Pascoag: Lessons Learned


A Confluence of Factors

Creating the Situation

In piecing together the events that took place in Pascoag in the fall of 2001, it quickly becomes apparent that numerous factors combined to create a situation that most officials interviewed described as unprecedented. Engineers at DEM, HEALTH and the PUD agreed that the nature of the Pascoag contamination was exceptional not only in the relatively large distance the contaminant traveled from the source of the gasoline release, but also in the speed with which contaminant levels rose in the water supply. Several factors contributed to the severity of the contamination:

  • The chemical nature of MTBE. Methyl tertiary-butyl ether, added to gasoline in significant quantities beginning in 1992 following amendments to the US Clean Air Act of 1990, is highly water-soluble. When a gasoline release occurs, MTBE often moves significantly farther and faster than the other chemical constituents of gasoline.
  • Topography and geology. Engineers at the PUD and DEM noted the downhill gradient from the Mobil station to the wells as a contributing factor in the contamination. Some also suggested that fractures in the bedrock that predominates in the region of the wells may have provided a conduit for the contaminant to move rapidly. The high-yield Pascoag wells, pulling upwards of 500 gallons of water per minute, may also have contributed by drawing the contaminant toward the groundwater aquifer.
  • Lack of redundancy of wellsource. Although the Pascoag Utility District had installed a second well in February of 2001, this well was housed in the same building as the first well and located just ten feet away. According to PUD General Manager Ted Garille, the district believed that the wells, though very close together, drew from separate aquifers. Nonetheless, both wells were found in September to be pumping MTBE-contaminated water.
  • Underground Storage Tank facility within the Wellhead Protection Area (WPA). The Wellhead Protection Area Program, required by the US EPA and administered in Rhode Island by the Department of Environmental Management, prohibits the installation of new underground storage tank facilities within a designated area surrounding a wellsource. This area is determined by a formula that incorporates well capacity, local geology and other factors. The Main Street Mobil Station pre-existed the WPA rules and lies within the Pascaog wellhead protection area, approximately 1700 feet from the wells.

What about the rest of Rhode Island?

Although the Pascoag contamination was unparalleled in the experience of DEM and HEALTH officials, this should not be taken to imply that the contamination faced by Pascoag was an improbable event. Many of the same factors that devastated Pascoag's public water supply exist in dozens of other towns and villages across Rhode Island. These include, but are not limited to:

  • A large number of small public water supplies with limited financial resources
  • Non-compliant underground storage tank owners
  • Underground storage tanks in close proximity to water sources

According to statistics from HEALTH, as of July 2002 there were 389,858 Rhode Island residents served by water systems with known underground storage tanks located within half a mile of the well. Most of the state and local officials interviewed believe there to be a high probability that another similar contamination event will occur in Rhode Island; some described such an event as inevitable. According to Janis Loiselle, senior policy advisor to Governor Almond, the next contamination in Rhode Island is not a question of "if" but of "when".

home • background • residents • officials • issues • this project • site map