Billerica Water Treatment Plant - Executive Summary

| Accident History | Chemicals | Emergency Response | Registration | Source | Executive Summary |

                                                          Section 1 
                                      Risk Management Plan Elements 
                                     Billerica Water Treatment Plan 
                                              Town of Billerica, MA 
 
1.1          Executive Summary 
The Town of Billerica Water Treatment Plant (WTP) accidental release prevention policy involves a 
consolidated approach that integrates technologies, procedures, and management practices.  All 
applicable procedures of the U.S. Environmental Protection Agency (EPA) Prevention Program are 
followed.  The WTP emergency response policy involves the preparation of response plans that are 
tailored to each facility and to the emergency response services available in the community, and 
meets the EPA Emergency Response Program requirements. 
 
The Town of Billerica WTP, located at 250 Boston Road, Billerica, Massachusetts, is required to 
provide disinfection of the treated water before its disc 
harge to the water distribution system.  The 
Town presently utilizes chlorine gas for disinfection to meet the minimum standards of the Safe 
Drinking Water Act.  Nine one-ton containers of pressurized liquid chlorine are located on site.  
Three one-ton containers of chlorine are located within the building of which two are manifolded to 
the chlorination system. The remaining six cylinders of chlorine are each stored in one-ton 
containers on an exterior elevated rack.   
 
The offsite consequence analysis includes consideration of two release scenarios, identified as "worst 
case release" and "alternative scenario."  EPA defines the first scenario, which states that "the owner 
or operator shall assume that the  . . .  maximum quantity in the largest vessel  . . .  is released as a 
gas over 10 minutes," due to an unspecified failure.  The alternative scenario is defined as "more 
likely to occur than the worst-case release scenario." 
 
Atmospheric dispersion modeling has to be performed to de 
termine the distance traveled by the 
chlorine released before its concentration decreases to the "toxic endpoint" selected by EPA of 3 
ppm (chlorine), which is the Emergency Response Planning Guideline Level 2 (ERPG-2).  The 
American Industrial Hygiene Association (AIHA) defines this as the "maximum airborne 
concentration below which it is believed that nearly all individuals could be exposed for up to one 
hour without experiencing or developing irreversible or other serious health effects or symptoms 
which could impair an individual's ability to take protective action."  The residential population 
within a circle with a radius corresponding to the toxic endpoint distance has to be defined, "to 
estimate the population potentially affected." 
 
The worst-case release scenario involves a failure of a one-ton storage tank containing either 2,000 
pounds of chlorine.  The offsite consequence analysis for these tanks was performed for two sets of 
conditions.  The first set of conditions was pr 
edefined by the EPA.  This analysis assumed that the 
vessel would completely release all of its contents in ten minutes.  The toxic endpoint used was the 
one-hour average ERPG-2.  The population residing within a full circle with a radius corresponding 
to the toxic endpoint distance was determined.  
 
For the worst-case modeling analysis, the EPA-mandated meteorological conditions were used.  
These correspond to Stability F, wind speed of 1.5 m/s, highest daily temperature of 77oF and an 
average humidity of 50%. 
 
From the modeling results, it was concluded that the radius which corresponded to the toxic endpoint 
distance was 3.0 miles.  Within the 3.0 miles, approximately 46,800 people would be affected by this 
EPA-specified release and the corresponding conditions. 
 
The alternative release scenario involves the release of a one-ton cylinder of chlorine.  In this case, 
however, the release is inside a building. The release is assumed to be over a ten-minute time period. 
Liquid chlorine  
released from the ruptured whip would flash immediately to a vapor.  The 
meteorological conditions used were Stability D, wind speed 3.0 m/s, average air temperature of 
50oF, and 50 percent average humidity.  Based on these conditions, the off-site impact extends 0.6 
miles.  The chlorine detector is the active mitigation measure considered.   
 
The general WTP accidental release prevention program is based on the following critical elements: 
 
~    High level of training of operators 
 
~    Preventive maintenance program 
 
~    Use of state-of-the-art process and safety equipment 
 
~    Use of accurate and effective operating procedures, written with the participation of the 
    operators 
 
~    Performance of a hazard review of equipment and procedures 
 
~    Implementation of an auditing and inspection program 
 
Chemical-specific preventions steps include availability of self-contained breathing apparatus 
(SCBA), awareness of the hazardous and toxic properties of chlorine, and presence of c 
hlorine 
detectors. 
 
No accidental releases of chlorine have occurred at this facility in the past five years. 
 
The facility has an emergency response program, which has been coordinated with the Billerica Fire 
Department.
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