The pupa is initially deep green in color (which blends with the lupine foliage), eventually <br /> turning white and then pink. Ant tending of larvae is mostly absent and larvae tend to <br /> remain on the lupine foodplant during the day, feeding on the apical shoots underneath the <br /> larger leaves, and apparently never descend to the ground (Hammond 1994). Larvae appear <br /> to diapause within 1 cm. of the soil surface (Schultz 1996). <br /> Dispersal Biology: Anecdotal evidence indicates that Fender's blue may disperse as much as <br /> 5 -6 km (Hammond, pers. comm.). Census data from 1993 suggest that Fender's blue <br /> occasionally travel up to 100 m from a lupine patch and they tend to aggregate in the center <br /> of lupine patches (Schultz 1994). Stepping stones rather than a continuous corridor might be <br /> a preferred solution to insure adequate movement between populations. <br /> Nectar Sources: At Willow Creek, Fender's blue butterflies prefer nectaring on native <br /> flowers over non - native flowers (70.3% of the 182 observations). Important native nectar <br /> plants include Allium amplectens, Calochortus tolmiei, Camassia quamash, Eriophyllum <br /> lanatum, Geranium oreganum, and Sidalcea virgata. Several non - native species are also <br /> used as nectar sources, including Linum angustifolium, several species of Trifolium, and <br /> several species of Vicia. <br /> Potential Habitat Modifications: Pest plant control is a major priority for protecting the <br /> upland prairie habitat in which lupine and the Fender's blue butterfly occur. Cutting, <br /> mowing, hand pulling, prescribed burning, or herbicides, can be effective control measures <br /> against Scot's broom, blackberry, tall oatgrass, tall fescue, false -brome grass and bracken <br /> fern, species that can displace lupine; however it is imperative that the timing and type of <br /> control measure match the species and conditions so as not to harm lupine in the process. <br /> For example, early mowing of tall oatgrass would also harm lupine, thus a later mowing <br /> would be more appropriate. There is some concern that burning may facilitate the spread and <br /> growth of certain exotic species into native grasslands (Hammond and Wilson 1993). Burning <br /> could have a deleterious effect on the Fender's blue butterfly larvae since they appear to <br /> diapause within 1 cm. of the soil surface (Schultz 1996), therefore burning should be applied <br /> to a very small percentage of the habitat on a rotation basis. Large mowers may compact the <br /> soil and also injure diapausing larvae which suggests their use should be kept to a minimum. <br /> Predation and Disease: Little is known about predation rates and diseases of the Fender's <br /> blue butterfly. However, a small sample of larvae reared in captivity produced no parasites, <br /> suggesting there is a low rate of parasitism by aerial enemies (Hammond 1994). <br /> Information on Known Populations <br /> The following tables summarize the existing information on individual element occurrences in <br /> the Conservation Strategy area. For each species, the Element Occurrences are organized by <br /> ownership or management status. Within each ownership, the occurrences are listed roughly <br /> 15 <br />