Fall Creek Water Treatment Plant - Executive Summary

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Introduction 
 
USEPA's RMP rule (40 CFR 68), published in the Federal Register on June 20, 1996, was developed to assist facilities in preventing accidental releases of highly toxic or flammable chemicals.  The RMP rule applies to an owner or operator of a stationary source that has more than a threshold quantity of a regulated substance in a process, as determined under '68.115. 
 
The USEPA has established three tiers of requirements to reduce the level of effort for facilities with a lower risk of off-site impacts.  These tiers are known as Programs 1, 2, and 3.  Program 1 applies to any process that has not had an accidental release with prescribed offsite consequences for five years and has no public receptors impacted by a worst-case release.  Program 3 applies to processes in specified industries, and to all processes subject to the OSHA Process Safety Management (PSM) standard, unless the process is eligible for Program 1.  Program 2 applies to processes not covered by Programs 1  
or 3. 
 
The Indianapolis Water Company's Fall Creek WTP utilizes more than the threshold quantity of chlorine (2,500 pounds) in their process.  Therefore, this facility is required to submit a Risk Management Plan (RMP) as defined in '68.150 by June 21, 1999 (three years after publication of the final rule). Since public employees are covered under the state-delegated OSHA program, the Fall Creek WTP is subject to the OSHA PSM standard and is therefore subject to Program 3 requirements.   
 
USEPA's RMP rule requires that covered facilities prepare an executive summary.  The following pages represent the executive summary, summarizing the items required as described in 68.155 (a) through (g). 
 
'68.155(a) Accidental Release and Emergency Response Policies 
 
The Indianapolis Water Company has documented emergency response procedures contained in their Emergency Response Plan.  The Emergency Response Plan has been endorsed by the officials at the highest level of the Indianapolis Water Compan 
y.  The Indianapolis Water Company maintains a staff specifically trained to handle chlorine safely and respond to minor releases.  In the case of a potentially major release, the Indianapolis Water Company will rely on the hazardous materials responders from the Indianapolis Fire Department.  The Fall Creek WTP operators coordinate with the local fire department once a year to perform an inspection of the chlorine facilities. An operator is located at the facility 24 hours a day, ready to respond to emergencies.  All personnel involved in handling chlorine are trained on chlorine safety and accident prevention. 
 
'68.155(b) Stationary Source and Substance Handled 
 
The stationary source subject to 40 CFR Part 68 is the Indianapolis Water Company's Fall Creek WTP.  The Fall Creek WTP is a 32-mgd facility treating surface water to drinking water standards.  The facility uses one 55-ton primary rail car and one 55-ton standby rail car for storage of chlorine.  The facility also has on site 
two to four one-ton chlorine containers for backup purposes stored in a room adjacent to the chlorine room.  Liquid chlorine from the rail cars is piped to evaporators and chlorinators in the chlorine room through 1 inch piping.  The facility typically has one 55-ton rail car connected to the evaporators/chlorinators, with the standby car also connected to the chlorinators for backup purposes.  Several one-ton containers may also be connected to process piping for backup purposes. 
 
The Fall Creek WTP is equipped with many safety devices to prevent a release and decrease response time in the unlikely event of a chlorine leak.  Chlorine leak detectors are located near the rail cars and in the chlorine container storage room.  Audible alarms automatically sound inside the building when chlorine levels reach one part per million (ppm), allowing safety personnel time to respond to emergencies.  The chlorine rail car liquid lines are equipped with excess flow check valves which close when t 
he chlorine flow from the rail car exceeds a certain level (15,000 pounds per hour).  Also, there are low pressure alarms for the chlorine feed.  An operator is located at the facility 24 hours a day, ready to respond to emergencies. 
 
'68.155(c) Offsite Consequence Analysis 
 
The worst-case release scenario was determined in accordance with the requirements provided in 40 CFR 68.22 and 40 CFR 68.25(b,c).  For the Fall Creek WTP, the worst-case scenario is a release from one of the 55-ton rail cars (greatest amount held in a single vessel) of chlorine. It is assumed that the container ruptures and its contents escape to the ground in 10 minutes.  The worst-case scenario requires a ground level release height.  It was assumed that the release occured outside, and no mitigation measures were incorporated into the evaluation.   The reference tables in the USEPA RMP Guidance for Wastewater Treatment Plants were used to determine the toxic endpoint for the worst case scenario.  The toxic endp 
oint distance indicated that schools, hospitals, prisons, parks, and churches could be impacted by a catastrophic release. 
 
The Fall Creek WTP is also required to complete at least one alternative release scenario.  The alternative release scenarios considered were completed in accordance with the guidelines provided in 40 CFR 68.22 and 40 CFR 68.28.  The alternative release scenario selected (the one with most signifcant off-site consequences) was that of a 1/2 inch diameter  hole in the piping from the railcar.  This release could result from vehicular contact with the piping, corrosion of the piping, or improper connection of piping.  As with the worst case scenario, the reference tables in USEPA's RMP Guidance for Wastewater Treatment Plants was used to determine the toxic endpoint, and the resulting toxic endpoint predicted potential off-site impacts.  
 
'68.155(d) Accidental Release Prevention Program 
 
The Fall Creek WTP has a documented Prevention Program for the chlorine systems 
that documents release prevention measures.  These prevention measures include elements such as employee participation, process safety information, process hazard analysis, operating procedures, training, contractors, pre-startup review, mechanical integrity, hot work permits, management of change, incident investigation, and compliance audits.   
 
The Fall Creek WTP is equipped with many safety devices to prevent a chlorine release and decrease response time in the unlikely event of a chlorine leak.  Chlorine leak detectors are located near the rail cars and in the chlorine container storage room.  Audible alarms automatically sound inside the building when a chlorine release occurs.  The chlorine rail car is equipped with excess flow check valves which close when the chlorine flow from the rail car exceeds a certain level.  Also, Fall Creek employees involved in chlorine operations are trained in specific procedures regarding handling and storage of chlorine at the facility. 
 
'68.155 
(e) Five-Year Accident History 
 
The Indianapolis Water Company's Fall Creek facility has had no accidental releases of chlorine in the last five years that have resulted in on-site injuries, off-site injuries or other impacts. Available records indicate that there has been no accidental releases of chlorine from the Fall Creek WTP that have resulted in on-site deaths, off-site injuries, or other impacts since the facility began using chlorine in approximately 1945. 
 
'68.155(f) Emergency Response Program 
 
The Fall Creek WTP operators coordinate with the local fire department once a year to perform an inspection of the chlorine facilities. An operator is located at the facility 24 hours a day, ready to respond to emergencies.  All personnel involved in handling chlorine are trained on chlorine safety and accident prevention. 
 
'68.155(g) Safety Improvements 
 
Recommendations for safety improvements were identified in the Process Hazard Analysis (PHA) which was completed per OSHA 29 CFR 191 
0.119(e) in November of 1995 by Battelle.  The Indianapolis Water Company has elected to voluntarily convert from the use of gaseous chlorine to sodium hypochlorite.  Sodium hypochlorite poses less threats to the surrounding community that gaseous chlorine and is not covered the 112(r) Risk Management Program Rule.  It is anticipated that the conversion to sodium hypochlorite at the Fall Creek WTP will be complete by May of 2001.
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