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<br />II- ' <br /> <br />216 <br /> <br />BRIAN D. RICHTER ET AL. <br /> <br />Ecological AppUcath:ms <br />Vol. 13, No, 1 <br /> <br />Boy 24 San Pedro River~ Arizona <br /> <br />In the upper San Pedro River .basill of southern Arizonai wate.r managers and conservationists argued <br />for mqre than a decade about the causes of measured declines in river base flows and the degree to which <br />continued groundwater -pumping for nllmicipal and agricultural use might affect the river ill the future <br />(CoITlmission 011 Environmental Cooperation ) 999). In 1998., under the leadership of the Arizona De.. <br />partment of Water- Resources, representatives frOln federal and state agencies, 111unicipal governments, and <br />conservation organizations agreed to step back from this debate and work together on a plan to nleet both <br />hU~l1an and ecosystem water delnands over the long run (Upper SaIl Pedro River Partnership 1998). They <br />fornled the Upper San Pedro Partnership to seek consensus-based ideas for reducing human inlpacts, for <br />organizing ecological research to -exalnine nlore rigorously the water needs of the riparian eco~ystem along <br />tbe l.iver, and for reassessing the groundwater models that nave been developeq by. various parties. <br />The paltnership ha:s .collaborated on an ambitious work plan including a variety of water conservation <br />activ~ties, recharge of treated wastewater effi1.l,ent, and retirel1'1el1t of water-consumptive agriculture. The <br />partnership committed more than $18 X 106 (U.S. dollars) to the effort during the first two years. In this <br />casep Step 4 of the framework (Fig. 2) was predicated on reiteration of Steps 1......3t and U)e Upper San" <br />pedi'O Partnership i's an inlportant ex.alllple of revisiting and possibly 1110difying e'cosyste111 flow r"equire- <br />ments. The willingness of the lnajor stakenolders to reexamine both human water needs and ecosystem <br />flow requirelnents ill a collaborative setting was an important ,breakthrough. + <br />This exafuple illustrates the fact that the tinle frames required for developing an ecologically sustainable <br />water manageznent plan can take .decades. The example from the Green River in Kentucky (see 'Box 1) <br />sugge~ts that quick progress is s?metimes possible and always. desirabte~ but hardly assured. <br /> <br />man.uses wiH likely have arisen, Evell when attempts <br />to resolve ifK:ompatib-ilities are purs.ued collaboratively <br />and earnestlyp water ulapagers nlay remain uncertain <br />about the feasibility of specific proposed modi:fication~ <br />to wate~. management. or river scientists will be un- <br />certain about expected ecological responses, <br />Unfortunately, thes~ uncertainties cOlllmonly cause <br />a breakdown in collaborative dialogue, When water <br />managers, scientists, water users, and conservati9nists <br />are asked to "cut a deal t, in the presence of substantial <br />1:111certainty, one or more parties may balk~ thus delay... <br />ins or telminating the search for cornpatibIe solutions, <br />However. by instead franling critical Ullcertainties as <br />hypothese~ that can be tested and resolved through wa- <br />ter managel11ent ,experiments, paralysis may be avoid-:- <br />ed. <br />Water. managen1ellt experiments mu'st be carefuliy <br />designed and executed if they are to yield the desi.red <br />reduction of uncertainty, however. It is essential that <br />scientifically credible experimental designs be em- <br />ployed to the extent feasible. If the experiment is not <br />intended to last for many. years, the selected response <br />variables should be adequately sJensitive to ~nable de- <br />tection of response d\lring the term of the experiment: <br />Most important is the formulation of testable hypoth- . <br />eses based upon conceptual lnodels - of the expected <br />response of the hydrologic and ecological, systems to <br />the ,vater management experiments (Richter and Rich- <br />ter 2000). These experiments must be carefully ll1ea- <br />sured or Iuonitored4 And of course, adequate financial <br />support must b~ provided4.-Without appropriate design, <br />evaluation, and fLulding, such water management ex'- <br /> <br />periments can backfire by introducing additional con- <br />fusio.n a oout ca.use and effect, and result in increa~d <br />frustration that can badly damage collaborative efforts. <br />The action plan developed by. the Upper San Pedl'o <br />Partnership (s:ee Box 2 for San- Pedro River, Arizona) <br />includes a number of water managenlent experiments <br />.designed to reduce- human itnpacts on groundwater <br />flows. For instance; wastewater fr0111 the City or Sien.a <br />V ista will now be inj ected back into the groundwater <br />aquifer rather than continuing to release it into evap- <br />orative ponds. Also, water conservation measures are <br />being implemented by various tllunicipalities and a 111il- <br />ita:ry base4 .The hydrologic impr0veme~t.s associated <br />with these water management experiments have been <br />modeled using groundwater shnulation models, but <br />verifying their actual bellefits will require careful mon.. <br />itoring. If these experiments suggest that less actual <br />benefit is attained than expected, the partnership will <br />. need to i denti fy additi onal me asures or broader app Ii- <br />cation of their measures to realize succeSS4 <br /> <br />STEP 6: DESIGNING AND IMPLEMENTING AN <br />ADAPTIVE WATER MANAGEMENT PLAN <br /> <br />The last step of our framework should never be com- <br />pleted; to be ecologically sustainable, water mallage- <br />ment should be perpetually informed by Inonitoring, <br />carefully targeted researchj and further experimenta- <br />tion to address new ullcertainties or,surprises, and man.. <br />agelnent approaches must be continually modified in <br />light of increased understanding or changes in human <br />and ecosystem conditions. While much has been writ- <br />ten about adaptive ecosystem management, we wa.nt to <br /> <br />J <br />