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SWSI
Title
Comments 4
Date
10/23/2003
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<br />" 1 <br />1- <br /> <br />220 <br /> <br />BRIAN D. RICHTER ET AL. <br /> <br />Ecological Applications <br />Vol. 13, No.1 <br /> <br />these flow guidelines have not received n1ucp attention ervoir operations) and other water management issues. <br />from the states and their proposals have not addressed In turn, the output of these n10del runs by the states <br />theJ1'l in any explicit way. This neglect can be largely has _ been analyzed by the federal enVirOn1l1el1tal agen.. <br />explained by' the reluctance ~of the _negotiators to use cies to assess incompatibilities with their instrean1 flow. <br />flow targets that they felt had not been adequately guideHnes~ <br />linked to desired floodplain of chanllel conditi011S and' There has been disagreenlent over some of the key <br />ecological responses~ While the federa.l flow guidelines inputs to these models", including the relationship be- <br />were supported with a narrative that described the "gen- twee.il grow'ldwater pumping and rlver flpws, irrigation <br />eral importance of the specified flow conditions for .delIla.nds, and other water use projections. Tremendous <br />sustaining species and ecosystem health, the numerical effort was expended in assembling a COll)!nOn set of <br />.targets were based primarily on statistical character... input data for the hydrologic models, but so~e key <br />izatioll of the histo~ical flow regime because the federal inputs such as irrigation water consunlPtion during <br />agencies hoped to preserve as much of the historicaI" . droughts was ~ery difficult to estilnate due to . lack of <br />flow conditions as possible. The" negotiators wanted to l'llonitoring data~ The lack o~agreement on model input <br />better understand ho\v'a flow ofa particular level would has been an obstacle in the negotiatiqns, because it has <br />fill the, channel, inundate the fioodpLaint or otherwise made comparisons of the states' proposals difficult. <br />affect biota in particular reaches. <br />Fortunately. work conducted dw~ing the Conlprehen.. <br />sive Study did provloe infornHltioll about instrealTI hab- <br />itat ava"ilability in the Apalachicola River at various <br />low-flow levels, an~r identified high-flow levels at <br />which fish gain access to secondary channels and back- <br />water areas ill the floodpiain (Freeman et a1. 1997. Light <br />et al. 1998). The Florida negotiators relied heavily upon <br />these limited sttldles in framing their watei. allocation <br />proposal, while .also trying to protect as much of the. <br />natural flow regill~e as possible (S. Leitnlan, Orn::oOOD <br />em 0 ftJO[[JDrffi). <br />We believe the lack of adoption of any form of con- <br />sensus-derived e;cosyste1l1 flow requirements greatly <br />hindered the ACF basin negotiations. Before any set <br />of flow guideIin"es can he fully employ~d in the fashion <br />suggeste-d by Steps 1-3 of our fraluework, the stat~s <br />and federal agencies lllUst reach consensus on ecosys- <br />tenl flow requirenlents. One way to facilitate such con- <br />sensus might be to convene a more forn1al and rigorous <br />. scientific assessment of 'ecosystenl flow requiremeiits, <br />engaging multidisciplinary aCadeJ11ic and agency sci- <br />entists fronl each of the three states and beyond. An <br />excellent model for such structured assessment is the <br />B llilding Block Methodology being employed in South <br />Africa (King and .Louw 1998). <br /> <br />DCOOJOQIJDO 00000 DO 1JITlOJJ <br /> <br />The C0111prehensive Study produced estimates of ex.- <br />isting and pl.ojected water den1ands for M and I, ag- <br />ricultural, and other uses. Subsequently, hydrologic <br />sinlulation models were developed to enable as~ess- <br />ment of daily flC?w regimes at 14 different locations in <br />the basin. Alternate water management s:cenarios can <br />be explored by n'lodifying projected water denlands and <br />reservoiI' operations in the models. <br />Each of the tItree states has u.sed these hydrologic <br />ITIodeJs in developing their water allocation proposals <br />for consideration by the other states and federal tep... <br />reselltatives~ Each state has modified the 11lodel(s) to <br />reflect key elements of their respective proposals, e.g., <br />projected growth in \vater cons1.l111ptionj proposed res- <br /> <br />o CDJD DO OiJITJO OOOf[J[][[il]] <br /> <br />While the ACF basin lies within the cOInparatively <br />water-rich Southeast, periodic episodes of droughts of- <br />ten lasting for multiple y~ars) ,do occur. During a <br />" drough t from 1999 to 200] the annual flows in the river <br />were only 40% of average. Such periods of drought <br />have become the nexus of conflict between human and <br />ecosystem needs for water. For example, l11aintaining <br />high reservoir levels for recreation and preserving wa- <br />tel' storage during droughts conflicts with needed re- <br />leases.- for water quality,. hyd1.~opowerJ navigation, and . <br />ecosystenl flo\vs. These conflicts are most acute during <br />. the summer) when naturally low river flows are depleted <br />by various human uses. In the negotiations3 suggestions <br />were made to cw.tail or constrain certain uses to enable <br />other llses to be met adequately. <br />The federal instream flow guidelines include t\.vo <br />low-flow parameters (Table 1): a linlit on the one...day <br />Ininiml.lm flow in each nloi1tb and a !inlEt on the max- <br />iInUll'l numb~r of days in each year that fio\vs can be <br />below a certain threshold. The water allocation agree" <br />l11ent fails to nleet these low-flow guidelines in SOlne <br />years (Fig~ 5). Therefore, the ecological sustainability <br />of this water allocation remains in question. <br /> <br />ODD [[[j!TIl rm mrnumo <br /> <br />The original deadline for arriving at "an acceptable <br />allocation formula was set by-the Compact far 31 De- <br />cember 1998, but the deadline was extended more than <br />10 times. The states are highly motivated to achieve a <br />negotiated agreement; the alternative is to resolve the <br />issue in the U.S. Supreme Court. The wa.ter allocation <br />pToposals submitted by each of the states have provided <br />the basis for the negotiati.ons. The hydrologic models <br />and analyses of their outputs have proved to be valuable <br />tools for developing, communicating, and assessing a <br />variety of ~vater management alternatives. Stakeholder <br />lneetings, technical meetingsl and workshops and other <br />private meetings have been conducted both inside and <br />outside of the formal negotiations. Each of these venues <br />offered an opportu,nity to .share infor.mation~ present <br />
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