Post-Fire Erosion Control Methods

Examples and recommendations for the North San Francisco Bay Area

Debris and cleanup efforts after the 2017 California fires

In total, the North Bay fires of 2017 burned about 40,000 acres. The southern California fires were even larger, totaling 1 million acres. The fires burned a wide variety of landscapes, including whole neighborhoods in flat, urbanized areas. Unlike rural areas, these areas are served by urban infrastructure, including storm drain systems, which tie into natural waterways such as creeks, rivers, bays, and oceans. As part of the engineering community, we observed that the potential for mobilization of ash from burned lots posed a major challenge for communities recovering from urban fires. This article is intended for professionals interested in erosion control and water-quality issues in post-fire areas.

The fires that devastated the North San Francisco Bay Area in October 2017 generated large volumes of ash and debris in subdivisions and on private lots. This material includes toxic compounds and heavy metals such as lead, mercury, and copper from the combustion of homes, cars, appliances, furniture, and other man-made materials.

In the aftermath of the North Bay fires, there was a period of vulnerability after homeowners had been allowed to reenter the burned area to recover their belongings, but before cleanup of ash and debris had occurred. During this period, the large quantities of ash and particulates left behind by the fires had the potential to overwhelm traditional sediment control methods. During high-intensity rainfall conditions, runoff could send this contaminated sediment into pipes, creeks, rivers, and bays. In the wake of the North Bay fires, government agencies employed traditional methods for temporary erosion control, such as localized inlet protection with wattles, to contain post-fire ash and particulates. However, these methods could be overwhelmed by the ash and debris from an entire neighborhood that had been burned.

We propose a novel use of existing soil binding technology as a part of the cleanup efforts for urban and suburban wildfires. Biodegradable soil binding compounds, also known as tackifier, would be applied to burned lots once local authorities deemed the site safe for entry. The tackifier would prevent the mobilization of ash and associated contaminants until cleanup could occur. Once resources could be mobilized for cleanup, work crews would collect bound ash material and transport it to a landfill for disposal. This practical and easily implementable approach would help address water-quality issues by vastly reducing the amounts of post-fire contaminants getting into our waterways from residential subdivisions that have burned. The approach was developed in the context of the fires that devastated the North San Francisco Bay area in 2017, but it has wider applicability to future fires in urban and suburban areas.

Credit: FINN
Aerial application

Traditionally, soil tackifier is used for erosion control of bare soil and for hydroseeding. To our knowledge, it has not been used on ash and debris from fires. However, the application methods would be similar to those for traditional uses. The tackifier can be spread across burned subdivision lots using hydroseeding equipment or commonly found construction equipment such as a mobile water tank (a.k.a. water buffalo), a large 2-inch hose, and a commercial-grade spray nozzle. The tackifier emulsion would be dispersed across the lot until the ash is saturated, at which time the tackifier would begin to harden and bind the ash and small debris into a crust. The curing time for tackifier and soil stabilizers ranges from 4 to 24 hours, making this a quick and responsive means of addressing erosion concerns. The cost of applying the tackifier would be approximately $250 per typical lot of 5,000 square feet (Table 1).

This solution is intended for limiting water-quality problems from ash and debris on flat residential lots with grades between 2% and 5%, such as the Coffey Park neighborhood in Santa Rosa, CA, and is not appropriate for the large-scale hillside slope stability efforts that are necessary to prevent landslides and mudslides that frequently follow fires on steep slopes.

Credit: FINN
Helicopter loading area

The best time for application of tackifier would be once law enforcement allows safe entrance back into a burned lot immediately after a fire and before debris removal efforts start—and, if possible, before the next heavy rainstorm. For the North Bay fires, the ideal period of application would have been in mid-November before the US Army Corps of Engineers began cleanup work. Once tackifier is applied, a burned lot would be closed to entry until debris removal commences. While the lot waits for debris removal, the erosion-resistant crust would remain in place, preventing the mobilization of the contaminant-laden ash. Care should be taken to choose a soil tackifier that is permeable to water, allowing rainwater to infiltrate through the ash rather than sheet-flowing off it.

Credit: FINN
After application

Once cleanup begins, crews would break the crust into manageable pieces for collection and off-hauling via truck. By binding the ash particles together into a crust, this method would reduce the effort required to collect ash and debris for disposal and significantly reduce the amount of airborne dust generated. Once collected, the consolidated ash would be transported to a landfill, where it would be disposed of according to current industry practice. The soil tackifier would add a negligible volume to the debris and therefore would have a negligible impact on debris disposal fees at landfills. The soil tackifier proposed is biodegradable, allowing it to be readily acceptable at any landfill, where it will slowly decompose.

Applying tackifier to the burned lots would provide several benefits to federal, state, county, and city agencies in the wake of large urban or suburban fires. By fixing toxic materials in place, this method would protect vital waters of the US from water-quality degradation and fish and wildlife impairment. It would also reduce the higher cleanup costs associated with trying to remove the toxic materials after they have been deposited in the storm drainage systems and our natural waterways. Finally, the tackifier would limit the amount of ash mobilized into the air during debris removal and disposal, reducing the cleanup crews’ exposure to respiratory hazards from toxic dust. In summary, application of soil tackifier to address post-fire challenges would provide multiple environmental and health benefits at low cost. We look forward to investigating this novel use of soil tackifier in collaboration with the rest of the engineering community. EC_bug_web


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