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.
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.
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.
FAQs
This test measures N‑acetyl‑S‑(2‑cyanoethyl)‑L‑cysteine (NACE), a urinary mercapturic‑acid metabolite and exposure marker formed from acrylonitrile and related 2‑cyanoethyl electrophiles.
It reflects recent internal exposure (typically via inhalation or dermal contact) and the body’s glutathione‑conjugation detoxification of those compounds, and is used in occupational and environmental biomonitoring to estimate acrylonitrile exposure.
Consider testing if you’re a current or recent smoker, have heavy secondhand smoke exposure, work around plastics/rubber manufacturing, or live near industrial sources—N-Acetyl (2-Cyanoethyl) cysteine (NACE) is a urine marker of acrylonitrile exposure from these settings.
It’s useful for establishing a baseline and for checking whether exposure-reduction steps (e.g., quitting smoking, improving ventilation/PPE) are working—levels typically fall when exposure drops.
Results are best interpreted alongside your exposure history and other relevant toxin markers; consult a clinician if your level is elevated or symptoms persist.
Obtain a baseline test once to assess exposure to N-Acetyl (2-Cyanoethyl) cysteine (NACE); if levels are elevated, perform periodic follow-up testing (for example every few months) to monitor changes, and retest after meaningful lifestyle or environmental changes — for example "after changing household products" or "following detoxification efforts."
Several factors can affect N-Acetyl (2-Cyanoethyl) cysteine (NACE) test results: timing of sample collection (levels can vary over time), recent exposure from food, air, water or consumer products, individual metabolism (including genetic and liver function differences), hydration status (which dilutes or concentrates urine), and the sample type used (urine versus blood have different matrices); certain medications or supplements may also influence readings.
Fasting is generally not required for N‑Acetyl (2‑Cyanoethyl) cysteine (NACE) testing; this test is usually performed on urine rather than blood. A first‑morning urine sample is often recommended because it is more concentrated and reduces within‑day variability, but many labs will accept a spot urine—follow the specific instructions from your testing lab or clinician.
If possible, avoid known recent exposures to likely sources (for example handling certain plastics or industrial materials, recent use of specific personal care products, or application/nearby use of pesticides) in the 24–48 hours before sampling to reduce the chance of acute contamination, though testing should not be delayed if the goal is to measure recent exposure. Document and tell the lab or clinician about any recent product use or environmental/occupational contacts (plastics, personal care items, pesticides, solvents, smoke, etc.), as this information helps interpret results and may affect sampling timing or instructions.
Accuracy depends strongly on sample timing (collection relative to exposure and whether a spot or 24‑hour sample is used), the laboratory method (mass spectrometry–based methods are preferred over less specific assays), and consistent, proper collection, handling, and storage (including normalization practices such as creatinine adjustment when appropriate). Biological variability (metabolism, hydration) and inconsistent sampling can cause false negatives or variability, so results are best interpreted alongside exposure history and, if needed, repeat testing or complementary biomarkers.
References
- De Jesús, V. R., Zhang, L., Bhandari, D., Zhu, W., Chang, J. T., & Blount, B. C. (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
- 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
- Calafat, A. M., & Needham, L. L. (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
- Barr, D. B., Wilder, L. C., Caudill, S. P., Gonzalez, A. J., Needham, L. L., & Pirkle, J. L. (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
- 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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