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Open AccessDOI: 10.0000/202605-1Original Research

Determination of Hydrazoic Acid and Sodium Azide in Workplace Air by Ion Chromatography with Suppressed Conductivity Detection

Binzhou Testing Center, Binzhou, 256600, China

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Determination of Hydrazoic Acid and Sodium Azide in Workplace Air by Ion Chromatography with Suppressed Conductivity Detection
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Published In
Environmental Chemistry
Published:January 15, 2026Edition:Vol. 45, Issue 5 • pp. 100-112Citation:ZHU Fuqiang et al. (2026), Environmental Chemistry
Impact FactorPeer-Reviewed Core
Source Journal环境化学

Key Takeaways & Executive Findings

  • • • Achieved baseline separation of azide (N3−) from nitrate (NO3−) using a Dionex IonPac™ AS11-HC column with KOH gradient elution, with retention times of 13.67 min and 14.88 min, respectively, eliminating interference from common anions. • • The method provides a limit of quantification (LOQ) of 0.005 mg·L−1 for N3− in solution, translating to minimum quantifiable air concentrations of 0.00256 mg·m−3 for hydrazoic acid and 0.00387 mg·m−3 for sodium azide, enabling detection below the occupational exposure limit. • • Spiked recoveries ranged from 92.0% to 100.4% across low (0.005 mg·L−1), medium (0.010 mg·L−1), and high (0.050 mg·L−1) levels, with relative standard deviations (RSD, n=6) between 0.76% and 2.51%, demonstrating high accuracy and precision. • • The method uses a simple sampling approach: 40 mg·L−1 KOH as absorption solution for vapor/mist and microporous membrane for sol, followed by elution, making it practical for routine workplace air monitoring.

Abstract

A method for the determination of hydrazoic acid and sodium azide in workplace air was established using ion chromatography with suppressed conductivity detection. Vapor and mist states of hydrazoic acid were collected in 40 mg·L−1 KOH absorption solution, while sol states of hydrazoic acid or sodium azide were collected on microporous membranes and eluted with 40 mg·L−1 KOH. Separation was performed on a Dionex IonPac™ AS11-HC (250 mm × 4.0 mm) anion analytical column with KOH gradient elution, followed by suppressed conductivity detection. The azide ion (N3−) exhibited good linearity in the range of 0.005–0.5 mg·L−1, with a correlation coefficient (r) of 0.9997. The limit of detection (S/N=3) was 0.002 mg·L−1, and the limit of quantification (S/N=10) was 0.005 mg·L−1. The minimum quantifiable concentrations in air were 0.00256 mg·m−3 for hydrazoic acid and 0.00387 mg·m−3 for sodium azide, based on a 10.0 mL sample solution and a 20 L air sample. Spiked recoveries ranged from 92.0% to 100.4%, with relative standard deviations (RSD, n=6) between 0.76% and 2.51%. The method is efficient, accurate, and sensitive, suitable for monitoring and safety assessment of hydrazoic acid and sodium azide in workplace air.

1. Introduction

Hydrazoic acid and sodium azide are highly toxic industrial chemicals used in energetic materials and pharmaceuticals. Their toxicity parallels cyanide, causing rapid absorption via inhalation, skin contact, and ingestion, leading to mucosal irritation, hypotension, organ damage, and central nervous system effects. Accurate determination of airborne concentrations is critical for occupational exposure assessment and worker safety. The current national standard method (GBZ/T 300.43-2017) employs ferric chloride spectrophotometry, which suffers from poor sensitivity and interference, with a minimum quantifiable concentration equal to the maximum allowable concentration, resulting in a 'detectable equals exceedance' dilemma that fails to reflect low-level exposure risks.

To address this bottleneck, the authors developed an ion chromatography method with suppressed conductivity detection, leveraging the high selectivity and sensitivity of IC for anions. Using a high-capacity AS11-HC column and KOH gradient elution, they achieved baseline separation of azide from nitrate, a common interferent. The method achieves a limit of quantification of 0.005 mg·L−1 in solution, corresponding to air concentrations of 0.00256 mg·m−3 for hydrazoic acid and 0.00387 mg·m−3 for sodium azide, well below the occupational exposure limits. This provides a reliable tool for accurate monitoring and safety evaluation in workplaces.

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Cite This Research Paper
ZHU Fuqiang, GANG Qiang, JIA Huimei, MENG Xianlong, LI Yuanyuan, CHEN Linlin (2026). Determination of Hydrazoic Acid and Sodium Azide in Workplace Air by Ion Chromatography with Suppressed Conductivity Detection. Environmental Chemistry. https://doi.org/10.0000/202605-1
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Frequently Asked Questions

What is the basis for selecting the AS11-HC column over other anion exchange columns for azide determination?

The AS11-HC high-capacity column was chosen because AS19 and AS11 columns failed to resolve azide (N3−) from nitrate (NO3−), which have similar chromatographic behavior. With AS11-HC and gradient elution, baseline separation was achieved with retention times of 13.67 min for N3− and 14.88 min for NO3−, ensuring accurate quantification without interference.

How does the method's sensitivity compare to the existing spectrophotometric standard, and what are the implications for regulatory compliance?

The ion chromatography method achieves a limit of quantification (LOQ) of 0.005 mg·L−1 in solution, corresponding to air concentrations of 0.00256 mg·m−3 for hydrazoic acid and 0.00387 mg·m−3 for sodium azide. This is significantly lower than the spectrophotometric method's minimum quantifiable concentration, which equals the occupational exposure limit, thus allowing detection of sub-limit exposures and avoiding the 'detectable equals exceedance' issue.

What are the recovery and precision metrics, and how do they validate the method's reliability for routine monitoring?

Spiked recoveries ranged from 92.0% to 100.4% across low, medium, and high concentration levels (0.005, 0.010, and 0.050 mg·L−1), with relative standard deviations (RSD, n=6) between 0.76% and 2.51%. These metrics demonstrate high accuracy and reproducibility, meeting the requirements for occupational exposure assessment.

How is the sampling procedure designed to capture different physical states of hydrazoic acid and sodium azide?

Vapor and mist states of hydrazoic acid are collected using 40 mg·L−1 KOH as an absorption solution in a multi-hole glass absorption tube. Sol states (aerosols) of hydrazoic acid or sodium azide are collected on a microporous membrane (0.80 μm pore size, 40 mm diameter) and subsequently eluted with 40 mg·L−1 KOH. This dual approach ensures comprehensive capture of both gaseous and particulate forms.

What is the total analysis time and throughput for routine monitoring?

The chromatographic run includes gradient elution with a final high-concentration step (35 mmol·L−1 KOH) to wash strongly retained components. The retention times for N3− and NO3− are 13.67 and 14.88 minutes, respectively, with additional time for column re-equilibration. The method is suitable for routine monitoring with a typical run time of approximately 20-25 minutes per sample, allowing efficient processing of multiple samples per day.

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