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1999-287
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1999-287
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Last modified
1/12/2024 2:10:06 PM
Creation date
1/12/2024 12:27:03 PM
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Template:
Official Documents
Official Document Type
Miscellaneous
Approved Date
11/16/1999
Control Number
1999-287
Subject
Final Draft for Sebastian Area-Wide FL Scrub-Jay Habitat Conservation Plan
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Breininger et al. 1995; Breiningor and Oddy 1998). Management Of the matrix <br />habitat types as low, open habitat areas enhances the dispersal potential of scrub <br />jays (Breininger and Oddy 1998), The spatial arrangement of habitat structure affects <br />demographic success and must be considered in management for population <br />persistence of Florida scrub -jays (Breininger et al. 1991, 1995, 1998a; Duncun et al. <br />1995; Breininger and Oddy 1998). Mesic flatwood forests that were observed to be <br />present on historical imagery within the Scrub -Jay Habitat Compensation Areas and <br />are located >328' (100rn) from focal scrub habitat types were not classified as <br />potential scrub -jay habitat to be covered Under this HCP. <br />Each habitat polygon was also evaluated to define management needs for restoration <br />to conditions that are optimal for scrub -jays. This includes habitat quality <br />considerations of pine thinning and shrub height class It also defines the current <br />extent of habitat use by existing scrub -jay territories to avoid negative impacts to <br />management actions. <br />these territories as a result of proposed habitat restoration and i n <br />The acreage of habitat currently used by scrub -jays on the Scrub -Jay Habitat <br />Compensation Areas was determined to assist in the determination of the regulatory <br />sufficiency of this HCP. <br />Optimal scrub -jay habitat features a tree canopy cover of less than 15%. Therefore, <br />potential scrub -jay habitat polygons exhibiting a tree canopy cover of greater than <br />15% are recommended for pine thinning. Review of Table 5 shows that pine thinning <br />is recommended within most of the habitat polygons. <br />The shrub height mapping classes evaluated for each habitat polygon included: 1.) <br />too short [entire polygon < 3.9' (1.2m) tail], 2,) optimal 1polygon exhibited a mosaic of <br />too short (<3.9' (1.2m)) and optimal (3.9-5.6' (1.2-1.7m WIWI and had no too tall <br />scrub [>5.6 (1.7m) tail] patch greater than 1 acre in size, 3.) mixed tall (polygon <br />exhibited a mix of too tall patches > 1 acre in size and short and/or optimal scrub), <br />and 4.) too tall [entire polygon was >5.6' (1.7rn tal0l. This attribute Was used to <br />classify habitat quality within the shrub stratum for purposes Of recommending <br />mechanical and fire management needs. Table 6, 11abitat Quality Classification <br />Regarding Shrub ]]eight an(I 1-labital Managetrient Needs, describes each habitat <br />quality attribute. <br />Scrub -Jay Occuparlgy Sttrclies <br />The final characteristic that was evaluated was the determination of present Use Of <br />the habitat polygon by Florida scrub -jays. As presented above in Section 3.2, the <br />known remaining scrub -jay territories located within the compensation areas and <br />affected lots were censused by SES for 51 hours between July 19, 1998 and <br />October 14, 1998 using FWS recommended methods set forth in Fitzpatrick et al. <br />(1991). Where contiguous territories did not facilitate initiation of disPutes between <br />families to define territory boundaries, occupancy of a habitat polygon area was <br />based on observed presence or absence of scrub -jays, in conjunction with an <br />AA, <br />
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