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4 Environmental Analysis <br /> 4.4 Biological Resources <br /> specified in the conditions of Project approval (see SJMSCP, Section 5.2.2.1b). <br /> The results of the preconstruction surveys shall be submitted to the Implementing <br /> agency prior to start of construction. <br /> Before Project construction, and under the direction of a qualified biologist, a <br /> wildlife exclusion fence shall be installed at strategic locations (e.g., where a work <br /> area occurs within 500 feet of suitable breeding habitat). The exclusion fence will <br /> remain in place and be maintained for the duration of ground disturbance. The <br /> wildlife exclusion fence will be tall enough to discourage dispersal of western <br /> spadefoot into active work areas. Any damage or gaps in the wildlife exclusion <br /> fence will be repaired immediately during routine inspections. <br /> For impacts to spadefoot toad upland dispersal habitat, compensatory mitigation <br /> shall be completed by the Project owner in accordance with the mitigation ratios <br /> and requirements in the SJMSCP. Compensatory mitigation may be combined with <br /> other special-status plant and animal species, such as the CTS. <br /> San Joaquin Coachwhip <br /> The San Joaquin coachwhip (also called the San Joaquin whipsnake) is covered under the <br /> SJMSCP, but is considered of very limited distribution in the County and specific Incidental Take <br /> Minimization Measures are not provided for this species (see Section 5.2.4.9). This species is not <br /> a focal species in the EACCS. The following measure would be implemented in accordance with <br /> the SJMSCP to mitigate impacts to this species in all Project areas: <br /> A qualified biologist shall conduct preconstruction surveys prior to (or, for some <br /> Incidental Take Minimization Measures, during) ground-disturbing activities to <br /> determine if SJMSCP Covered Species are present and/or verify that the <br /> appropriate Incidental Take Minimization Measures have been implemented, as <br /> specified in the conditions of Project approval (see SJMSCP, Section 5.2.2.1 b). If <br /> any special-status reptiles are found and cannot or do not move off-site on their <br /> own, work would not begin until coordination with the USFWS and/or CDFW has <br /> occurred to determine the appropriate course of action. Incidental Take <br /> Minimization Measures shall be formulated by the Technical Advisory Committee <br /> (TAC) and approved by the Joint Powers Authority (JPA) with the concurrence of <br /> the Permitting Agencies' representatives on the TAC in accordance with the <br /> SJMSCP's Adaptive Management Plan (see Section 5.9.4). <br /> Special-status Vernal Pool Invertebrates <br /> The longhorn fairy shrimp and vernal pool fairy shrimp are covered species under the SJMSCP <br /> (see Sections 5.2.4.4 and 5.5.9). Per the SJMSCP, if final site design is confirmed to be within <br /> 250 feet of the ephemeral pond, then one of the following will occur: <br /> 1. Receive concurrence from USFWS that the ephemeral pond does not support special- <br /> status vernal pool invertebrate species given the lack of ponding observed in historic aerial <br /> imagery. <br /> 2. Conduct pre-construction surveys in compliance with current USFWS protocols to <br /> determine the presence or absence of longhorn fairy shrimp within ponds southwest of 1- <br /> 580 unless complete avoidance of vernal pools and/or wetlands is achieved, per Section <br /> 5.2.2 of SJMSCP. <br /> 3. Conduct a hydrologic study to determine if a setback less than 250 feet would maintain <br /> the hydrology of the ephemeral pond and achieve the same, if not greater, habitat value <br /> Griffith Energy Storage Project 4.4-41 Tetra Tech/SCH 2022120675 <br /> Draft Environmental Impact Report August 2023 <br />