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<br />Sequoia Ecological Consulting, Inc. <br />CalVTP Project-Specific Analysis and Addendum <br />Augustin Bernal Community Park Fuel Reduction <br />November 2025 <br />2-15 <br /> <br /> <br />prevention. Invasive plants can be spread when crews and equipment travel between sites, transporting <br />soil and mud contaminated with seeds. <br />2.5.1. Sudden Oak Death <br />SOD infects coastal forests throughout California and Oregon and kills susceptible species, including valley <br />oak (Quercus lobata), coast live oak (Q. agrifolia), California black oak (Q. kelloggii), canyon live oak (Q. <br />chrysolepis), and Pacific madrone (Arbutus menziesii) saplings. Host species that are in the treatment area <br />include California bay laurel (Umbellularia californica) and coast redwood (Sequoia sempervirens). To avoid <br />the spread of this pathogen, all hand equipment and boots worn by treatment crews would be sanitized, <br />and heavy equipment, hosed off, prior to operations in areas where the spread of SOD is possible. The <br />California Oak Mortality Task Force offers additional information regarding treatment and disposal <br />measures for plants infected with SOD, which would be monitored for changes in SOD treatment <br />recommendations (California Oak Mortality Task Force 2023). <br />2.5.2. Pitch Canker <br />The fungal disease commonly referred to as pitch canker affects many pine species and can infect <br />Monterey pine (Pinus radiata). Most California native pines are susceptible to pitch canker, but Monterey <br />pine is the most widely affected host. To avoid the spread of this pathogen, the same measures described <br />above to prevent the spread of SOD would be implemented. The Pitch Canker Task Force offers additional <br />information regarding treatment and guidelines for handling woody material infected by pitch canker <br />fungus, which would be monitored for recommendation changes (Pitch Canker Task Force 2023). <br />2.5.3. Yellow Starthistle <br />Yellow starthistle is an annual that germinates in February and March and matures in June and July. It <br />produces viable seeds at late senescence of the flower head, and it is therefore vital to control before that <br />point. Management would strategically combine chemical, manual, and mechanical (mowing) methods <br />for removal. Physical methods should focus on reducing seed production and preventing seed <br />germination. Methods for yellow starthistle removal would be based on treatments described by the Cal- <br />IPC. Effective and common treatment methods for yellow starthistle include mowing and focused <br />herbicide application, but other methods may be used as determined by a professional. <br />2.5.4. French Broom <br />French broom is a particularly ignitable invasive species known for its ability to shade out seedlings, <br />replace native plant species, and carry fire into tree canopies. This species creates a large seed bank and <br />readily resprouts from the root after cutting, freezing, or fire (Cal-IPC 2020). Removal of French broom is