In the late 1990s, a state maintenance yard in Bellingham, Washington, became a test site for mycoremediation. Researchers from Battelle’s Marine Sciences Laboratory and the Washington State Department of Transportation built mounds from old soil contaminated with diesel. One mound got oyster mushroom mycelium, others got bacteria or nothing, and the team watched for four months.
The story that spread afterward was simple. Oyster mushrooms sprouted across the treated pile and the fuel was said to be mostly gone. Paul Stamets, the mycologist most associated with the test, later reported in talks and books that more than 95 percent of the aromatic hydrocarbons had been destroyed.
The official report, published in November 1998, reads differently. It found that the results “were not conclusive in distinguishing the outcome of the various treatments”, mainly because the contamination was spread unevenly through the mounds and the fuel was heavily weathered. Together, the two accounts show where mycoremediation stands today.
What mycoremediation is
Mycoremediation is the use of fungi for cleaning contaminated soil or water. It is one branch of bioremediation, the family of remediation methods that put living organisms to work. Most bioremediation is done using bacteria. Mycoremediation uses the mycelium, the thread-like underground body of a fungus, and the enzymes it releases.
Stamets popularized the term in his 2005 book *Mycelium Running*. Fungi have been studied for remediation for longer: U.S. government scientists were testing wood-rotting species on contaminated soil in the early 1990s.
How fungi degrade petroleum and PAHs
The main workers are white rot fungi, which decompose dead wood, and relatives such as the oyster mushroom (*Pleurotus ostreatus*). Fungi are expert decomposers of organic matter. To digest lignin, the tough polymer in wood, they release enzymes into the soil around them. Lignin is built from irregular ring structures, and so are many petroleum hydrocarbons, including polycyclic aromatic hydrocarbons (PAHs), the toxic and persistent part of crude oil and diesel.
A 2012 review in *Biotechnology Research International* names four enzymes that start the degradation of PAHs:
- Lignin peroxidase, which pulls electrons from the PAH molecule
- Manganese peroxidase, which works mostly through free radicals
- Versatile peroxidase, a hybrid of the two that has been studied far less
- Laccase, an oxidizing enzyme that gets much stronger with helper molecules
This matters because the enzymes have low substrate specificity: they are able to attack many different organic pollutants. Their first products are usually quinones, which dissolve in water more easily. Soil bacteria then break down the quinones further, which makes biodegradation a joint microbial process of fungi and bacteria. Some species can also turn PAHs all the way into carbon dioxide.

What the field tests found
Biodegradation rates in the lab are often impressive. Field results are mixed. The table lists documented projects.
| Project | Year | Contaminant | Reported result |
|---|---|---|---|
| Brookhaven, Mississippi (U.S. EPA field demonstration) | 1992 | Wood-preserving waste: PCP and creosote PAHs | 64% less PCP in 20 weeks vs. 26% and 18% in control beds; 5- and 6-ring PAHs barely changed |
| Bellingham, Washington (WSDOT and Battelle) | 1998 report | Aged diesel in soil | Inconclusive due to uneven contamination |
| Orleans, California (community clean-up) | reported 2017 | Diesel and motor oil at a community center | Practitioner reported over 90% reduction after more than 18 months; not peer-reviewed |
| Ecuadorian Amazon fungal strains (lab study) | 2025 | Total petroleum hydrocarbons | 95.7 to 99.3% removed in 60 days vs. 12 to 24% in controls |
| Louisiana sweet crude (NOAA-hosted lab study) | 2025 | Crude oil in brackish water | Oyster mycelium grew at estuary salinities and changed hard-to-degrade oil fractions |
The EPA trial is the most carefully documented. Its site profile from the U.S. EPA Bioremediation Field Initiative blames heavy rain for the weaker field result: the beds could not be tilled on schedule and probably lost oxygen, and the fungal inoculum was less active than planned. The agency still called the result encouraging, because the fungi handled PCP at about 1,000 mg/kg, roughly ten times the level bacterial treatments usually attempted at the time.
The Orleans project sat near the Klamath River on Karuk tribal land. According to local press, the Mid Klamath Watershed Council led it and local tribes monitored it. Workers layered the contaminated soil with straw and burlap carrying oyster mushroom mycelium.
The Ecuador study used strains native to the Amazon, where decades of drilling left soil contaminated with petroleum. Its authors, from Belgian and Ecuadorian universities, stress that the results come from controlled lab microcosms and still need testing in the field.

What fungi cannot do
Supporters see mycoremediation as a low-cost, low-energy way to treat fuel spills on land, with real potential for community projects. Many researchers agree this chemistry works, but they point to clear limits:
- Heavy metals and other elements are never destroyed. No organism can degrade lead, cadmium or mercury. Fungi can bind and concentrate metals in their mycelium and mushrooms, but those mushrooms then become hazardous waste.
- Big molecules resist. The EPA trial saw little change in 5- and 6-ring PAHs. A 2023 review in the *Journal of Fungi* calls low removal of long-chain hydrocarbons a major limitation compared with thermal treatment.
- The process is slow. Lab tests run from a few weeks to three months; field projects have run from four months to well over a year.
- Fungi need food. White rot fungi generally cannot live on pollutants alone. They need a carrier such as straw, wood chips or spent mushroom substrate, plus oxygen and moisture.
- Native microbes compete. Introduced strains can lose out to bacteria already in the soil.
- Scale is unproven. The same review says mycoremediation is “widely studied at lab scale” but has few pilot-scale trials and no registered large-scale methods.
These limits matter for related environmental problems. Soil from military sites, for example, often holds metals and radioactive material such as depleted uranium, which fungi can concentrate but never neutralize.
Mycoremediation compared with other bioremediation methods
| Method | Main worker | Good at | Weak spots |
|---|---|---|---|
| Bacterial bioremediation | Native or added bacteria | Fresh fuel spills, lighter hydrocarbons | Large aromatic molecules, very high concentrations |
| Mycoremediation | Wood-decay and other fungi | PAHs, PCP, dyes and other ring-shaped pollutants | Needs substrate and oxygen, slow, few field trials |
| Phytoremediation | Plants and root microbes | Large, lightly polluted areas; some metals | Shallow reach, takes years |
| Excavation or thermal treatment | Machines and heat | Fast, predictable results | High cost and energy use |
The methods overlap in practice. Fungi start the breakdown and bacteria finish it, which is why some research teams combine fungal species with bacterial strains.
Science and speculation
Stamets brought fungi to a broad audience, and his books inspired many community projects. Some of his wider claims go well beyond what has been measured, such as describing mycelial networks as a natural internet of the planet, or fungi as an answer to many global problems at once. The measured science is narrower: certain fungal species break down certain pollutants under the right conditions.
This gap means each project needs its own environmental measurements. The approach fits the thinking behind natural capitalism, which tries to put biological processes to work.
If your community is considering a fungal clean-up
Practical steps drawn from the documented trials:
- Test first. Get a lab analysis of what is in the soil and at what concentration; fungi suit petroleum and PAHs, metals much less.
- Involve your state environmental agency early, since it decides what counts as clean.
- Leave an untreated control plot so you can tell whether the fungi made a difference.
- Plan disposal. Never eat mushrooms from a polluted site.
- Expect a season or more.
Local growers can supply spawn and straw, tying a clean-up to building a local economy.
Quick answers
Can mushrooms clean up oil spills?
On land, fungi are able to degrade a large share of the hydrocarbons in contaminated soil under good conditions. For spills on water, research is still at the lab stage, as in the 2025 crude oil study hosted by NOAA.
Can you eat mushrooms used for mycoremediation?
No. They can contain fuel residues and concentrated heavy metals.
How long does mycoremediation take?
Lab trials take a few weeks to three months. Field projects have taken four months to more than a year, depending on weather, soil and pollutant.
Sources
- U.S. EPA: Bioremediation Field Initiative Site Profile, Escambia Wood Preserving Site (1995)
- TRID: Mycoremediation of Aged Petroleum Hydrocarbon Contaminants in Soil (WSDOT/Battelle, 1998)
- NOAA Institutional Repository: Mycoremediation of Louisiana sweet crude oil with Pleurotus ostreatus and nutrient amendments (2025)
- Pozdnyakova (2012): Involvement of the Ligninolytic System of White-Rot and Litter-Decomposing Fungi in the Degradation of PAHs
- Antón-Herrero et al. (2023): Main Factors Determining the Scale-Up Effectiveness of Mycoremediation, Journal of Fungi