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486 <br />S.M. NELSON AND D.C. ANDERSEN <br />described by early investigators as `jungle' (Grinnell, 1914; Brown, 1923). In areas of near-surface ground <br />water, salt grass (Distichlis spicata) was common (Brown, 1923). Lagoons and marshes, formed from <br />abandoned. stream channels, were often present at some distance from the river and usually replenished <br />with flood waters every year (Brown, 1923). The rarely flooded Second Bottom was characterized by <br />mesquite (Prosopis spp.), saltbush (Atriplex spp.); and creosote bush (Larrea tridentata) (Grinnell, 1914). <br />River regulation and trans-basin diversion has promoted both invasion of exotic plants and conversion <br />of floodplain landscapes to irrigated agriculture. Exotic tamarisk (Tamarix ramosissima) now often <br />dominates non-agricultural riparian areas along the lower Colorado River, and areas of original <br />vegetation types, especially those associated with the First Bottom, are very rare (Ohmart et al., 1988). <br />The prediction by Sykes (1937) that river regulation and agriculture would cause the `luxuriant vegetation' <br />along the river to become desert-like has in large part come true. In response to these changes, attempts <br />are being made to restore some tamarisk-dominated sites to a condition more like that of the historic <br />riparian ecosystem. <br />Assessment of the environmental quality of revegetated areas relative to that of the historic riparian <br />ecosystem is difficult, in part because baseline data on the structure and dynamics of desert riparian <br />assemblages maintained by a highly irregular flow regime are either limited or lacking. Despite these <br />limitations,. butterfly assemblages may be useful for. investigating these riparian ecosystems., Collection. is <br />practical, natural histories-are relatively well-known, and taxa richness is. high in most areas. Sensitivity <br />of butterfly species to environmental. perturbations varies from sensitive to resilient; with various species <br />sensitive'td vegetation changes, fragmentation of habitat; and pesticides: Although direct measurement" of <br />vegetation"'can provide insight into the effects of altered flows, vegetation °may be slow to respond fo <br />environmental change. For example, cottonwood and willow may persist for many .years in a " non- <br />functioning ecosystem: Because of their rapid response to environmental perturbation, butterfly assem- <br />blages," particularly in this situation, can. serve to integrate riparian vegetation, fragmentation, and <br />ecological processes and provide a responsive measure of biodiversity (i.e., .composition,. structure, and <br />function). - <br />b ~:jt`~ c~ 1 ..t <br />The purpose. of this study was to determine whether the structure of the butterfly assemblage associated <br />with revegei'ated sites tends towad-that'assbciated~wlth "natural'riparianxlaridsca`pes as plantings~mature <br />:,; _ <br />- ~ 3,000 <br />T <br />_ `y 2,50C <br />io <br />m <br />2,000 <br />a <br />U <br />m <br />t 1,500 <br />w <br />T <br />0 1,000 <br />m <br />s 500 <br />m <br />m <br />a 0 <br />Jsn JQn 2~°` Q~° ~s~ Jce ~~~ Jy~ ,00~ ~0~ ~0~ ,00~ <br />Aso 0~~ ~ P ~ ~ ~A OF o~0 mF OF <br />Q Q' ~OQ~ O ~p`~ Op,~+ <br />Month <br />Figure 1. Comparison of non-regulated (1904-1935, n = 32) and regulated (1936-1964, n = 29) flows in the Colorado River at <br />Yuma, Arizona. Values shown are averages of mean daily discharge by month. Vertical bars around averages enclose the middle half <br />of the data (25th to 75th quartiles). Data from US Geological Survey 1954, 1964 and 1970 <br />Copyright ©1999 John Wiley & Sons, Ltd. Regut. Rivers: Res. Mgmt. 15: 485-504 (1999) <br />