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<br />. <br /> <br />. <br /> <br />. <br /> <br />Figure 5. <br />Re-establlsh- <br />ment of Indige- <br />nous and intro- <br />duced plants <br />three months <br />after fire <br /> <br /> <br />Figure 4. Flooding and mudflows following first rain- <br />storm, Laguna Beach, November 1993 <br /> <br /> <br />538 JOURNAL OF SOIL AND WATER CONSERVATION <br /> <br />menta hIe process wherein the effort is phased to <br />allow [he highest hazard areas to be identified <br />and addressed first, followed by the: next most <br />urgent hazard areas. <br />During and immediately following the fires, <br />available informadon was gathered and re- <br />vi~ed for identification of potential haz.ards. <br />This information included storm drain maps, <br />topographic maps, geologic maps, hydtologic <br />information, and aerial photographs. Both aeri- <br />al and ground site reconnaissances were: per- <br />formed with cwo-person field teams to assess <br />the damage and ga.ther information on the po- <br />tential haz.ards caused by the fire, including <br />mud flows, debris flows. high sediment loads; <br />flooding; rockfalls; retaining structure damage; <br />and landslides. <br />Based on the gathered information, the po- <br />tential for post-fire hazards was evaluated and <br />tabulated for various sites within the burned <br />areas. Next, the impacts of those potential haz~ <br />ards were evaluated. Impacts of the pon-fire <br />hazards included public health and safety; pub- <br />lic and private property damage; damage to in- <br />frastructure (such as the storm drain system); <br />transportation route damage {such as key artery <br />loss}; or damage to receiving waters. Based on <br />an assessment of the likelihood of the hazard <br />wgc:ther with the severity of its impact, an over~ <br />all judgment was made as w which sites, if any, <br />should have the highest priority for mitigation. <br />This evaluation was a particularly valuable tool <br />for allocating resources. An example of a hazard <br />assessment matrix is presented in Table 2. <br />In both the Oakland and Southern Califor- <br />nia fires, this technique was used, and resulted <br />in mitigation efforts being focused on those <br />hazards that would have a high impact on pub- <br />lic health and safety, public and private proper- <br />ty damage, infrastructure damage, transporta- <br />tion route damage, and damage to receiving <br />waters. In all cases, these hazards occurred at <br />the urban interface areas. Where mere were po~ <br />tential hazards with a medium or high likeli- <br />hood of occurring, but the potential impacts <br />were low, then no mitigation of the hazards was <br />recommended or implemented. Typically, this <br />occurred in the more open, undeveloped areas. <br /> <br /> <br />Development of plans <br /> <br />The first step in mitigating the identified <br />high priority post-fire hazards was to develop <br />Early Action Plans that provided for immediate <br />sediment control to reduce the impact of flood- <br />ing and mudflows on developed areas. Early ac- <br />tion measures should be identified to imple- <br />ment immediately if rains are imminent. Both <br />the Oakland and Southern California fires oc- <br />curred in late October at the start of the rainy <br />season, and in both cases, Early Action Plans <br />were prepared and being implemented within a <br />week of the fites being put out. These early ac- <br />tion measures were intended to provide as <br />