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Case Study 200: When a Refrigerant Becomes a Hazard

When a Refrigerant Becomes a Hazard: Anhydrous Ammonia Release Exposure Assessment

By Paul E. Rosenfeld, M.S., Ph.D., Principal Environmental Chemist, RoseyFields LLC, Santa Monica, California

An essential industrial chemical with acute hazard potential

Anhydrous ammonia is widely used as an industrial refrigerant, particularly in food processing and cold storage facilities, and as an agricultural fertilizer, making it one of the highest-volume industrial chemicals in the country, and its combination of high production volume, transport frequency, and acute toxicity makes accidental release exposure assessment a distinct and recurring environmental forensics need.

The regulatory framework governing ammonia release prevention

EPA’s Risk Management Program requires facilities storing ammonia above threshold quantities to develop release prevention programs, conduct hazard assessments, and prepare emergency response plans, while OSHA’s Process Safety Management standard imposes parallel requirements addressing the process safety systems intended to prevent an accidental release in the first place (US EPA, 40 CFR Part 68; OSHA, 29 CFR 1910.119).

Why acute exposure reconstruction differs fundamentally from chronic exposure work

Unlike the multi-decade historical reconstructions common to legacy contamination litigation, an ammonia release exposure assessment typically addresses a single, short-duration acute event, hours or less, requiring a fundamentally different technical approach centered on emergency-release atmospheric dispersion modeling calibrated to the specific release rate, duration, and immediate meteorological conditions rather than long-term average concentrations.

Specialized dense-gas dispersion modeling

Because ammonia vapor released from a pressurized or refrigerated source can initially behave as a dense gas that sinks and spreads along the ground rather than dispersing like a neutrally buoyant plume, acute ammonia release modeling frequently requires specialized dense-gas dispersion models rather than the standard Gaussian plume models used for routine industrial emissions, a modeling distinction with direct implications for predicted near-source concentrations (US EPA, ALOHA Model).

The concentration-dependent acute health effect thresholds

Ammonia’s health effects are strongly concentration-dependent, ranging from detectable odor and mild irritation at low parts-per-million concentrations to immediately dangerous to life or health conditions at higher concentrations, with NIOSH’s Immediately Dangerous to Life or Health value and EPA’s Acute Exposure Guideline Levels providing the standard regulatory benchmarks for evaluating a reconstructed acute exposure concentration against specific health effect categories (NIOSH, IDLH; US EPA, AEGL Values for Ammonia).

Reconstructing the release source term

A defensible acute exposure reconstruction begins with the release source term, the total quantity released, the release rate over time, and the physical state and temperature of the ammonia at release, information typically drawn from facility process records, incident investigation reports, and post-incident regulatory filings rather than direct air monitoring, since acute releases rarely occur with monitoring equipment already deployed at the eventual exposure location.

Meteorological conditions at the time of the specific event

Because a dense-gas or Gaussian plume model’s predicted concentration at a given receptor depends heavily on the specific wind speed, wind direction, and atmospheric stability present at the exact time of the release, acute exposure reconstruction requires meteorological data specific to the incident date and time rather than the long-term average conditions used in chronic exposure assessments.

Respiratory and ocular effects as the primary health endpoints

Ammonia’s toxicological profile is dominated by acute respiratory tract and ocular irritation and, at sufficiently high concentrations, chemical burns to the airway and eyes, rather than the cancer risk profile central to many other chemicals addressed in this case study series, meaning the relevant medical causation questions in ammonia release litigation typically concern acute injury severity and any resulting chronic respiratory impairment rather than cancer causation (ATSDR, Toxicological Profile for Ammonia).

Why community notification and evacuation records matter to exposure reconstruction

Emergency response records, including community notification timing, evacuation zone boundaries, and any air monitoring conducted during the emergency response itself, provide contemporaneous evidence that can corroborate or refine a subsequent dispersion modeling reconstruction, making preservation and early collection of these emergency response records particularly time-sensitive compared to legacy contamination matters where historical records may remain available for years.

Why ammonia release litigation remains a recurring industrial hazard category

With anhydrous ammonia remaining essential to food refrigeration and agricultural fertilizer production nationally, and with aging refrigeration infrastructure at many industrial and food processing facilities, accidental ammonia releases continue to occur with sufficient regularity that acute exposure reconstruction methodology remains a continuing rather than purely historical practice need. A fuller account of Dr. Rosenfeld’s acute chemical release exposure assessment work can be found at RoseyFields.com.

References

1. US Environmental Protection Agency. Risk Management Program (RMP) Rule. 40 CFR Part 68.

2. Occupational Safety and Health Administration. Process Safety Management of Highly Hazardous Chemicals. 29 CFR § 1910.119.

3. National Institute for Occupational Safety and Health. Immediately Dangerous to Life or Health (IDLH) Value: Ammonia. Cincinnati, OH: CDC/NIOSH.

4. US Environmental Protection Agency. Acute Exposure Guideline Levels (AEGLs) for Ammonia. Washington, DC: US EPA.

5. Agency for Toxic Substances and Disease Registry. Toxicological Profile for Ammonia. Atlanta, GA: US Department of Health and Human Services; 2004.

6. US Environmental Protection Agency. Areal Locations of Hazardous Atmospheres (ALOHA) Model. Washington, DC: US EPA.

7. Occupational Safety and Health Administration. Permissible Exposure Limit for Ammonia. 29 CFR § 1910.1000, Table Z-1.

8. US Chemical Safety Board. Investigation Reports: Ammonia Refrigeration Releases. Washington, DC: CSB.

9. International Institute of Ammonia Refrigeration. Ammonia Refrigeration Safety Guidelines. Alexandria, VA: IIAR.

10. US Environmental Protection Agency. Revisions to the Guideline on Air Quality Models. 40 CFR Part 51, Appendix W. Fed Regist. 2017;82(10):5182-5235.

11. National Research Council. Acute Exposure Guideline Levels for Selected Airborne Chemicals, Volume 6: Ammonia. Washington, DC: National Academies Press; 2008.

12. US Environmental Protection Agency. Risk Management Program Guidance for Ammonia Refrigeration Facilities. Washington, DC: US EPA.

13. Rosenfeld PE. RoseyFields LLC: Acute Chemical Release Exposure Assessment. Santa Monica, CA: RoseyFields LLC; 2026.

14. US Environmental Protection Agency. Toxicological Review of Benzene (Noncancer Effects). Integrated Risk Information System (IRIS). Washington, DC: US EPA; 2003.