Final—July 2, 2015

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Significant New Alternatives Policy Program 

Refrigeration and Air Conditioning Sector

Risk Screen on Substitutes in Retail Food Refrigeration, Vending Machines, and 

Commercial Ice Machines

Substitute: R-513A (Opteon® XP10)

This risk screen does not contain Clean Air Act (CAA) Confidential Business Information 

(CBI) and, therefore, may be disclosed to the public.

1. INTRODUCTION

Ozone-depleting substances (ODS) are being phased out of production in response to a series of diplomatic 

and legislative efforts that have taken place over the past two decades, including the Montreal Protocol and 

the Clean Air Act Amendments of 1990 (CAAA). The U.S. Environmental Protection Agency (EPA), as 

authorized by Section 612 of the CAAA, administers the Significant New Alternatives Policy (SNAP) 

Program, which identifies acceptable and unacceptable substitutes for ODS in specific end-uses based on 

assessment of their health and environmental impacts. 

EPA’s decision on the acceptability of a substitute is based on the findings of a screening assessment of 

potential human health and environmental risks posed by the substitute in specific applications. EPA has 

already screened a large number of substitutes in many end-use applications within all of the major ODSusing sectors including: refrigeration and air conditioning, solvent cleaning, foam blowing, aerosols, fire 

suppression, adhesives, coatings and inks, and sterilization. The results of these risk screens are presented 

in a series of Background Documents that are available in EPA's docket.

The purpose of this risk screen is to supplement EPA’s Background Document on the refrigeration and air 

conditioning sector (EPA 1994) (hereinafter referred to as the Background Document). This risk screen 

evaluates the potential use of R-513A (also known as Opteon® XP10) as a substitute in the retail food 

refrigeration (specifically, convenience stores, direct racks, indirect racks, remote condensing units, and 

stand-alone display cases), vending machines, and commercial ice machines end-uses. Table 1 presents the 

composition of the proposed substitute. 

Table 1. Composition of R-513A and Potential Impurities

Constituent Chemical Formula CAS Number Concentration

(Weight Percent)

2,3,3,3-Tetrafluoropropene 

(HFO-1234yf) CH2CFCF3 754-12-1 ≤56%

1,1,1,2-Tetrafluoroethane

(HFC-134a) CF3CH2F 811-97-2 ≤44%

Potential Impurities

Section 2 summarizes the results of the risk screen for the proposed substitute blend listed in Table 1. The 

remainder of the risk screen is organized into the following sections:

• Section 3: Atmospheric Assessment

• Section 4: Volatile Organic Compound Assessment 

• Section 5: Discussion of End-Use Scenario Modeled 

• Section 6: Potential Health Effects 

• Section 7: Flammability Assessment

• Section 8: Asphyxiation Assessment 
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• Section 9: End-Use Exposure Assessment

• Section 10: Occupational Exposure Assessment 

• Section 11: General Population Exposure Assessment

• Section 12: References

2. SUMMARY OF RESULTS

R-513A is recommended for SNAP approval for the retail food refrigeration, vending machines, and 

commercial ice machine end-uses. EPA's risk screen indicates that the use of the proposed substitute will 

be less harmful to the atmosphere than the continued use of ODS and other commonly used refrigerants, as

it is less harmful to the ozone layer, has lower climate impact, and a shorter atmospheric lifetime. The

components of R-513A are not subject to volatile organic compound (VOC) regulations under the CAA 

(40 CFR 51.100(s)), so environmental impact from the release of these substances is not a concern. In 

addition, because R-513A is considered to be nonflammable, the proposed substitute is not expected to 

present a flammability concern. It is expected that the manufacturer’s safety data sheet (SDS) for R-513A

and good manufacturing practices will be adhered to during handling or use of R-513A.

Additionally, it is expected that the appropriate safety and personal protective equipment (PPE) (e.g., 

protective gloves, tightly sealed goggles, protective work clothing, and suitable respiratory protection in 

case of leakage or insufficient ventilation) consistent with Occupational Safety and Health Administration 

(OSHA) guidelines will be used during manufacture, installation and servicing, and disposal of retail food 

refrigeration systems, vending machines, and commercial ice machines using R-513A. Because retail food 

refrigeration systems, vending machines, and commercial ice machines are to be installed in locations with 

adequate space and/or ventilation in accordance with EPA recommendations and the equipment 

maintenance manuals for R-513A in each end-use, significant toxicity risk to consumers is also unlikely. 

Additional safeguards, including specified refrigerant concentration limits (RCL) of R-513A components, 

are also provided by adherence to industry standards including American Society of Heating, Refrigerating 

and Air-Conditioning Engineers (ASHRAE) Standards 15,1 34,2 and 62.3

3. ATMOSPHERIC ASSESSMENT

This section presents an assessment of the potential risks to atmospheric integrity posed by the use of R513A in retail food refrigeration, vending machines, and commercial ice machines. The ozone depletion 

potential (ODP), global warming potential (GWP), and atmospheric lifetime (ALT) of the proposed 

substitute are presented in Table 2.

The proposed substitute is substantially less harmful to the ozone layer, has lower climate impact, and a 

shorter ALT when compared to CFC-12, R-502, and HCFC-22. In addition, R-513A also has lower 

climate impact and a shorter ALT than those predicted for other substitutes examined in the Background 

Document as well as commonly utilized refrigerants in commercial refrigeration, HFC-134a, R-404A, R507A, and R-407C. Thus, EPA believes that the use of R-513A would result in substantially less harm to 

the climate and ozone layer than the continued use of ODS and other commonly used refrigerant. 

 1 Safety Standard for Refrigeration Systems ASHRAE Standard 15 establishes safeguards for life, limb, health, and property and 

prescribes safety requirements.

2 Designation and Safety Classification of Refrigerants ASHRAE Standard 34 establishes a uniform system for assigning reference

numbers, safety classifications, and refrigerant concentration limits to refrigerants. Safety classifications based on toxicity and 

flammability data are included.

3 Ventilation for Acceptable Indoor Air Quality ASHRAE Standard 62 establishes minimum ventilation rates and other measures

intended to provide indoor air quality that is acceptable to human occupants and that minimizes adverse health effects.
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Table 2. Atmospheric Impacts of R-513A Components Compared to Other Refrigerants Used in 

Commercial Refrigeration

Refrigerant Ozone Depleting Potential

(ODP)a

Global Warming Potential

(GWP)b

Atmospheric Lifetime in 

Years (ALT) 

R-513A 0 631 NAc

Individual Components

HFC-134a 0 1,430 14b

HFO-1234yf 0 4d 11 daysd

CFC-12 0.82 10,900 100b

R-502e 0.2 4,650 NAf

HCFC-22 0.13 1,810 12a

R-404Ag 0 3,922 NAh

R-507Ai 0 3,985 NAj

R-407Ck 0 1,774 NAl

a WMO 2010 Scientific Assessment Report (2011)

b IPCC 4th Assessment Report (Forster et al. 2007) c Atmospheric lifetimes are not given for blends, because the components separate in the atmosphere. The ALT for the individual components 

are listed in the table. 

d Papadimitriou et al. (2007) e R-502 is a blend consisting of HCFC-22 (49%) and CFC-115 (51%). f Atmospheric lifetimes are not given for blends, because the components separate in the atmosphere. The ALT for HCFC-22 is 12 years and the 

ALT for CFC-115 is 1,700 years (IPCC 4th Assessment Report [Forster et al. 2007]).

g R-404A is a blend consisting of HFC-143a (52%), HFC-125 (44%) and HFC-134a (4%). h Atmospheric lifetimes are not given for blends, because the components separate in the atmosphere. The ALT for HFC-143a is 52 years, the 

ALT for HFC-125 is 29 years, and the ALT for HFC-134a is 14 years (IPCC 4th Assessment Report [Forster et al. 2007]). i R-507A is a blend consisting of HFC-125 (50%) and HFC-143a (50%).

j Atmospheric lifetimes are not given for blends, because the components separate in the atmosphere. The ALT for HFC-125 is 29 years and 

ALT for HFC-143a is 52 years (IPCC 4th Assessment Report [Forster et al. 2007]). k R-407C is a blend consisting of HFC-32 (29%), HFC-125 (25%) and HFC-134a (52%). l Atmospheric lifetimes are not given for blends, because the components separate in the atmosphere. The ALT for HFC-32 is 4.9 years, the ALT 

for HFC-125 is 29 years, and the ALT for HFC-134a is 14 years (IPCC 4th Assessment Report [Forster et al. 2007]).

4. VOLATILE ORGANIC COMPOUND ASSESSMENT

The components of R-513A, HFC-134a and HFO-1234yf, are exempt from the definition of VOCs under 

CAA regulations (40 CFR 51.100(s)). Therefore, VOC impacts from the release of R-513A are not a 

concern.

5. DISCUSSION OF END-USE SCENARIOS MODELED

R-513A has been proposed for use in retail food refrigeration, vending machines, and commercial ice 

machines. As provided by the submitter, retail food refrigeration equipment will have charge sizes ranging 

from 0.3 kg for a typical stand-alone, self-contained display case to a maximum charge size of 800 kg for a 

direct rack system. Vending machines are expected to have a typical charge size of 0.3 kg and a maximum 

charge size of 0.6 kg. Commercial ice machines are anticipated to have a typical charge size of 3 kg and a 

maximum charge size of 30 kg. The intended maximum and typical charge sizes for R-513A in all of the 

proposed applications are listed in Table 3. 
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Table 3. Typical and Maximum Charge Sizes for Various R-513A End-Uses and Applications

End-Use Application Typical Charge Size 

(kg)

Maximum Charge Size 

(kg)

Retail food 

refrigeration

Direct rack 400 800

Condensing unit 4 25

Stand-alone, self-contained display case 0.3 1.5

Vending machines Vending machines 0.3 0.6

Commercial ice 

machines Commercial ice machines 3 30

Bolded applications and charge sizes represent those modeled in this risk screen. Condensing units were not modeled in this risk screen 

because this application is assumed to fall within the range of the charge sizes and room sizes identified for direct rack systems and stand-alone 

units. 

To represent a reasonable worst-case scenario for the retail food refrigeration end-use, it is assumed that a 

catastrophic leak of refrigerant occurs at the end-use for a direct rack system (i.e., grocery supermarket)

and a stand-alone beverage cooler (i.e., convenience store). The analysis considers the maximum charge 

size provided by the submitter for each scenario. Because retail refrigeration equipment can be installed in 

a wide range of locations with varying room volumes, the analysis in this risk screen conservatively 

assumes that the direct rack system is located in a grocery supermarket and the beverage cooler is located 

in a convenience store.

The grocery supermarket is assumed to have an effective volume of 24,200 m3 (855,000 ft3

) with an 

effective floor area of 4,400 m2 (i.e., excluding the space filled by the rack system, shelving, display cases, 

etc.) and a height of 5.5 meters (Armines 2008). Based on minimum convenience store sizes located in 

California (Armines 2008), the convenience store is assumed to have an effective volume of 244 m3 (8,620 

ft3

) with an effective floor area of 100 m2 (i.e., excluding the space filled by the beverage cooler, shelving, 

display cases, etc.) and a height of 2.44 meters. 

For the vending machine end-use, it is assumed that the vending machine is located in the minimum room 

size, an enclosed alcove of a commercial building that can be isolated by a door. The alcove is assumed to 

have an effective floor area of 6.15 m2 (i.e., excluding the space filled by the vending machine, furniture, 

boxes, etc.) and a height of 2.44 meters, equivalent to a volume of 15 m3 (530 ft3

). 

For the commercial ice machine end-use, it is assumed that the ice machine is located in a seafood 

processing facility with an assumed effective volume of 5,700 m3 (201,300 ft3

), with an effective floor area 

of 1,040 m2 (i.e., excluding the space filled by the ice machine, shelving, processing equipment, etc.) and a 

height of 5.5 meters.

Under these worst-case scenarios, the full charge of each unit is assumed to be emitted into the grocery 

supermarket, convenience store, enclosed alcove, or seafood processing facility with 8, 1, 0.5, and 15 air 

changes per hour (ACH), 4,5 respectively over the course of two time durations: 1) one minute, which 

represents a catastrophic release of refrigerant due to a puncture or other major damage to the refrigeration 

system, and 2) fifteen minutes, which represents the accidental release of refrigerant due to a noncatastrophic leak in the system (e.g., valve failure). The one-minute time duration is most appropriate for 

flammable refrigerants and presents a less relevant scenario for R-513A, which is nonflammable. 

Therefore, while both scenarios are evaluated in this risk screen for consistency purposes, the scenario 

which analyzes a release of refrigerant over a 15-minute time duration more accurately represents a 

 4 The air exchange rates for a grocery supermarket, convenience store, and enclosed alcove are derived from the requirements in 

ANSI/ASHRAE Standard 62.1-2007, Table 6.1 (ANSI/ASHRAE 2007). Ventilation requirements (presented as cubic feet per 

minute per square foot of ventilated space in the standard) were converted to air exchanges per hour using the assumed room size 

for the scenario.

5 The air exchange rates for a seafood processing facility are derived from the suggested sufficient air changes per hour in enclosed 

processing and food handling areas of between 5 and 25 air changes per hour (Lelieveld, H.L.M. 2014).
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reasonable worst-case scenario for R-513A in retail food refrigeration, vending machines, and commercial 

ice machines. 

A vertical concentration gradient is also assumed since R-513A is denser than air (the specific gravities of 

both HFC-134a and HFO-1234yf are greater than 1) and will settle in higher concentrations closer to the 

ground. In order to simulate the vertical concentration gradient, it is assumed that 95 percent of the leaked 

refrigerant mixes evenly into the bottom 0.4 meters of the room, and the rest of the refrigerant mixes 

evenly in the remaining volume (Kataoka 2000). Table 4 details the end-use modeling assumptions used 

throughout the risk screen (i.e., in Sections 8 and 9).

Table 4. End-Use Scenario Model Assumptions 

Parameter Assumptions 

Large Retail Food Small Retail Food Vending Machine Ice Machine

Refrigeration Unit Direct Rack System Stand-Alone Beverage 

Cooler Vending Machine Commercial Ice Machine

Room Grocery 

Supermarket Convenience Store Enclosed Alcove Seafood Processing Facility

Maximum Charge Size (kg) 800 1.5 0.6 30

Length of Release (minutes) 1; 15 1; 15 1; 15 1; 15

Room Size (volume - m3) 24,200a 244b 15 5,700c

Room Ventilation (air changes 

per hour) 8 1 0.5 15

Vertical Concentration Gradient Yes Yes Yes Yes a The average grocery supermarket sales area size found during a California survey (Armines 2008) – 4,400 m2 – was used for this scenario and 

a 5.5 m (18-foot) ceiling was assumed. b Specific information was not available regarding which types of stores would utilize beverage cases or commercial ice machines, so a small 

store (i.e., a convenience store) was used in the model. The minimum convenience store size found during a California survey (Armines 2008) –

100 m2 (1,076 ft2) – was used for this scenario and a 2.44-meter (8 ft) ceiling was assumed. c The average size of the seafood processing facility is assumed to be consistent with typical factory size used in occupational exposure 

modeling.

EPA recognizes that direct rack systems, beverage coolers, other retail food refrigeration units, vending 

machines, and commercial ice machines may be placed in a variety of locations, including retail stores,

manufacturing establishments, and other spaces with differing sizes and ventilation rates. When units are

installed in smaller, enclosed spaces, there is a higher risk for asphyxiation or exposure concerns. To 

address this variability in room volumes and charge sizes for installed retail food equipment, vending 

machines, and commercial ice machines, this risk screen incorporates threshold analyses in addition to the 

worst-case scenario modeling. The threshold analyses are performed in order to determine the room size 

and charge size requirements that ensure that the use of R-513A in retail food refrigeration, vending 

machines, and commercial ice machines does not present risk to end-users or servicing technicians.

6. POTENTIAL HEALTH EFFECTS

To assess potential health risks from exposure to the proposed substitute in retail food refrigeration and 

commercial ice machines, EPA identified the relevant toxicity threshold values for comparison to modeled 

exposure concentrations for different scenarios. According to ASHRAE Standard 34-2013, R-513A is 

listed under safety group A1 with a RCL of 72,000 ppm (ASHRAE 2015). ASHRAE 34 RCLs are 

intended to reduce the risks of acute toxicity, asphyxiation, and flammability hazards in normally 

occupied, enclosed spaces during refrigerant use and protect end-users from the potential dangers of a 

catastrophic leak from a refrigeration unit (ASHRAE 2010b). ASHRAE Standard 15 implements the 

aforementioned standard, requiring that “the concentration of refrigerant in an enclosed space following a 

complete discharge of a high-probability system shall not exceed the RCL” (ASHRAE 2010a). As such, 

this risk screen references the proposed RCL for R-513A in addition to the hypoxia no observed adverse 
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effect level (NOAEL) and exposure limits, as an additional, conservative limit to ensure that significant 

asphyxiation and end-use exposure risks, respectively, do not occur.

For the occupational exposure analysis, potential risks from chronic and acute worker exposure were 

evaluated by comparing exposure concentrations to available occupational exposure limits. Potential risks 

of chronic worker exposure were evaluated using workplace guidance levels (WGLs), such as Workplace 

Environmental Exposure Levels (WEELs). Risks from potential short-term consumer exposures were 

evaluated by comparing exposure concentrations to emergency guidance levels (EGLs). In the absence of 

an established short-term exposure limit (STEL), acute exposure guideline level (AEGL), or emergency 

response planning guideline (ERPG) for R-513A, potential short-term, end-use exposures were evaluated 

on a component basis (i.e., HFC-134a and HFO-1234yf). Table 5 lists the relevant toxicity limits for R513A and its components and is followed by Table 6, which provides an explanation of each toxicity limit.

EPA’s approach for identifying or developing these values is discussed in Chapter 3 of the Background 

Document. 

Table 5. Exposure Limits of R-513A Components

R-513A

Component

WGL

(Long-term Exposure)

ppm

EGL 

(Short-term Exposure)

ppm

Refrigerant Concentration 

Limit (RCL)

ppm

R-513A 653 (8-hour AEL) 1,960 (15-min STEL)a 72,000

Individual Components

HFC-134a 1,000 (8-hour WEEL) 8,000 (10-min AEGL-1)

8,000 (30-min AEGL-1) 50,000

HFO-1234yf 500 (8-hour WEEL) 1,500 (15-min STEL)b 100,000c

a Neither the American Conference of Governmental Industrial Hygienists (ACGIH) nor the American Industrial Hygiene Association (AIHA)

recommend ceiling or short term exposure limits for the blend R-513A. A STEL for R-513A of 1,960 ppm was developed by EPA based on the 

653 ppm AEL value. The STEL was estimated as three to five times the AEL, which is an established method of estimating a short-term 

exposure limit by ACGIH. [STEL] = [AEL] x 3 = 653 ppm x 3 ≈ 1,960 ppm b Neither ACGIH nor AIHA recommend ceiling or short term exposure limits for HFO-1234yf. A STEL for HFO-1234yf of 1,500 ppm was 

developed by EPA based on the 500 ppm WEEL value. The STEL was estimated as three to five times the AEL, which is an established method 

of estimating a short-term exposure limit by ACGIH. [STEL] = [AEL] x 3 = 500 ppm x 3 ≈ 1,500 ppm c Although a RCL has not been proposed for HFO-1234yf, the recommended ATEL for HFO-1234yf is 101,000 ppm (DuPont Fluoroproducts 

2014).

Table 6. Explanation of Exposure Limit-Related Terminologya

Organization Definition

OSHA Occupational Safety and Health Administration

NIOSH National Institute for Occupational Safety and Health

ACGIH American Conference of Governmental Industrial Hygienists

AIHA American Industrial Hygiene Association

OARS Occupational Alliance for Risk Science

Exposure Limit Definition Explanation

Short-Term Exposure

RCL Refrigerant Concentration 

Limit

The RCL for a refrigerant is intended to reduce the risks of acute toxicity, 

asphyxiation, and flammability hazards in normally occupied, enclosed 

spaces. The RCL for each refrigerant is the lowest of the Acute-Toxicity 

Exposure Limit (ATEL), Oxygen Deprivation Limit (ODL), and Flammable 

Concentration Limit (FCL). Determination assumes full vaporization with 

no removal by ventilation, dissolution, reaction, or decomposition and 

complete mixing of refrigerant in the space to which it is released.

ATEL Acute Toxicity Exposure Limit The ATEL is the refrigerant concentration limit intended to reduce the 

risks of acute toxicity hazards in normally occupied, enclosed spaces 

according to ASHRAE Standard 34. The ATEL includes consideration of 

mortality, cardiac sensitization, anesthetic or central nervous system 
Final—July 2, 2015

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effects and other escape impairing effects and permanent injury. The 

ATEL is similar to the Immediately Dangerous to Life or Health (IDLH)

concentrations set by NIOSH.

STEL Short-Term Exposure Limit A 15-minute time-weighted average (TWA) exposure that should not be 

exceeded during a workday, even if the 8-hour TWA is within the 

threshold limit value-time weighted average (TLV–TWA), set by ACGIH. 

AEGLb,c

Acute Exposure Guideline 

Level 1

AEGL-1 is the airborne concentration (expressed as ppm or mg/m3) of a 

substance above which it is predicted that the general population, 

including susceptible individuals, could experience notable discomfort, 

irritation, or certain asymptomatic nonsensory effects. However, the 

effects are not disabling and are transient and reversible upon cessation 

of exposure. 

Acute Exposure Guideline 

Level 2

AEGL-2 is the airborne concentration (expressed as ppm or mg/m3) of a 

substance above which it is predicted that the general population, 

including susceptible individuals, could experience irreversible or other 

serious, long-lasting adverse health effects or an impaired ability to 

escape.

Acute Exposure Guideline 

Level 3

AEGL-3 is the airborne concentration (expressed as ppm or mg/m3) of a 

substance above which it is predicted that the general population, 

including susceptible individuals, could experience life-threatening health 

effects or death.

Long-Term Exposure

PEL Permissible Exposure Limit This is an 8-hour TWA exposure limit set by OSHA. 

AEL Acceptable Exposure Limit The maximum 8-hour TWA at which a worker can be exposed regularly 

without adverse effects.

WEEL Workplace Environmental 

Exposure Level 

Developed by OARS for to protect healthy workers against acute and 

chronic health effects, this limit is based on repeated daily exposures 

over a working lifetime and averaged over an 8-hour workday. 

TLV-TWA Threshold Limit Value –TimeWeighted AverageThe TWA concentration for a conventional 8-hour workday and a 40-

hour workweek, to which it is believed that nearly all workers may be 

repeatedly exposed, day after day, for a working lifetime without adverse 

effect according to ACGIH. 

a All information in this table taken from EPA (1994) except where otherwise noted.

b EPA (2012)

c Applicable to emergency exposure periods ranging from 10 minutes to 8 hours.

According to the SDS, exposure to R-513A may be hazardous if inhalation, skin contact, or eye contact 

with the proposed substitute occurs. The most likely pathway of exposure is through inhalation. R-513A

can cause symptoms of asphyxiation when present in concentrations high enough to significantly lower 

oxygen concentrations below 19.5 percent by volume, such as headaches, ringing in ears, dizziness, 

drowsiness, nausea, vomiting, depression of all senses, and also unconsciousness. Under some 

circumstances of over-exposure (i.e., oxygen levels fall below 6 percent by volume), death may occur. 

If inhaled, R-513A can cause symptoms such as light-headedness, dizziness, confusion, incoordination, 

drowsiness, unconsciousness, and anesthetic effects. Excessive inhalation of R-513A may also result in an 

irregular heartbeat or death, due to cardiac effects. Furthermore, R-513A vapors are denser than air and can 

cause asphyxiation if the oxygen concentration in a room is significantly reduced. 

If R-513A is inhaled, person(s) should be immediately removed from the contaminated space and exposed 

to fresh air. In accordance with the SDS, EPA further recommends that if breathing is difficult or irregular, 

person(s) should be given oxygen, provided a qualified operator is present, and medical attention be 

sought. Exposures of R-513A to the skin may cause frostbite. In the case of dermal exposure, the SDS for 

R-513A recommends that person(s) immediately wash the affected area with water and remove all 

contaminated clothing; if frostbite occurs, bathe (not rub) the affected area with lukewarm, not hot, water. 

If water is not available, cover the affected area with a clean, soft cloth, and seek medical attention 
Final—July 2, 2015

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immediately. Exposures of R-513A to the eyes could cause eye irritation. In case of ocular exposure, the 

SDS for R-513A recommends that person(s) immediately flush the eyes, including under the eyelids, with 

copious amounts of water for 15 minutes. 

EPA’s review of the human health impacts of this proposed substitute is contained in the public docket for 

this decision. These risks and procedures after exposure are similar for other common refrigerants. The 

potential health effects of R-513A can be minimized by following the exposure guidelines and ventilation 

and PPE recommendations outlined in the SDS for R-513A and this risk screen.

7. FLAMMABILITY ASSESSMENT

R-513A is classified as an A1 refrigerant by ASHRAE, and is considered to be nonflammable (DuPont 

Fluoroproducts 2014; ASHRAE 2015). Based on this classification, manufacture, servicing, and use of R513A is not expected to present a flammability risk in the retail food refrigeration, vending machines, or 

commercial ice machine end-uses.

8. ASPHYXIATION ASSESSMENT

The risk of asphyxiation for the reasonable worst-case scenario described in Section 5 was investigated for 

R-513A. In this section, risk of asphyxiation is assessed in three ways: 1) modeling the oxygen 

concentration under the charge size and room size specified in the worst-case scenario, 2) performing a 

threshold analysis of minimum charge size at which an asphyxiation risk could occur in the room size 

specified in the worst-case scenario (i.e., charge sizes greater than this are expected to cause an 

asphyxiation risk), and 3) performing a threshold analysis of the maximum room size at which an 

asphyxiation risk could occur with the charge size specified in the worst-case scenario (i.e., room sizes 

smaller than this are expected to cause an asphyxiation risk). This analysis does not consider ventilation or 

conditions that are likely to occur that would increase oxygen levels to which individuals would be 

exposed, such as open doors or windows, fans operating, conditioned airflow (either heated or cooled), or 

even openings at the bottom of doors that allow air to flow in and out. As specified in Section 5, the 

reasonable worst-case scenario assumes a vertical concentration gradient. If the proposed substitute passes 

the screening analysis with these restrictive assumptions in place, it can be reasonably assumed that no 

risks of asphyxiation will be present under real-world conditions. The results of the asphyxiation 

assessment are summarized in Table 7 below.

Table 7. Asphyxiation Assessmenta,b

Equipment Scenario Charge 

Size (kg)

Effective Room 

Size (m3)

Percent Oxygen 

Concentration in 

Lower 0.4 Meters

Direct Rack System Reasonable Worst-Case 1 800 24,200 (855,000 ft3) 19%

Beverage Cooler Reasonable Worst-Case 2 1.5 244 (8,620 ft3) 21%

Vending Machine Reasonable Worst-Case 3 0.6 15 (530 ft3) 20%

Ice Machine Reasonable Worst-Case 4 30 5,700 (201,300 ft3) 21%

Direct Rack System Threshold Analysis 1a: Charge Size 3,360 24,200 (855,000 ft3) 12%

Threshold Analysis 1b: Room Size 800 5,760 (203,000 ft3) 12%

Beverage Cooler Threshold Analysis 2a: Charge Size 76 244 (8,620 ft3) 12%

Threshold Analysis 2b: Room Size 1.5 5 (169 ft3) 12%

Vending Machine Threshold Analysis 3a: Charge Size 4.7 15 (530 ft3) 12%

Threshold Analysis 3b: Room Size 0.6 2 (67.8 ft3) 12%

Ice Machine Threshold Analysis 4a: Charge Size 790 5,700 (201,300 ft3) 12%

Threshold Analysis 4b: Room Size 30 220 (7,620 ft3) 12%

Bold font indicates modeling results.
Final—July 2, 2015

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a Cells highlighted in green are the scenarios in which the charge and room sizes evaluated in this risk screen are acceptable according to the 

threshold analysis or the scenarios with acceptable oxygen concentrations, given various modeling assumption options. b The typical concentration of oxygen in air is considered to be 21 percent (Mackenzie & Mackenzie 1995).

Based on the worst-case scenario modeling assumptions, R-513A in retail food refrigeration, vending 

machines, and commercial ice machines does not present a significant risk of asphyxiation. In Reasonable 

Worst-Case Scenario 1 for direct rack systems, the percent oxygen concentration in the lower 0.4 meters of 

the room was modeled to be approximately 19%, which is lower than 19.5% and therefore may pose a risk 

of experiencing symptoms of asphyxiation as discussed in Section 6. However, this risk is not likely as the 

model does not take into account the presence of ventilation. Furthermore, the normal concentration of 

oxygen in air (21 percent) in the lower 0.4 meters of the room must be reduced more significantly, to 12 

percent, in order for an actual risk of asphyxiation to occur.

6 Based on the reasonable worst-case scenario 

modeling assumptions, use of R-513A in retail food refrigeration equipment, vending machines, and 

commercial ice machines does not present a significant risk of asphyxiation.

• As shown in Threshold Analysis 1a for direct rack systems, the minimum charge size of R-513A

necessary to reduce the oxygen levels to 12 percent in air in the lower 0.4 meters of a room of 

volume 24,200 m3 (855,000 ft3

) was calculated to be 3,360 kg assuming that 1) nitrogen and 

oxygen retain the same relative volumes in the rooms with the balance composed entirely of R513A, and 2) the pressure of the room does not increase significantly with the addition of the 

refrigerant. This amount represents more than eight times the typical charge of approximately 400 

kg (or more than four times the maximum charge size of 800 kg) for a direct rack R-513A system. 

• Under Threshold Analysis 2a for beverage coolers, the minimum charge of R-513A necessary to 

reduce the oxygen levels to 12 percent in air in the lower 0.4 meters of a room of volume 244 m3

(8,620 ft3

) was calculated to be 76 kg, which represents approximately 250 times the typical 

charge of 0.3 kg for a single R-513A beverage cooler (or more than 50 times the maximum 

intended charge size of 1.5 kg). 

• For vending machines, Threshold Analysis 3a shows that the minimum charge of R-513A

necessary to reduce oxygen levels to 12 percent in air in the lower 0.4 meters of a room of volume 

5,700 m3 (201,300 ft3

) was calculated to be 4.7 kg, more than 15 times the typical charge of 0.3 kg

for a vending machine (or more than 7 times the maximum charge size of 0.6 kg). 

• For commercial ice machines, Threshold Analysis 4a shows that the minimum charge of R-513A

necessary to reduce oxygen levels to 12 percent in air in the lower 0.4 meters of a room of volume 

5,700 m3 (201,300 ft3

) was calculated to be 792 kg, more than 264 times the typical charge of 3 kg

for a commercial ice machine (or more than 26 times the maximum charge size of 30 kg). 

Because this threshold modeling does not take into account any ventilation which is likely to occur, such 

as conditioned airflow, open doors, or even openings at the bottom of doors that allow air to flow in and 

out, as mentioned above, the actual asphyxiation risk to consumers is likely to be lower than modeled. 

For the room size threshold scenarios, the room size at which an asphyxiation concern would exist (i.e., 

when the oxygen concentration in the lower 0.4 meters of the room is 12 percent) using the typical 

equipment charge sizes provided by the submitter were also determined: 

• For direct rack systems, in order for asphyxiation to be of concern with a charge size of 800 kg, 

the system would have to be installed in a store with an effective volume of 5,760 m3 (203,000 ft3

) 

(see Threshold Analysis 1b in Table 7). 

• For beverage coolers, in order for asphyxiation to be of concern with the maximum charge size of 

1.5 kg, the volume of the convenience store would have to be about 5 m3 (169 ft3

) (see Threshold 

Analysis 2b in Table 7). 

 5 Twelve percent oxygen in air is the NOAEL for hypoxia (ICF 1997).
Final—July 2, 2015

10

• For vending machines, Threshold Analysis 3b indicates that the volume of the enclosed alcove 

would have to be about 2 m3 (67.8 ft3

) with the maximum charge size of 0.6 kg in order for 

asphyxiation to be of concern.

• For commercial ice machines, Threshold Analysis 4b indicates that the volume of the seafood 

processing facility would have to be about 216 m3 (7,620 ft3

) with the maximum charge size of 30

kg in order for asphyxiation to be of concern. 

Based on the worst-case modeling results and threshold analysis, EPA does not believe that the use of R513A in retail food refrigeration, vending machines, and commercial ice machines poses a significant risk 

of asphyxiation or impaired coordination to personnel, provided systems are installed in appropriate spaces 

according to guidelines from the manufacturer and the SDS for R-513A.

9. END-USE EXPOSURE ASSESSMENT

This section presents estimates of potential end-user exposures to R-513A and each of its components in 

the event of a catastrophic release from the proposed substitute’s use in retail food refrigeration, vending 

machines, and commercial ice machines. An end-use exposure analysis was performed to examine 

potential catastrophic releases of R-513A under the reasonable worst-case scenarios outlined in Section 5.

For the end-use exposure assessment scenario, 15-minute TWA exposures for the proposed substitute were 

calculated using the box model described in the Background Document, which was adapted to estimate 

concentrations on a minute-by-minute basis. Estimates for acute/short-term end-use exposures resulting 

from catastrophic leakage of refrigerant from retail food refrigeration, vending machines, and commercial 

ice machines were examined. As discussed in Section 5, the full charge of the unit is assumed to be 

emitted over the course of 1 minute and 15 minutes, where the latter scenario more accurately represents a 

reasonable worst-case scenario for R-513A in retail food refrigeration, vending machines, and commercial 

ice machines because R-513A is nonflammable. 

The analysis was undertaken to determine the 15-minute exposures for R-513A, which were then 

compared to the standard toxicity limits presented in Table 5 to assess the risk to end-users. The estimated 

TWA values are fairly conservative as the analysis does not consider opened windows, fans operating, 

conditioned airflow (either heated or cooled) and other variables that would reduce the levels to which 

individuals would be exposed. Because HFO-1234yf is present in larger concentrations and because it has 

a lower exposure limit than HFC-134a, Table 8 only displays exposures for HFO-1234yf, the component 

with greater potential concerns. 

Table 8. End-Use Exposure Assessment for HFO-1234yf Componenta

Equipment R-513A

Component

Charge 

Size (kg)

Room 

Size (m3)

15-minute TWA 

Occupational Exposure 

(ppm)

15-min Short 

Term Exposure 

Limits (ppm)

Acute Toxicity 

Exposure 

Limit (ATEL)

(ppm) 1-minute 

release

15-minute 

release

Direct Rack System

HFO-1234yf

800 24,400 22,400 15,700

1,500 101,000b Beverage Cooler 1.5 244 3,740 2,070

Vending Machines 0.6 15 25,800 14,000

Ice Machine 30 5,700 2,130 1,730

Bold font indicates modeling results. a Cells highlighted in green are the scenarios with acceptable exposure levels given various modeling assumption options.

b ATEL for HFO-1234yf is 101,000 ppm; see Table 4 for more information.

Under the reasonable worst-case scenarios described in Section 5 for direct rack systems, beverage coolers, 

vending machines, and ice machines, catastrophic releases of the maximum charge sizes of R-513A were 

modeled. The modeling scenarios evaluate two refrigerant release time durations (i.e., 1 minute and 15 

minutes). The anticipated 15-minute TWA exposures for the HFO-1234yf component of R-513A are likely 
Final—July 2, 2015

11

to exceed their respective STELs for direct rack systems and vending machines, assuming both 1-minute 

and 15-minute releases.

Although the exposure estimates for the reasonable worst-case scenario for a direct rack system and 

vending machines exceed the respective STELs for the HFO-1234yf component (see Table 8), the STEL is 

a conservatively-derived exposure limit that is intended to protect workers in an occupational setting in 

which they are exposed to these chemicals on a daily basis. The STEL values do not represent limits for a 

single exposure in a lifetime. These modeled exposures are one-time exposures so exceedances of the 

STEL values do not necessarily indicate a significant risk of harm to consumers. The effect of a one-time 

exposure can be more accurately evaluated by comparing the modeled exposure concentrations to the 

ATEL for HFO-1234yf, which is a limit intended to reduce the risks of acute toxicity hazards in normally 

occupied, enclosed spaces according to ASHRAE Standard 34 (see Table 4). All of these exposure 

estimates are significantly lower than the ATEL of 101,000 ppm for HFO-1234yf. Furthermore, the 

estimated exposures for R-513A in each of these scenarios are also significantly lower than the RCL for R513A (i.e., 72,000 ppm).

In addition, these exposure estimates were derived using fairly conservative assumptions (e.g., minimum 

room volume for the modeled maximum charge size, low ventilation rate, maximum charge size) that do 

not necessarily reflect the actual room attributes where R-513A retail food refrigeration equipment, 

vending machines, and commercial ice machines will be installed. Finally, these exposures represent 

concentrations of leaked refrigerant in the bottom 0.4 meters (1.3 feet) of the room, accounting for 95 

percent of the refrigerant charge in this lower compartment of the room. The probability that an individual 

would be present in this lower compartment (e.g., prone or supine on the floor) in the event of the 

catastrophic release of refrigerant is low. Furthermore, although children may be at increased risk because 

of their short stature when the proposed substitute is found at higher concentrations in the lower 

compartment of the room, the probability that they are present in the location in which a catastrophic 

release of the entire charge of the commercial refrigeration system is low.

To prevent exposure and potential serious side effects during larger releases, EPA recommends that the 

proposed RCL for R-513A (i.e., 72,000 ppm or 320 g/m3

) is not exceeded in any location where an R513A system is installed, unless proper leak protection devices are in place in order to prevent exposures 

of R-513A beyond the recommended limits. Proper leak protection devices, engineering control 

requirements, and adherence to the SDS will further ensure that exposure limits are maintained below 

those described in Table 8. 

10. OCCUPATIONAL EXPOSURE ASSESSMENT

This section assesses potential exposures to workers during manufacture, charging and servicing, and 

disposal of R-513A retail food refrigeration equipment, vending machines, and commercial ice machines. 

To ensure that use of the proposed substitute in retail food refrigeration, vending machines, and 

commercial ice machines does not pose an unacceptable risk to workers during servicing and disposal, 

occupational exposure modeling was performed using a box-model approach. For a detailed description of 

the methodology used for this screening assessment, the reader is referred to the occupational exposure and 

hazard analysis described in Chapter 5 of the Background Document. 

Estimates of refrigerant release per event for various release scenarios were obtained from the Vintaging 

Model.7

 To determine the estimated level of occupational exposure for a constituent in a blend, the total 

anticipated release rate of the refrigerant is multiplied by the weight percent composition of each 

 7 ICF International maintains the Vintaging Model for EPA in order to simulate the aggregate impacts of the ODS phaseout on the 

use and emissions of various ODS and their substitutes over a period of several years across 60 different end-uses. The model 

tracks the use and emissions of various compounds for the annual vintages of new equipment that enter service in each end-use. 

The vintage of each type of equipment determines such factors as leak rate, charge size, number of units in operation, and the 

initial ODS substance that the equipment contained. 
Final—July 2, 2015

12

compound in the blend. For charging, servicing, and disposal activities, the release rate per event was 

multiplied by the number of events estimated to occur over a workday. During charging and servicing of 

the retail food refrigeration, vending machine, and commercial ice machine end-uses, the release per event 

was conservatively assumed to range between 0.25 percent and 5 percent of the equipment charge, 

respectively. For equipment charging and servicing, the number of events per workday was assumed to 

equal the maximum number of units anticipated to be serviced in one day (i.e., eight units divided by eight 

hours per workday for beverage coolers, vending machines, and commercial ice machines, and one unit 

divided by eight hours per workday for direct rack systems) (see Section 10.2).

For disposal of direct rack systems, it was conservatively assumed that one unit is disposed of during an 8-

hour work day. For smaller equipment (i.e., beverage coolers, vending machines, and commercial ice 

machines), the release per event was conservatively assumed to be 100 percent of the equipment charge 

(representing a catastrophic release). It was assumed that 10 units are disposed during an 8-hour work day; 

however, it was assumed that of the 10 units, only the last unit per workday would experience the 

catastrophic release (i.e., 100 percent). The remaining 9 units were assumed to release an incidental 

amount of refrigerant (i.e., 1 percent per unit) from the connecting and disconnecting of lines, as it is likely 

that if a worker was exposed to the entire charge of a system during disposal activities, they would 

immediately stop working, clear the area until all refrigerant has been removed from the space (e.g., 

through ventilation), and adhere to the exposure procedures recommended in the SDS for the proposed 

substitute (see Section 10.3).

The modeled exposure concentrations were compared to STELs at charging and servicing and long-term 

exposure limits at disposal.

10.1 Occupational Exposure at Manufacture

During manufacture of the components and blending of R-513A, the SDS for both HFC-134a and HFO1234yf should be referenced and proper engineering controls and PPE used. 

Refrigerant quality control testing may also result in release of de minimus quantities of refrigerant, which 

would typically be to exhaust ducts or fume hoods. 

To prevent significant exposure if such leaks occur, engineering controls should be used, including normal 

and local ventilation (e.g., chemical hoods) and vapor-in-air detection systems for standard manufacturing 

procedures so workers can avoid physical contact with the refrigerant and to achieve emission control. In 

general, use of PPE consistent with OSHA guidelines is recommended, such as respiratory protection 

(including a self-contained breathing apparatus [SCBA] in case of insufficient ventilation), tightly sealed 

goggles, and protective gloves (OSHA 1994).

In addition, as for other halogenated refrigerants, there is a risk of generation of toxic degradation products 

such as hydrogen fluoride and hydrogen chloride if HFC-134a or HFO-1234yf are exposed to high 

temperatures or fire. Other reaction products such as carbon dioxide might also be present. Containers 

should be stored in cool, dry conditions (maximum storage temperature should be 40°C) in well-sealed 

receptacles and should not be allowed to contact open flames, glowing metal surfaces, or electrical heating 

elements. EPA believes that when proper handling and disposal guidelines are followed, in accordance 

with both good industrial hygiene and manufacturing practices and the SDS for R-513A and its 

components, there is no significant risk to workers during the manufacture of R-513A.

10.2 Occupational Exposure at Charging and Servicing

Large commercial refrigeration equipment (e.g., direct rack systems) is typically field-erected and 

therefore, equipment is charged in the field. Charging for smaller retail refrigeration equipment (e.g., 

beverage coolers and commercial ice machines) would be conducted by the Original Equipment 

Manufacturer (OEM). For both OEM system manufacture (i.e., charging at OEM location) and field 

charging (i.e., charging at the end-use location), points of release for charging and servicing these leak-
Final—July 2, 2015

13

tight systems would be from connection/disconnection of temporary lines for charging and recovery 

equipment.

Charging occurs within an enclosed area equipped with automatic ventilation, refrigerant detectors, and 

alarm systems. Release points during charging would be connection/disconnection of temporary lines from 

charging equipment. 

Charging and servicing activities for retail refrigeration equipment, vending machines, and commercial ice 

machines are not expected to result in significant worker exposure when certified technicians follow the 

procedures outlined in the R-513A SDS and maintenance manual, undergo proper training, and wear 

appropriate PPE (e.g., gloves and safety glasses). Nevertheless, the potential occupational exposure during 

servicing was analyzed. The maximum 15-minute TWA exposures for each R-513A constituent were 

estimated for the charging and servicing exposure scenarios and compared to their respective STELs (see 

Table 9). Because HFO-1234yf is present in larger concentrations and because it has a lower exposure 

limit than HFC-134a, Table 9 only presents exposures for HFO-1234yf, the component with greater 

potential concerns.

Table 9. Occupational Risk Assessment at Charging and Servicing for HFO-1234yf Componenta

Equipment R-513A 

Component

Charging Servicing 15-min Short Term 

Exposure Limits 

(ppm)c

Release 

Rateb

15-minute 

TWA (ppm)

Release 

Rateb

15-minute 

TWA (ppm)

Direct Rack Systemd

HFO-1234yf

2% 2,440 5% 5,610

1,500 Beverage Cooler 1% 16 0.25% 17

Vending Machine 1% 6.4 0.25% 6.7

Ice Machine 1% 320 3% 4,030

Bold font indicates modeling results. a Cells highlighted in green are the scenarios that are deemed to be acceptable given various modeling assumption options.

b Release rates are consistent with IPCC (2006), CARB (2013), and EPA’s Vintaging Model. c See Table 5 for more information. d One installation or servicing event per day was modeled for direct rack systems.

The 15-minute STEL for the HFO-1234yf component of R-513A is not exceeded in the charging exposure 

scenarios for beverage coolers, vending machines, or ice machines. However, the 15-minute estimated 

exposures for charging the direct rack system exceeded the STEL for HFO-1234yf. The 15-minute STEL 

for the HFO-1234yf component is not exceeded in the servicing scenario for beverage coolers and vending 

machines. However, the 15-minute estimated servicing exposures for HFO-1234yf in direct rack systems 

and ice machines exceeded the STEL for HFO-1234yf. Although the modeling indicates that the worstcase charging scenario for direct rack systems and the worst-case servicing scenario for direct rack systems

and ice machines could exceed the STEL for HFO-1234yf, the estimated exposures were derived using 

conservative assumptions, and do not take into account the use of ventilation or PPE. Additionally, all of 

these exposure estimates are significantly lower than the ATEL of 101,000 ppm for HFO-1234yf, which is 

a limit intended to reduce the risks of acute toxicity hazards in normally occupied, enclosed spaces 

according to ASHRAE Standard 34. Furthermore, these types of systems are typically serviced by Section 

608-certified personnel using proper industrial hygiene techniques and using proper engineering controls 

(e.g., local ventilation, refrigerant detectors, and alarm systems). Thus, EPA does not believe that charging, 

installation, or servicing of retail food refrigeration units, vending machines, and commercial ice machines 

containing R-513A presents a significant concern to workers.

10.3 Occupational Exposure at Disposal

Disposal of R-513A retail food refrigeration equipment is expected to occur with limited frequency (up to 

approximately ten disposal events per day for smaller equipment such as beverage coolers and commercial 

ice machines and one disposal event per day for direct rack systems) at disposal facilities or, for larger 

equipment (e.g., direct rack systems) at the end-use and with limited duration of exposure to the installed 

refrigerant. Typically, potential exposures to the refrigerant during recovery and disposal are expected to 
Final—July 2, 2015

14

occur during activities related to decommissioning refrigeration systems (e.g., attaching of hoses 

associated with draining or otherwise discharging of refrigerant from the refrigeration units into cylinders) 

and would be similar to those during servicing, because similar refrigerant charging and/or recovery 

equipment would be used (see Section 10.2 and Table 9 for information and modeling results related to 

exposure during servicing activities). 

As shown in Table 9 in Section 10.2, exposures during servicing (and therefore during typical disposal 

activities) are not anticipated to present a significant concern for workers. To model a worst-case scenario 

during disposal for direct rack systems, it was conservatively assumed that 14 percent of the equipment 

charge would be released per disposal event. For smaller equipment (i.e., beverage coolers, vending 

machines, and commercial ice machines), it was assumed that of the 10 disposal events, 9 units are 

properly disposed of with only incidental releases of refrigerant (i.e., 1 percent per unit) followed by the 

disposal of one unit that results in a catastrophic release of refrigerant (i.e., 100 percent of the equipment 

charge). Because HFO-1234yf is present in larger concentrations and because it has a lower exposure limit 

than HFC-134a, Table 10 only presents the maximum estimated 8-hour TWA occupational exposure levels 

at disposal for HFO-1234yf, the component with greater potential concerns. 

Table 10. Occupational Risk Assessment at Disposal for HFO-1234yf Componenta

Equipment R-513A Component

8-Hour TWA 

Occupational 

Exposure (ppm)

8-Hour Long Term 

Exposure Limitsb

(ppm)

Direct Rack System

HFO-1234yf

2,280

500 Beverage Cooler 120

Vending Machine 120

Ice Machine 2,500

Bold font indicates modeling results. a Cells highlighted in green are the scenarios with exposure levels deemed to be acceptable given various modeling assumption options. b WEEL OEL

The results in Table 10 indicate that long-term (8-hour) worker exposure concentration of the HFO-1234yf 

component of R-513A is not likely to exceed its WEEL (i.e., 500 ppm) for the beverage cooler or vending 

machine scenarios while the reasonable worst-case disposal scenario for direct rack systems and 

commercial ice machines could exceed the WEEL for HFO-1234yf. However, the estimated exposures 

were derived using conservative assumptions (e.g., no mechanical or local exhaust ventilation), and 

represent a worst-case scenario with a low probability of occurrence (e.g., for smaller commercial 

refrigeration equipment, it is highly unlikely that a worker would be exposed to the maximum release rate 

at disposal for every unit decommissioned in a day). These types of systems are also typically disposed of 

by Section 608-certified personnel using proper industrial hygiene techniques to maximize recovery 

efficiency and limit releases. The average recovery efficiencies and maximum disposal release rates (see 

Table 10) are also representative of release rates for currently used refrigerants in commercial refrigeration 

equipment (e.g., R-404A, R-507A, R-407C), and there are already established standards of practice and 

training requirements that apply to fluorinated refrigerants to reduce exposures (and would therefore 

extend to R-513A systems). 

It is also unlikely that workers would be exposed to the unrecoverable portion of refrigerant during the 

recovery process, and therefore anticipated exposures would be approximately 10 percent lower. For 

example, some of the refrigerant would likely be dissolved in the refrigerant oil (which would be drawn 

out and separated from the recovered refrigerant) or trapped within deeper parts of the refrigeration circuit 

(e.g., the accumulator or receiver) and wouldn’t be released until the system is actually dismantled later on 

in the disposal process (Oko-Recherche 2003). 

Because anticipated occupational exposures could be above the exposure limits for HFC-134a and HFO1234yf for the direct rack system, beverage cooler, and commercial ice machine disposal release scenarios, 
Final—July 2, 2015

15

the recommendations for proper engineering controls and PPE in the SDS for R-513A should be followed. 

Adequate ventilation should always be established during any use, handling, or storage of R-513A. If 

recovery and disposal is taking place in an enclosed space without any mechanical ventilation, facilities 

should be cleared of non-essential personnel and technicians should wear a SCBA and other appropriate 

protective equipment. 

Engineering controls should include vapor-in air detection systems and local exhaust ventilation during use 

of R-513A to prevent dispersion throughout the workplace. In addition, an eye wash and safety shower 

should be near the manufacturing facility and locations where R-513A is stored and ready for use. In 

general, use of PPE is recommended, such as splash goggles, mechanical-resistance gloves (e.g., oilrepellent or thermal resistant gloves) when handling cylinders and chemically-resistant gloves when 

handling the gas mixture (e.g., butyl rubber, chlorinated polyethylene, or neoprene). For larger retail food 

refrigeration (e.g., rack systems) and commercial ice machine (e.g., remote systems) systems, toxicity risks 

could be further minimized through the installation of signage which warns room occupants to remain 

standing (as higher concentrations are likely to accumulate near the floor), not to enter recessed parts of the 

facility (e.g., maintenance crawl spaces and below grade service areas), and exit the facility immediately 

should they hear the refrigerant detector alarm and/or smell the leaked refrigerant. EPA believes that if 

proper handling and disposal guidelines are followed, in accordance with good industrial hygiene and 

manufacturing practices and the SDS for R-513A, there is no significant risk to workers during the 

manufacturing, installation, servicing, and disposal of R-513A in retail food refrigeration units, vending 

machines, and commercial ice machines.

11. GENERAL POPULATION EXPOSURE ASSESSMENT

R-513A is not expected to cause a significant risk to human health in the general population when 

manufactured for use and used as a refrigerant in retail food refrigeration, vending machines, and 

commercial ice machines. The proposed substitute will be manufactured in a closed process and is 

proposed for use in closed systems; thus, significant releases are not anticipated. At room temperature, R513A is a gas and, therefore, releases to ground or surface water are not anticipated, as R-513A is 

anticipated to dissipate into the atmosphere upon release to outside air (i.e., because natural ventilation 

rates would be higher and there is no enclosed space to maintain a high concentration of R-513A). Should 

air releases during manufacturing operations occur, engineering controls should be used (e.g., carbon 

absorption scrubbers) to collect R-513A and prevent the release of R-513A to the atmosphere. EPA 

believes that by using proper engineering controls and by following disposal and containment 

recommendations outlined in the proposed substitute’s SDS and this risk screen, exposure to R-513A is not 

expected to pose a significant toxicity risk to the general population. 
Final—July 2, 2015

16

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