Substance derived from tire debris is toxic to two trout species, not just coho salmon

Rubber tires are fortified with protectants, such as N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine or simply 6PPD, so they can be safely driven for a long time. However, as the treads wear down and pieces flake off over time, small rubber particles scatter across roads. There, they react with oxidants such as ozone in the air, converting 6PPD to 6PPD-quinone, which washes into waterways along with the source tire particles in stormwater runoff. Previous studies reported that exposure to small amounts of 6PPD-quinone is toxic to coho salmon -- a popular fish among recreational fishers and an environmentally important species -- and likely caused the phenomenon in urban streams called urban runoff mortality syndrome. Conversely, another study indicated that zebrafish and Japanese medaka can withstand even very high amounts of 6PPD-quinone. So, Markus Brinkmann, Markus Hecker, Steve Wiseman and colleagues wanted to see whether this contaminant poses a risk to a broader range of commercially, culturally and ecologically important fish species.

The researchers exposed juvenile brook trout, rainbow trout, Arctic char and white sturgeon to varying levels of 6PPD-quinone. They found that even small concentrations, such as those regularly occurring in surface waters after stormwater runoff events, were fatal to brook and rainbow trout. For both trout species, the researchers observed an increased blood glucose level after 6PPD-quinone exposure, suggesting it affected the fish's energy metabolism pathways. However, none of the Arctic char and white sturgeon died after four days of exposure to a high level of the contaminant that was similar to the maximum amount previously observed in stormwater runoff. The results indicate mortality from exposure to 6PPD-quinone varies among fish species, but for animals that don't die, possible non-lethal effects could be occurring and need further examination, the team says.

This project was supported partially by a financial contribution from Fisheries and Oceans Canada. The authors acknowledge additional funding from the Discovery Grants program of the Natural Sciences and Engineering Research Council of Canada (NSERC), Western Economic Diversification Canada (WED), the Canadian Foundation for Innovation, the Banting Postdoctoral Fellowship program of NSERC, the Canada First Research Excellence Funds (CFREF) and the Canada Research Chairs Program.