NACE: A Urinary Footprint of Acrylonitrile and Tobacco-Smoke Exposure

REVIEWED BY

William Maish, MD MBA MPH

Clinical Product Lead

Published

Last updated

Key takeaway:

This test measures N-acetyl-(2-cyanoethyl) cysteine (NACE), a urinary biomarker of acrylonitrile and tobacco-smoke exposure, revealing your toxicant burden from smoking, secondhand smoke, or occupational sources. Identifying and reducing this exposure may help lower risks linked to these pollutants, including cardiovascular strain, respiratory problems, and cancer risk.

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NACE: A urinary footprint of acrylonitrile exposure

N-Acetyl (2-Cyanoethyl) cysteine — abbreviated NACE — is a mercapturic acid your body produces after encountering acrylonitrile, a volatile compound found primarily in tobacco smoke, certain combustion emissions, and a few industrial settings. Once inhaled, acrylonitrile is conjugated to glutathione in the liver and ultimately excreted as NACE in urine.

Labs typically measure NACE in urine using mass spectrometry and report results adjusted to creatinine to account for hydration. Because acrylonitrile clears quickly, NACE reflects exposure over roughly the prior day or two rather than long-term body burden. It's a near-term snapshot, not a lifetime accumulation marker.

Why acrylonitrile exposure is worth quantifying

Acrylonitrile reaches the body almost entirely by inhalation, and tobacco smoke — both active and secondhand — is the dominant source for most people. Ambient air near certain combustion sources and a small number of workplace settings can also contribute. Inside the body, acrylonitrile draws on glutathione-dependent detoxification and kidney clearance, and regulatory agencies have flagged it for potential long-term concern at higher or sustained exposures.

NACE turns that exposure from an abstract concept into a measurable signal. It can separate a one-off encounter — a smoky bar, a single high-traffic commute — from sustained background contact, and it can show whether changes in environment or routine are actually moving the needle. The aim isn't a pass/fail cutoff; it's to know where you stand and whether the pattern shifts in the direction you want.

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Who benefits most from NACE testing

NACE is especially informative for people whose environments put acrylonitrile on the short list of plausible contributors:

  • Smokers and people living with smokers, where tobacco smoke is the dominant route.
  • People with regular secondhand smoke exposure at work or in shared housing.
  • Workers in or near combustion-heavy industrial settings.
  • Pregnant individuals or those planning pregnancy, when minimizing inhaled toxicant exposure carries extra weight.
  • Anyone wanting a baseline before and after a meaningful change — quitting smoking, moving households, changing work environments.

Reading a NACE result

Your report typically shows a creatinine-adjusted urine value compared against population-based reference data. For an environmental toxicant marker like NACE, lower values are generally preferable when feasible. Interpretation is most robust when you factor in what happened in the day or two before the test, and when you repeat testing to see direction and magnitude of change.

Relatively lower values usually signal limited recent exposure, with less near-term demand on glutathione-dependent detoxification and kidney clearance. In everyday terms, your body isn't currently encountering much acrylonitrile from smoke or ambient air.

Relatively higher values suggest recent or ongoing exposure. That can translate into added workload for the liver's glutathione pathways and the kidneys that excrete the resulting conjugates. Depending on individual sensitivity and the broader exposure mix, some people notice upper-airway or eye irritation, headaches, or neurologic discomfort — though symptoms are non-specific and shouldn't be attributed to a single biomarker. Because acrylonitrile's main route is inhalation, confirming a pattern with timing, environment, and follow-up measurements is more reliable than reading any single result.

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What can shift a NACE reading

Several inputs move the number without reflecting a change in true body burden:

  • Recent smoke exposure — even a single high-intensity event can produce a transient spike.
  • Hydration — spot urine concentrations shift with fluid intake, which is why creatinine normalization is standard.
  • Time-of-day variability — exposure is episodic, so collection timing relative to exposure events matters.
  • Individual differences in glutathione capacity and detoxification efficiency.
  • Lab methodology — detection limits and reference ranges vary across laboratories.

What to pair with a NACE result

NACE carries the most signal when read alongside other markers that frame combustion and smoke exposure:

  • Other tobacco-smoke biomarkers, where they're available on the same panel.
  • Other VOC metabolites, which can help distinguish broad combustion exposure from a single specific source.
  • Kidney function — creatinine and eGFR — because clearance shapes urine readings.
  • Liver function, since the liver handles the glutathione conjugation that produces NACE.

What a NACE test can and can't tell you

A single NACE result can quantify your recent acrylonitrile exposure, flag whether smoke or combustion sources are likely contributing, and provide a baseline to compare against later. It can't, on its own, identify the precise source, diagnose any specific condition, or measure long-term cumulative risk.

The signal sharpens with pattern over time. A clear decrease after a meaningful change — quitting smoking, removing exposure to secondhand smoke, changing work environments — suggests you've found a real source. Stable low values across consistent collection conditions suggest the current setup is keeping exposure modest.

Frequently Asked Questions

References

  1. De Jesús VR, Zhang L, Bhandari D, Zhu W, Chang JT, Blount BC (2021). Characterization of acrylonitrile exposure in the United States based on urinary N-acetyl-S-(2-cyanoethyl)-L-cysteine (2CYEMA): NHANES 2011-2016. *Journal of Exposure Science & Environmental Epidemiology*, *31*(2), 377-385. https://doi.org/10.1038/s41370-020-00286-1
  2. Pluym N, Gilch G, Scherer G, Scherer M (2015). Analysis of 18 urinary mercapturic acids by two high-throughput multiplex-LC-MS/MS methods. *Analytical and Bioanalytical Chemistry*, *407*(18), 5463-5476. https://doi.org/10.1007/s00216-015-8719-x
  3. Calafat AM, Needham LL (2008). Factors affecting the evaluation of biomonitoring data for human exposure assessment. *International Journal of Andrology*, *31*(2), 139-143. https://doi.org/10.1111/j.1365-2605.2007.00826.x
  4. Barr DB, Wilder LC, Caudill SP, Gonzalez AJ, Needham LL, Pirkle JL (2005). Urinary creatinine concentrations in the U.S. population: Implications for urinary biologic monitoring measurements. *Environmental Health Perspectives*, *113*(2), 192-200. https://doi.org/10.1289/ehp.7337
  5. Centers for Disease Control and Prevention. (2021). *Fourth national report on human exposure to environmental chemicals, updated tables, March 2021*. https://stacks.cdc.gov/view/cdc/105345

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