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remaining territories is provided in Section 2.1 above, one notable increase h occurred in the Sebastian Highlands -Unit 17/Pelican Island Elementary School south f subpopulation cluster, where the scrub -jay territories increased from 3 to 5. This increase in territories was a result of territory budding by 2 colorbanded males. r i, The Sebastian south subpopulation also includes the Wabasso Scrub Conservation Area cluster containing 2, possibly 3, breeding pairs. The Wabasso Scrub Conservation Area is located just south of the incorporated limits of the City of Sebastian (see Figure 2). The Wabasso Scrub Conservation Area is less than 1 mile south of the Pelican island Elementary School/Sebastian Highlands Conservation Area scrub -jay subpopulation (see Figure 2 - "Unit 17 Conservation Areas"). The Wabasso Scrub Conservation Area scrub -jay families were colorbanded in support of demographic studies during 1988 through 1991 (Toland 1995, unpubl. ,data). Several dispersals between this cluster and the Pelican Island Elementary School cluster occurred between 1990 and 1993 (Toland unpubl. data) Two colorbanded scrub -jay families were monitored at the Wabasso Scrub Conservation Area through the 1996-97 breeding season. These families primarily occupy the north one-half of the conservation tract. The 1998 survey conducted at the Wabasso Scrub Conservation Area in support of this HCP found that these 2 families continued to occupy nearly the same habitat areas. However, a third pair of unhanded scrub -jays was observed foraging in the northernmost section of the habitat restoration parcel that was mechanically renovated in January 1998. This area is adjacent to, and south of, the two historic territories (Toland unpubl. data). "Therefore, the 1998 nesting season included a total of 2. distinct Florida scrub jay I it possibly pioneering a territory in the restored area. ' ries and a third a Y p J ternto p p Each of the 2 colorbanded scrub -jay families at Wabasso Scrub Conservation Area included 2 juveniles as recent as August 6, 1998. Therefore, their mean annual productivity was 2.0 nutritionally -independent young per pair per year. Nesting was not recorded for the third and newest pair of scrub -jays that were observed foraging in the northern section of the habitat restoration parcel, as well as on tile adjacent golf course. Although the number of territories (2) remained stable on the Wabasso Scrub Conservation Area from 1988 through 1998, individuals per family had been declining prior to habitat restoration in 1998 (Toland unpubl, data). Implementation of the Wabasso Scrub Conservation Area Habitat Restoration and (Management Plan (SES 1996) during early- 1998 initially appears to have been successful in restoring habitat conditions that are suitable for recruitment of an additional scrub -jay on this conservation tract. Additional habitat restoration and management activities, as covered under this HCP, are needed on Wabasso Scrub Conservation Area to optimize the scrub habitat for use by scrub -jays. 39