Munster Wastewater Treatment Plant - Executive Summary

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LDEQ Facility ID Number: 27960                  27960 LDEQ FACILITY ID NUMBER 
 
                    RISK MANAGEMENT PLAN FOR 
 
              MUNSTER WASTEWATER TREATMENT PLANT  
 
                       ST. BERNARD PARISH 
 
                       EXECUTIVE SUMMARY 
 
 
INTRODUCTION 
 
    In 1990, the United States Congress amended the Clean Air Act to address Chemical 
Accident Prevention by requiring the USEPA to develop chemical accident prevention/community 
right-to-know regulations referred to as the Risk Management Program Rule. 
    The Rule requires covered facilities, whether they be Public, Commercial, or Industrial 
entities, to create and implement a risk management/accident prevention program and to submit a 
structured Risk Management Plan (RMP) to the USEPA by not later than June 21, 1999.  A covered 
facility is one that stores any of a long list of dangerous chemicals (e.g., chemicals that are either 
toxic, flammable, or explosive), in quantities greater than the threshold leve 
ls listed in the Rule.  
Listed toxic chemicals and their respective threshold quantities can be found in the Federal 
Regulations at 40 CFR 68. 
    The stationary (potential) source that is addressed herein is the Munster Wastewater  
Treatment Plant.  The Plant's location is identified as follows: 
 
                                  1) Street Address:       3300 Munster Blvd. 
                        Meraux, LA 70075 
                                       2) Geographical Location:     29o56'47" North Latitude 
                        89o55'39" West Longitude 
 
 
    Chlorine gas, an air toxic chemical, is listed.  Chlorine is used by most water treatment and 
wastewater treatment plants as a disinfectant.  The threshold quantity listed for chlorine is 2,500 
pounds.  The Munster Wastewater Treatment Plant stores chlorine gas in quantities that exceed the  
threshold quantity and, as a result, is a covered facility.  Accordingly, St. Bernard Parish has 
conducted a Program 2 Hazard Review, 
a Compliance Audit, and developed this RMP for the 
wastewater treatment plant.  The Parish also is preparing written Safety, O&M, and Emergency 
Response Plans for the safe handling of the toxic gas, as required by the USEPA.   
    It is pertinent to note, however, that the Munster Wastewater Treatment Plant has been in 
continuous operation for more than 31 years.  During that long operational history, there has never 
been a release of chlorine gas of such a magnitude so as to cause injury to people, pets or property 
surrounding the wastewater treatment plant.   
    Pure chlorine gas (an air toxic), used to disinfect the Parish's treated wastewater supply, is 
received and stored at the above location in the form of a gas that is liquified under pressure.  The 
liquified chlorine gas is supplied in steel pressure cylinders that contain one ton (2000 lbs) of 
chlorine when received.  Typical inventory of chlorine at the Munster Wastewater Treatment Plant 
is six ton cylinders.   
OFF-SITE 
CONSEQUENCE ANALYSIS 
"Worst-Case" Scenario  
    The USEPA regulations require an assessment of risk and emergency response planning for 
accidental release of any of the listed air toxics under two (or more) different scenarios.  That is, the 
regulations call for analysis/planning for a "worst-case" scenario based on rigid scenario conditions 
for any air toxic.  These "worst-case" scenario - required conditions are identified as follows: 
 
                                                      Release Duration                   10 minutes 
                                                           Quantity of Air Toxic Released          2000 lbs 
                                                      Release Rate                       200 lbs/min 
                                                                Endpoint Toxic Concentration (safe level)    0.0087 mg/l 
                                                 Windspeed                     1.5 M/sec (3.36 mph) 
 
                                           Meteorological Stability Conditions          "F" 
                                                           Ambient Relative Humidity               50 % (rare in New Orleans area) 
                   Ambient Air & Chemical's Temperature 
                                                      (before release)                   77o (OK for air, not for chemical 
                                            which drops temperature as released) 
 
 
 
    Under the USEPA's regulations the above requirements must be plugged into any offsite 
consequence analysis (OCA) modeling, regardless if any of the factors are unrealistic or very 
unlikely to occur.  The resulting risk area for this "worst-case" scenario was determined from the 
USEPA's Risk Management Program Guidance for Wastewater Treatment Plants for the Munster 
Wastewater Treatment Plant.  For an urban setting, such as is the condition at the Munster 
Wastewater Treatment Plant, the distance to t 
he endpoint (or safe exposure distance) is listed in 
Exhibit 4-12 in the Guidance document as a 1.3 miles radius around the wastewater treatment plant. 
    Additionally, the USEPA regulations provide for consideration of passive mitigation in 
"worst-case" assessments, i.e., enclosure of air toxic containers/feed systems within a building is 
considered a valid, passive mitigation condition.  Passive mitigation presence provides for a toxic 
gas release area reduction of 45 percent (i.e., by multiplying the model "worst-case" radius by a 
factor of 0.55).  However, the Munster Wastewater Treatment Plant has no passive mitigation 
present.  Thus, the USEPA's model endpoint for chlorine remains 1.3 miles for the Munster 
Wastewater Treatment Plant in the "worst-case" scenario. 
 
Alternative Scenario 
    The regulations also permit planners to provide one or more realistic, alternative scenarios 
involving accidental release of air toxics.  The alternative scenario considered for the Munster 
Wa 
stewater Treatment Plant was based on a tubing failure, a bad connection or valve failure 
resulting in the release of chlorine gas through a 5/16 inch-diameter whole or opening in a ton 
cylinder.  
    This scenario was modeled by the USEPA study, (see Exhibit 4-15 in the Guidance 
document) and produced the following information.  The release described above would last for 60 
minutes with an average maximum gas flow rate of 15 lbs/min.  Again, for an urban setting, the 
release impact area, i.e., the distance from the source out to the endpoint concentration for chlorine 
(0.0087 mg/l or 3 ppm) was found to be 0.1 miles. 
    Further, while only passive mitigation can be considered for the "worst-case" scenario, the 
regulations permit inclusion of active mitigation factor(s) for the alternative scenario modeling that 
can further reduce the estimated toxic gas spread area (i.e., distance to endpoint).  A few examples 
of active mitigation are air scrubbers, emergency shut-down systems, and 
sprinkler systems.  
However, the Munster Wastewater Treatment Plant employs no form of active mitigation.  Thus, the 
USEPA's model endpoint for chlorine remains 0.1 miles for the Munster Wastewater Treatment 
Plant in the "alternative" scenario. 
    The Parish has developed a toxic gas release Emergency Response Plan (ERP) that is 
applicable to both the Parish's Water and Wastewater Treatment Plants.  The plan has been 
coordinated with the Parish's Fire and Police Departments. 
    During the operational history of the plant and certainly for the past 5 years, there have been 
no toxic gas releases from the plant.
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