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<br /> <br />I <br /> <br />I <br /> <br />11 <br /> <br />I <br /> <br />t lrne of con[erlt~ation values were com~'llted from an ern~)erical equatjofl <br />i f! S (I i I C (I n S E' t~ \/ a t j (I n S E' t- vie e En 3 j nee t" i rl 8 F i f:.l I d iT1 a n L:. a! ~~ C hap t e t- ;2, <br />I f1terpjE'd fOt" srlli::.l i t"LH" a I wat~.?t.sherjs. <br /> <br />I <br /> <br />-rc=[L^CI.8((1(\OO/CN)-9)^O.7J/1140(Y^O.5) <br />Tc= tirne of corlcentration in hours <br />L= flow ler'lgttl in feet <br />eN= t-u~off cut"ve number <br />y= average watershed slope <br /> <br />I <br /> <br />I <br /> <br />Y~100CI/A <br />y= average watershea siope In percent <br />A= drainagE: area in square feet <br />I ~':: C ontour- i ntE.'t-va.! in feet <br />c::= t (I t~. i C (I n t (I u. t" 1 e r::3 t: h j n fee t <br /> <br />I <br /> <br />I <br /> <br />11:; was determined at a rneetins on Jan. 6f i~~~ ttlat the Rational <br />Formula (Q=CIA) would be useful to the city in Nlaking site speCific <br />pea~( discharge computations. The!'"efore the TR-20 dischargE vaiues <br />oeternline,j for" t~ljs study couid be used to develop necessa~y runoff <br />coe+'fic!t.nts ~c: ValUE!!::.) for- local use.. <br /> <br />I <br /> <br />S'rlce t~le BeS 24 ~Iour type II rainfal I distritrution was used irl TR-Z0, <br />iT should also be used to determine rairlfaI I inter:sity values (I). <br />f'r1ost of the appl ic:ation of the r~ationai f'ot~roula wi jl be for" sma! I <br />(j~-ajr!a8e aXf?a.s '..Jhpre tt'le time of concentr"ation i~l le':;.s tha.n :~:O <br />IT:irlutes. Therefore a rainfal I duratjofl of 30 minutes was selected f(.v <br />tet2rmirlirlg I. l'he 8~eate5t 30 minu'~e interlsity ir"clm the BCS 24 hour- <br />type II rail1fal I dlstributiofl produces 37.8 % (If t~le total 24 hour <br />t-ainfal I dept~. Ttlis 30 minute r~infal I depth was determined for eacri <br />storm frequency of interest and then converted to inches per ~Iour fOt- <br />IjS~ as I, see Table 2. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />Tf!e rational formula was rearranGed (C=Q/IA) to ((Impute C values usiG8 <br />previollsly determined Q and A vaiues from TR-20 data, and I values <br />previously discussed. A tHelationship between C values and curve <br />nl_Frlbet~s (eN) ft-orn TF:--;2:0 was estab i i shed. eN va! ll€'S fOt~ the TF\-20 <br />watersheds reflect weighted average CNs for a variety of land uses and <br />~.oils within each water~shed. The cr\lS 8enet~al1y did not e;'~ceed the low <br />:::(15. Since the t"'a.tional equation may be used fOt" smallet~ individual <br />land us-es. and -::;.(lils, such 3.S a. city block of cOfl1rnet~cial buiidinss, tne <br />C.~s ftHom TR-2(1 may not be sufficiently site specific. TtlEt-efore for <br />iarld uses with eNs greater than the low 80s, a table (Table 14-1) from <br />tti2 Ill"'landbook of App lied Hydt~o J 08yl1 by' Ven Te Chol.v was usef'u J in <br />selecting C values for rnore site specific types of land uses. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br />