active sediment coatings are abun- <br />dant (Figure 19), This input of oxygen to the <br />streambed stimulates a high level of activity <br />by aerobic (oxygen-using) microorganisms if <br />dissolved oxygen is readily available, It is not <br />uncommon for dissolved oxygen to be completely <br />used up in hyporheic flow paths at some distance <br />into the streambed, where anaerobic microorgan- <br />isms dominate microbial activity. Anaerobic <br />bacteria can use nitrate, sulfate, or other solutes in <br />place of oxygen for metabolism, The result of these <br />processes is that many solutes are highly reactive <br />in shallow ground water in the vicinity <br />of streambeds, <br /> <br />E <br />m <br />~ <br />Iii <br /> <br />Direction of streamflow ~ <br /> <br />\ High oxygen) <br />AerObic microbial <br />processes <br />Very fow or <br />no OXygen AnaerObic m' . <br />JCrObJal <br />Processes <br /> <br />u <br />'i;; <br />.c <br /><; <br />c. <br />> <br />:I: <br /> <br />\ Nit"'e <br /> <br />) <br /> <br />Ammonium <br /> <br />eft) <br />iJ <br />"' <br />If" <br />,,~ <br />,0 <br />o'~ <br />'o~ <br />Direct' <br /> <br />! <br />m <br />3 <br />'C <br />C <br />~ <br />o <br />t; <br /> <br />/ <br /> <br />cOmm I <br />On y low' <br />dependin In Oxygen <br />land Use 9 On geology, <br />, and presen <br />organic C b ce of <br />ar On <br /> <br />The movement of nutrients and other chem- <br />ical constituents, including contaminants, between <br />ground water and surface water is affected by <br />biogeochemical processes in the hyporheic zone, <br />For example, the rate at which organic contami- <br />nants biodegrade in the hyporheic zone can exceed <br />rates in stream water or in ground water away <br />from the stream, Another example is the <br />removal of dissolved metals in the hyporheic <br />zone, As water passes through the hyporheic zone, <br />dissolved metals are removed by precipitation of <br />metal oxide coatings on the sediments, <br /> <br />Ferric irO) <br /> <br />Ferrous <br />iron <br /> <br />I <br />Inches <br />to <br />feet <br />I <br />I <br />Feet <br />to <br />miles <br />-L <br /> <br />27 <br /> <br />Figure 19, Microbial activity and <br />chemical transformations commonly <br />are e11hanced in the hyporheic zone <br />compared to those that take place <br />in ground water and swface water, <br />This diagram il/ustrates some of the <br />processes alld chemical transforma- <br />tions that may take place ;n the <br />hyporhe;c zone, Actual chemical <br />interactions depend on numerous <br />factors including aquifer mineralogy, <br />shape of the aquifer, types of organic <br />matter in surface water and ground <br />water, and nearby land use, <br />