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492 <br />100 <br />E <br />E <br />c <br />0 <br />.Q <br />~U <br />N <br />L <br />Q <br />a <br />c <br />0 <br />(LS <br />80 <br />60 <br />40 <br />20 <br />S.M. NELSON AND D.C. ANDERSEN <br />------------------ <br />~ l^^^ _ I I _^_.^^ l l~l In ^^^^^ I n ^^ fl n I I f ^^ 11 I II I1' <br />~~9 4. A P 6 01 0 9,~0,~~.,~q...A ti 9 M b 6 1 0 oi,~0,~'~,~'~a ~t. 9 P <a 6 1 0 N,~O,~'.,~'~(o ~L 9 b y 6 1 '0 9,~0,~~.,~~L..'~ ry A P h 61 0 9 <br />J~ J~ X66'' J~ aP ~~ a~ v~ ~° <br />Month <br />Figure 4. Total monthly precipitation in study area. Graphed values are-the mean of total monthly precipitation for Needles and <br />Blythe, California and Lake Havasu City and Parker; Arizona. Dark bars represent winter months (October-March). Data from <br />iNational Oceanic and Atmospheric Administration <br />The amount of nectar produced by a `plant growing on the xerified floodplai`r is probably related to <br />depth to groundwater. Tamarisk flowers were. abundant- at Tam, situatednext to the river, presumably <br />from the presence of shallow ground water. Revegetated sites away from the river also contained tamarisk <br />but less nectar perhaps because of a lower water table. Negative responses of nectar to high groundwater <br />were observed in some cases. High groundwater at R96 may have been responsible for Bermuda grass <br />(Cynodon dactylon) competitively eliminating low-lying nectar sources (e.g.; Melilotus, Trianthema portu- <br />lacastrum, and Heliotropium curassavicum) that were readily accessible in March 1997 but effectively <br />concealed by the grass in November 1997. <br />Assemblage analysis <br />Correspondence analysis suggested that the butterfly assemblage at BW is unique and that assemblages <br />at revegetation sites are not trending toward it. CA differentiated the butterfly assemblages of BW from <br />those of Tam and the revegetated sites in each of the three seasonal periods examined (Figure 8a-c; <br />Tables II, III and IV). The hypothesis that the CA pattern explained by the data-set was the same as a <br />randomized data-set was rejected (p < 0.05) for the first several axes for both the March and June data <br />sets. The first two axes derived from these ordinations accounted for 45% of the variation in the <br />assemblage in March and 33% in June. Only the first axis (27% of variation) differed from the random <br />data-set in August. <br />In no case did age of revegetation site result in a closer ordination to BW assemblages. Rather, Tam <br />and the revegetation sites were scattered in ordination space in a manner unrelated to age. Correlation of <br />Axis I and Axis II scores with age of revegetation sites were all non-significant (p > 0.4). However, a <br />faunal basis for the ordination patterns was evident in the differences in occurrence and abundance of <br />butterfly taxa (Tables II, III and IV). March ordination (Figure 8a; Table II) grouped revegetated sites <br />from the Cibola area that contained Pyrgus communis and Hesperopsis gracielae but lacked taxa unique <br /> <br />Copyright ©1999 John Wiley & Sons, Ltd. Regul. Ricers: Res. Mgmt. 15: 485-504 (1999) <br />