What We Monitor
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Maui Wildfire Data: What We Monitor
DOH and partners collect samples and test them for substances such as heavy metals (like lead, arsenic, cobalt, copper, and zinc), asbestos, polycyclic aromatic hydrocarbons (PAHs), dioxins, and other hazardous substances that could have been released during the fires in Lahaina and Kula. DOH also monitors whether windblown dust and stormwater runoff are still spreading fire-related substances in the environment around Lahaina. When tests detect a substance at a level of concern, DOH looks at many samples collected over time to determine whether the substance level is elevated because of the fires, for another reason, or because it occurs naturally in the area. DOH also modifies the list of substances for analysis based on initial sampling activities to focus on substances at levels of concern. As of June 2024, monitoring activities include:
- Sampling ash from burned homes in Lahaina and Kula and testing them for heavy metals, dioxins, PAHs, asbestos, and other substances of potential concern. (Visit the Ash page for more information and results.)
- Monitoring air quality with more than 50 devices mounted throughout Lahaina that continuously measure levels of particle pollution in the air. DOH also tests particles from the air to see if they contain metals or asbestos fibers. (Visit the Air page for more information and results.)
- Sampling coastal water, with samples collected by four different organizations quarterly to weekly. Samples are tested for metals (the primary substances of concern, based on ash sampling), nutrients, and other aspects of water quality. This sampling is important because hurricane-force winds during the fire blew smoke and ash far offshore, and because stormwater runoff could continue to carry fire-related substances into coastal waters. (Visit the Nearshore Coastal Water Quality page for more information and results.)
- Quarterly sampling of sediment at nine locations along the coast, starting in May 2024. Samples collected to date, including from many other locations on and near shore, have been tested for up to 85 different substances of potential concern, including metals. (Visit the Sediment page for more information and results.)
- Beach sand sampling for metals at three beaches near the burn area. (Visit the Beach Sand page for more information and results.)
- Testing of air, groundwater, and runoff (leachate) at the West Maui Temporary Debris Storage (TDS) Site near Olowalu, along with portable air monitoring during debris removal activities in Lahaina. (Visit the TDS Site page for more information and results.)
The conceptual site model below shows how these monitoring activities cover the many ways in which people could come into contact with potentially hazardous substances from the fires. As recovery continues, results from ongoing monitoring will allow DOH to make decisions that keep people safe. Providing the results of the ongoing monitoring through this portal will also empower the people of Lahaina and Kula to make their own informed decisions.
This Conceptual Site Model shows how fire-related substances could move through the environment, how people are possibly exposed, and how sampling and monitoring programs have been set up to assess the potential for exposure and inform people about potential exposures.
Monitoring focuses on three potential “exposure pathways.” These pathways are based on our understanding of how fire-related substances could move through the environment and how people could come into contact with them. The pathways are numbered in the diagram above as follows:
1. Air
Residents, visitors, and workers could breathe in particulates from the air. Measures are in place to stabilize ash and dust (Soiltac®) and suppress dust during removal activities. Multiple air monitors are continuously active and consistently show good quality air.
2. Settled Debris and Ash
Disturbed ash and debris could lead to skin contact and incidental ingestion. Safety measures protect workers during removal activities. Before allowing public access or issuing completion letters for rebuilding, samples are collected to confirm fire-related substance levels are below levels of public health concern.
3. Nearshore Water and Sediment
People could contact ash in water and sediment during recreation, especially after rain. Continued sampling shows that fire-related substance levels are below levels of public health concern, even on Brown Water Advisory days.
Table 1 provides a more detailed discussion of the conceptual site model. It identifies specific receptors (people who could be exposed to fire-related substances originating from remaining ash and debris), how and when they might be exposed, and steps that DOH and partners are taking to monitor and prevent these possible exposures. DOH looks at the actual concentrations of substances in the environment and compares them with established screening levels such as DOH’s Environmental Action Levels. The appropriate screening levels depend on factors such as the exposure route and length of exposure. Based on the wide range of sampling conducted so far, heavy metals appear to be the fire-related substances that pose the highest concern in the environment around Lahaina. One possible explanation for this result is that this particular fire was so intensely hot that it could have destroyed other substances that might typically be found after a fire. Widespread evidence of melted glass, aluminum, and even asbestos means the fire was hot enough to destroy most dioxins and PAHs, for example.
These findings mean that metals are the main risk drivers in the area. In other words, out of all the substances that could have been produced by the fire, metals likely pose the greatest risk to people and ecosystems. Therefore, ongoing sampling activities continue to focus on metals. If a particular sample reveals highly elevated concentrations of metals, it likely indicates a high concentration of ash in that area. DOH can then test that area for additional substances of concern.
Table 2 shows additional ways that fire-related substances could move through the environment, and explains why people are not expected to come into direct contact with substances through these routes. For example, some substances on land can eventually leach into groundwater, but people do not contact the leachate or use the groundwater under Lahaina for drinking water. This means the pathway is “incomplete.” Although these exposures do not currently occur, DOH will consider whether any changes in site conditions might warrant DOH and partners to reevaluate them.
Table 1. Potential exposure pathways.
COPC = Fire-related contaminant of potential concern
DOH = Hawaii Department of Health
Table 2. Eliminated exposure pathways.
Eliminated Exposure Points | Eliminated Exposure Routes | Reason for Eliminating Exposure Pathway |
---|---|---|
Food chain | Shellfish ingestion |
|
Food chain | Fruit and vegetable consumption |
|
Inland surface water and sediments | Incidental contact |
|
Groundwater | Ingestion |
|
Public drinking water | Ingestion |
|
COPC = Fire-related contaminant of potential concern
DOH = Hawaii Department of Health
Air | Ash and Debris | Beach Sand | Coastal Sediment | Coastal Waters | County Parks | West Maui TDS Site | Coral Reef Health | Drinking Water | Fish | Soil | Wastewater