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5.7 Biological Resources

               populations within the Mitigation Preserve and promoting the distribution of this species in
               the Project region through the propagation of new or expanded populations in the Mitigation
               Preserve. The expansion of the local population of this species is expected to increase its
               potential to be sustained in perpetuity.

               Sylvan scorzonella is a CRPR 4.2 species. Numerous occurrences (roughly approximated at
               500), were identified on the Project site in 2004 and, in 2008 the number of individuals
               observed  across  the  site  likely  exceeded  100,000  plants.  This  species  was  observed  in
               scattered patches in grasslands predominately east of the Aqueduct. It was most commonly
               found  on  the  upper  north  sides of  ridges  and  hills,  and  on  slopes and flats immediately
               bordering ephemeral drainages. Nearly all occurrences were located within grasslands; a
               few were in areas bordered by oak woodland (Vollmar Consulting 2004). In 2015, estimated
               population  counts  exceeded  100,000  and,  as  in  previous  years,  it  was  observed
               predominately  in  grasslands,  but  was  also  noted  to  occur  in  scrub  habitat.  Project
               implementation would remove most occurrences of this species on the site. As discussed
               above, the County of Los Angeles Department of Regional Planning typically does not require
               mitigation for impacts to CRPR 4.2 species. However, due to the lack of botanical knowledge
               in the region for this species, the level of impact is difficult to ascertain and therefore the
               impact is considered potentially significant. Implementation of MM 7-1, proposed to mitigate
               for impacts to special status plants, would reduce the level of impact by preserving existing
               populations within the Mitigation Preserve and promoting the distribution of this species in
               the Project region through the propagation of new or expanded populations in the Mitigation
               Preserve. The expansion of the local population of this species is expected to increase its
               potential to be sustained in perpetuity.

               Piute Mountains navarretia is a CRPR 1B.1 species. It was observed on the Project site in
               2004 at 3 locations, with approximately 20,100 total plants. Occurrences on the site were all
               located in the hills in the far western region of the Project site, associated with clay soils in
               areas that had been recently disturbed by feral pigs. These occurrences represent the only
               known occurrences for this species in Los Angeles County and the southernmost known
               occurrences. However, this population is outside the Project impact area; as such, impacts to
               this species are not expected to occur and no mitigation for this species would be required.

               Adobe  yampah  is  a  CRPR  4.3  species.  In  2004,  one  occurrence  of  this  species  with
               approximately  16  individuals  was  identified  on  the  Project  site.  It  was  found  in  native
               grassland habitat on a dry, moderately steep slope with bare soil and low total vegetation
               cover south of SR-138 (Vollmar Consulting 2004). In 2006, three occurrences were identified
               including  approximately  15  individuals.  In  2008,  approximately  108  individuals  were
               observed. In 2015, approximately 100 occurrences were recorded in the survey area, with
               an estimate  of 3,100  individuals. Project implementation  would  result  in  impacts  to
               approximately 1,490 individuals. On Liebre Mountain, this species has been described as
               “generally infrequent and scattered in open chaparral and grassland on the higher ridges,
               but locally common in clay-rich openings on the north face of Sawmill Mountain” (Boyd
               1999); Sawmill Mountain is located about ten miles southeast of the Project site. Like CNPS
               4.2 species, although CRPR 4.3 species are considered special status species, impacts on
               CRPR  4.3  species  often  do  not  meet  the  significance  criteria  under  CEQA  to  require
               mitigation. However, due to the lack of botanical knowledge in the region for this species, the

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