Evanston Water Utility - Executive Summary

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EXECUTIVE SUMMARY 
 
 
Stationary Source and Regulated Substances  
 
Chlorine is the major hazard and regulated substance in Evanston Water Utility.   An inadvertent release of chlorine to the atmosphere may reach public receptors surrounding the facility.  Chlorine is heavier than air and seeks low areas.  It appears as a greenish-yellow gas and impacts public health when inhaled above the toxic end point as defined within 40 CFR 68.22.  
 
Evanston Water Utility uses chlorine to treat raw water for public consumption.  The chlorine feed system is redundant and feeds chlorine from alternate cylinders through alternate piping in the event of a leak.  
 
The stationary source is the treatment process.  Liquid chlorine in eight one-ton cylinders naturally vaporizes into the piping system.  The cylinders are mounted on load cells and are connected to a 1 inch steel pipe header with pigtails (3/8" tubing).  In response to the load cell when the tanks are nearly empty, an automatic valve switches f 
low from four cylinders at a time.  The four cylinder valves are partially open, and at vapor pressure, deliver chlorine gas to the header and vacuum regulator. Chlorine flows at vacuum pressure from the regulator, into the chlorinator that meters and controls the flow, and then flows into the ejectors.  The ejectors provide motive vacuum power for the chlorinating system and mix the chlorine gas with water to form a solution.  
 
At any time, a total of 16 one-ton cylinders and four 150-pound cylinders may be stored in the chlorine building. Maximum inventory is 32,600 pounds and exceeds EPA's threshold quantity of 2500 pounds. 
 
Hazard Assessment 
 
Failing to control the hazard and exceeding the toxic end point, EPA requires that the facility provide an offsite hazard assessment by evaluating two release scenarios ( Worse Case and Alternate Case ) to determine the toxic end point.   
 
Toxic end point is based on ERPG-2 concentrations developed by the American Industrial Hygiene Associati 
on (AIHA).  The ERPG-2 is a maximum air borne concentration in which is believed that almost all individuals could be exposed for up to one hour without developing serious irreversible health effects or other symptoms that could impair an individuals ability to take protective action.  The AIHA has identified chlorine's toxic end point as three parts per million ( 3 PPM ) or .0087 mg/l. 
 
Worse Case is liquid chlorine released to the atmosphere for 10 minutes from a one ton storage cylinder that is caused by catastrophic failure due to corrosion, impact, or construction defects. The worse case scenario is rupture of a one ton cylinder when falling from a truck or hoist while unloading outside the building or inside the building with unloading door open.   The toxic end point is based on ALOHA dispersion modeling developed by the National Safety Council and summarized in Table A5-1 of AWWA's Compliance and Model RMP for Water Treatment Plants.  The toxic end point of the worse case scena 
rio is 2.6 miles radius from the chlorine building.  Modeling does not include the effects of fires, chemical reactions, site topography, and other factors.   
 
Alternate Case is more likely to occur than the Worse Case.  This scenario could be the failure of chlorine gas tubing (pigtail) connected from the storage cylinder to the 1" supply header when multiple cylinders are connected to the header.  Anticipated operator's response time to attempt to stop the leak is approximately 10 minutes.   Toxic level alarms will warn the operators who will respond by putting on self - contained breathing apparatus, turning on the ventilation system before entering the building, and closing all isolation valves from the cylinder to the header to stop the flow. The release inside the building is not considered a mitigating factor because of the availability of the ventilation system that replaces the air volume in the building in one minute.  Based on the above tables, the toxic end point of this al 
ternate case is 0.63 miles radius from the chlorine building. 
 
The Topographic Map in Appendix shows the radius of exposure for the toxic endpoints. 
 
Prevention of Chlorine Release 
 
The process is designed in compliance with recognized and generally accepted good engineering practices of the Chlorine Institute and other applicable codes and standards of water treatment facilities.  It is our policy to adhere to all applicable Federal and state rules and regulations.  Safety depends upon the manner in which we handle chlorine, safety devices inherent in the design of this facility, safe handling and operating procedures that we use, and training of our personnel.  Program 2 Prevention Program as described in 40 CFR Part 68 is followed to accomplish these goals and will minimize the potential for an unplanned release of chlorine to the environment.   
 
Five Year Accident History 
 
In the past five years, no accidental releases have occurred. 
 
 
 
 
 
 
Emergency Response Program 
 
Despite the Pr 
evention Program, incidents may still occur. An Emergency Response Program is required to minimize the duration and effects of an accidental release, thereby protecting the public health and the environment.  
 
Except for minor releases, this facility relies on community emergency responders (Evanston Fire Department) and works closely with them to ensure that they are suitably trained and drilled in emergency response for chlorine releases.  Notification and evacuation procedures meet EPA's requirements (OSHA Standards) and Illinois Chemical Safety Act requirements. The Emergency Contingency Plan is included in Appendix E.  
 
Planned Changes for Improved Safety 
 
This Water Treatment facility was constructed in 1994.  It complies with latest codes and standards, and the Chlorine Institute guidelines.  We continue to participate in the Chlorine Institute programs and to improve our operations.
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