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7/14/2009 5:01:47 PM
Creation date
5/22/2009 6:42:35 PM
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UCREFRP
UCREFRP Catalog Number
9530
Author
Nelson, S. M. and D. C. Andersen
Title
Butterfly (Papilionoidea and Hesperioidea) Assemblages Associated with Natural, Exotic, and Restored Riarian Habitats along the Lower Colorado River, USA
USFW Year
1999
USFW - Doc Type
Regulated Rivers
Copyright Material
YES
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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 />
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