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Technical Review Article | Open Access | Published 29th September 2026


Nitrite-Driven Nitrosamine Formation in Pharmaceutical Systems: A Water-Mediated Risk Framework and Control Strategies


Santosh Bhende, Atul Phatak, Pravin Chaudhari - Department of Pharmaceutics, PES's Modern College of Pharmacy, Nigdi, Savitribai Phule Pune University, Pune, Maharashtra, India | EJPPS | 313 (2026)| https://doi.org/10.37521/ejpps31311  


 


Summary 


N-nitrosamines are genotoxic impurities whose detection in several marketed medicines has raised major safety concerns for pharmaceutical systems. They form when nitrosating agents - particularly nitrite - react with amine precursors under favourable physicochemical conditions. This review examines nitrite-driven nitrosamine formation with an emphasis on water-mediated pathways in pharmaceutical systems. It outlines the underlying nitrosation chemistry, including classical acid-catalysed routes and alternative chloramine-mediated and oxidative mechanisms, and evaluates how water sources, water-purification processes and physicochemical parameters (pH, temperature and moisture) influence formation. Particular attention is given to how trace nitrite in pharmaceutical water systems generates nitrosamines even at very low concentrations. Analytical methods for nitrosamine and nitrite determination are reviewed, highlighting advances in LC-MS/MS, GC-MS and high-resolution mass spectrometry for ultra-trace quantification. Risk-based mitigations are discussed, including nitrite control, water-quality management, raw-material assessment, process optimisation and lifecycle monitoring. A key regulatory gap identified is the absence of defined nitrite limits for pharmaceutical water in pharmacopoeial standards. Overall, the review offers a mechanistic, risk-oriented framework for understanding nitrite- and water-related nitrosamine formation and argues for stricter, precursor-focused control measures to safeguard pharmaceutical product quality and safety.


Keywords: Nitrite, Nitrosation mechanism, Water-mediated reactions, Nitrosamine formation, Pharmaceutical water systems, Regulatory risk assessment

 


Introduction


N-nitrosamines are potent genotoxic impurities that have drawn intense scientific and regulatory attention because of their carcinogenic potential1,2,3. The detection of N-nitrosodimethylamine (NDMA) and related nitrosamines in widely used medicines such as angiotensin II receptor blockers and ranitidine triggered global regulatory action and closer scrutiny of contamination-control practices4,5,6. These events exposed the complexity of nitrosamine formation and the need to define its sources across the entire pharmaceutical lifecycle2,3.


Nitrosamine formation typically involves reaction between nitrosating agents - chiefly nitrite - and secondary or tertiary amines under favourable physicochemical conditions7,8,9. In classical chemistry, nitrite yields nitrous acid and reactive intermediates such as dinitrogen trioxide that drive N-nitrosation8. Recent work shows that formation can also proceed through alternative routes, including chloramine-mediated and oxidative pathways, so risk assessment must consider both direct and indirect mechanisms10,11.


Although earlier emphasis fell on synthetic routes and excipients, water is increasingly recognised as an influential yet often overlooked participant. Water is not merely a solvent but a medium that promotes the transport, interaction and transformation of reactive species such as nitrite and amines, raising the probability of nitrosation7,12. Trace nitrite in pharmaceutical systems is now established as a major driver of nitrosamine formation even at very low concentrations13,12, and it can originate from raw materials, degradation, excipients and water7. Physicochemical parameters - pH, temperature and moisture - strongly modulate reaction kinetics and the stability of nitrosating species14. Despite advances in analytics and regulation, an important gap remains: neither the United States Pharmacopeia nor the European Pharmacopoeia specifies a nitrite limit for pharmaceutical water, although its role is well documented13. This review focuses on water-mediated mechanisms of nitrite-driven nitrosamine formation and integrates chemistry, analysis, mitigation and regulation into a risk-based framework6.



Chemistry and mechanisms of nitrosamine formation


Nitrosamine formation is governed by nitrosation reactions between nitrosating agents and amine substrates, strongly mediated by pH, temperature and reactivity14,15,16. Nitrite is pivotal: in aqueous systems it is protonated to nitrous acid (HNO2), a key intermediate in equilibrium with dinitrogen trioxide (N2O3), an efficient agent that converts secondary amines to N-nitrosamines15,16. Kinetics are highly pH-dependent. Mildly acidic conditions (about pH 3-4) favour HNO2 and N2O3 and promote nitrosation, whereas strong acidity over-protonates amines and reduces nucleophilicity, and neutral to alkaline conditions limit nitrosating species8,14. Even so, radical-mediated and aldehyde-assisted routes indicate that formation can occur across broader conditions7,8.


Secondary amines react directly to give stable N-nitrosamines, while tertiary amines generally require prior oxidative or hydrolytic dealkylation to reactive secondary intermediates15,16. Electronic and steric features of the amine influence reactivity and formation rate7,15. Water-treatment chemistry adds further pathways17: chlorination and chloramination form NDMA from monochloramine and dimethylamine or other amine precursors via unsymmetrical dimethylhydrazine-type intermediates10,9, and these reactions are sensitive to pH, disinfectant dose and organic precursors10. Ozonation can convert nitrogen-rich organics into reactive intermediates that undergo nitrosation18. Because many nitrosamines are polar and water-soluble, aqueous diffusion enhances precursor contact and raises the probability of reaction at trace levels1.



Water as a medium and source of nitrosating species


Water is a complex participant in nitrosamine formation, acting as solvent, reaction medium and a source of both nitrosating agents and precursors. Nitrite is the principal contributor, participating directly in nitrosation even at negligible concentrations1,11; it can arise from source-water contamination, the environment, and in situ nitrate reduction by microbial or chemical routes1. Although mildly acidic conditions favour nitrosating intermediates14, localised microenvironments - such as those in semi-hydrated solid dosage forms - can support nitrosation near neutrality through transient pH shifts and enhanced molecular mobility19. Sub-ppb nitrite has been reported to generate nitrosamines in the presence of reactive amines11, underscoring the need to control water-borne precursors.


Water treatment has a dual effect, removing precursors yet sometimes generating them. Chloramination is a well-known route to NDMA10,9; ozonation can transform nitrogenous organics into reactive intermediates18,20; and ion-exchange resins may degrade to release amine precursors17. Activated carbon can promote surface reactions or incompletely remove precursors10, while reverse osmosis and nanofiltration remove dissolved impurities efficiently but can foul, indirectly favouring nitrite formation via nitrate reduction1. Distillation yields high-purity water, yet storage and distribution can reintroduce trace precursors11. Source-water composition varies with agricultural runoff, industrial discharge and geochemistry, altering inorganic nitrogen and dissolved organic matter21. Drinking-water nitrite limits set by the World Health Organization and equivalent regulations are far above the levels that can drive nitrosation in pharmaceutical systems, highlighting a gap between environmental and pharmaceutical requirements22. Municipal chloramination adds monochloramine that reacts with amine-bearing components to form NDMA9, affecting the feed water used pharmaceutically. Even after purified-water or water-for-injection treatment, trace nitrite may persist or be introduced downstream11,7, so water should be assessed for reactivity as well as purity. The influence of common purification techniques is summarised in Table 1, and the regulatory status of pharmaceutical water types in Table 2.


Table 1. Influence of water purification techniques on nitrosamine formation risk

 

Water treatment technique

Primary function

Potential contribution to nitrosamine risk

Mechanistic basis

Chlorination / chloramination

Disinfection 35,36

Formation of NDMA and related nitrosamines 37,38

Reaction of chloramines with secondary/tertiary amines 39,38

Ozonation

Oxidation of organic contaminants 40,41

Formation of nitrosamine precursors, e.g. dimethylamine-derived species 21,42

Oxidative transformation of nitrogen-containing compounds 43,44

Activated carbon filtration

Removal of organic matter and disinfectants

Catalytic or surface-mediated reactions under certain conditions 45,18

Adsorption/desorption and surface-catalysed transformations 18,46

Ion exchange resins

Removal of ionic impurities 47,48

Release of amine-containing compounds upon degradation 1,18

Decomposition of quaternary ammonium functional groups 1,18

Reverse osmosis / nanofiltration

Removal of dissolved impurities 49,50

Indirect risk via membrane fouling or microbial activity 51,52

Precursor accumulation 53,51

Distillation

Removal of non-volatile impurities 54,55

Minimal intrinsic risk; possible post-treatment contamination 12

Reintroduction via storage/distribution systems 56,17


Table 2. Regulatory perspective on nitrite in water and its relevance to nitrosamine risk

Water type

Regulatory framework

Nitrite limit

Regulatory interpretation

Nitrosamine risk perspective

Potable water

World Health Organization; European Drinking Water Directive

WHO approx. 3 mg/L; EU approx. 0.5 mg/L 57

Nitrite is a controlled impurity

Major upstream source of nitrosating agents

Purified water (PW)

United States Pharmacopeia; European Pharmacopoeia

Not specified

Controlled indirectly 58,59

Trace nitrite possible; risk-based monitoring required

Distilled water

United States Pharmacopeia

Not specified

High purity expected

Low intrinsic risk; depends on storage/system

Water for injection (WFI)

United States Pharmacopeia; European Pharmacopoeia; FDA

Not specified

Stringent microbiological/endotoxin control

Very low nitrite expected; still relevant with amines

Sterile water for injection (SWFI)

United States Pharmacopeia

Not specified

Sterile packaged WFI

Minimal intrinsic risk


Nitrite as a critical determinant


Nitrite is among the most critical determinants of N-nitrosamine formation because it acts almost directly as a precursor to reactive nitrosating species23. Protonation to nitrous acid and equilibrium with N2O3 enable conversion of secondary amines to N-nitrosamines, so that even small amounts contribute materially to the impurity burden15,12,24. Reactivity is governed chiefly by pH5: moderate pH (3-4) maximises nitrosation, but chloramine-mediated and aldehyde-assisted routes allow formation near neutrality, revealing the limits of pH control alone25,8. Critically, trace nitrite produces quantifiable impurities; reactions with susceptible amines yield detectable nitrosamines at sub-ppm and even ppb levels24,26, and multiple low-level sources - water, excipients and degradation products - act cumulatively12. In solid dosage forms, moisture- and pH-variable microenvironments create local conditions favouring nitrosation despite low bulk nitrite11.


Nitrite enters pharmaceutical systems from water, excipients, active substances and environmental contamination; excipient nitrite content is a recognised, variable source25,1. Processing amplifies its effect: higher temperature accelerates kinetics14, prolonged processing or storage allows reactions to proceed, and recycled process water can accumulate nitrite12. Despite growing recognition in risk assessments7,13, neither the United States Pharmacopeia nor the European Pharmacopoeia defines a nitrite limit for pharmaceutical water12. Effective control of nitrite at every stage is therefore essential to minimise N-nitrosamine risk24.



Analytical determination of nitrosamines and nitrite


The genotoxicity and very low acceptable-intake limits of nitrosamines demand highly sensitive, selective methods, often at parts-per-billion or parts-per-trillion levels27,28. Gas chromatography-mass spectrometry (GC-MS) is widely used for volatile nitrosamines such as NDMA and offers high sensitivity for low-molecular-weight analytes, though thermal degradation at high injector temperatures can cause artefacts29. Liquid chromatography-tandem mass spectrometry (LC-MS/MS) is preferred for complex pharmaceutical matrices, operating under milder conditions, reducing thermal degradation and resolving diverse nitrosamines including N-nitrosamine drug substance-related impurities (NDSRIs)12,28; multiple reaction monitoring improves specificity and enables ultra-trace quantification. High-resolution mass spectrometry (HRMS) adds accurate-mass selectivity useful for screening novel nitrosamines and NDSRIs that targeted methods may miss30,31,32.


Sample preparation is decisive: solid-phase extraction, liquid-liquid extraction and headspace analysis improve sensitivity and reduce matrix effects29. Assessment of precursors - especially nitrite - is increasingly recognised as essential for pre-emptive risk management; ion chromatography and LC-based methods detect nitrite at trace levels13. Method validation for accuracy, precision, linearity, limit of detection (LOD) and limit of quantification (LOQ) is mandatory, and the diversity of nitrosamines drives multi-analyte and combined targeted/non-targeted strategies that detect known impurities while flagging new ones30.


Mitigation strategies and regulatory considerations


Controlling nitrosamines requires a risk-based strategy that limits reactants and slows reactions through process design25. Because even low nitrite triggers nitrosation with susceptible amines7,25, water-quality management is central: pharmaceutical water systems should be designed and operated to minimise nitrite generation and accumulation, with ongoing monitoring of nitrite, nitrate and residual disinfectants14,9. Raw-material control is equally important, since excipients and actives may carry nitrite or amine impurities; vendor qualification, material characterisation and impurity assessment help prevent precursor ingress25,8. Process optimisation - controlling pH, temperature and residence time, avoiding acidic conditions where feasible, and segregating nitrosating agents from amines - reduces formation14. Nitrite scavengers and inhibitors offer an effective option where nitrite cannot be eliminated, subject to compatibility and safety evaluation. Because formation can continue in situ and on storage, lifecycle assessment and stability studies under relevant temperature and humidity are essential.


Global regulators, including the US Food and Drug Administration and the European Medicines Agency, expect documented risk assessments, source identification, mitigation and validated trace-level methods27,11,33, consistent with ICH M7 principles for the assessment and control of mutagenic impurities34. Regulatory guidance emphasises precursor control, yet the absence of pharmacopoeial nitrite limits for pharmaceutical water remains a significant gap that targeted monitoring and risk-based control must bridge. Major mitigation strategies are summarised in Table 3.


Table 3. Mitigation strategies for nitrosamine risk control.

Strategy

Approach

Impact on nitrosamine risk

Water purification

RO, distillation, activated carbon

Removes nitrite and precursors

Nitrite monitoring

Routine analytical testing

Early detection and control

Raw material control

Excipient/API screening

Prevents precursor introduction

Process optimisation

pH and temperature control

Reduces nitrosation kinetics

Segregation of processes

Separate amines and nitrosating agents

Minimises interaction

Nitrite scavengers

Ascorbic acid, antioxidants

Inhibits nitrosation reactions

In-line monitoring

Real-time detection systems

Immediate corrective action

Equipment cleaning

Cross-contamination prevention

Reduces precursor carryover

Storage control

Control humidity and temperature

Prevents delayed formation

Figure 1. Nitrite-driven N-nitrosamine formation in pharmaceutical systems: water-mediated mechanisms, risk assessment and control strategies
Figure 1. Nitrite-driven N-nitrosamine formation in pharmaceutical systems: water-mediated mechanisms, risk assessment and control strategies

Challenges and future perspectives


Several scientific and regulatory challenges persist. Formation under realistic, complex conditions is incompletely understood: alternative chloramine-mediated and oxidative pathways can operate near neutrality and depend strongly on water composition, precursor concentration and process conditions, complicating prediction25,9. The lack of a defined nitrite limit for pharmaceutical water, together with variability from source water, treatment and system design, leaves risk assessment uncertain for amine-containing products7,10,1. Analytical challenges remain around confident ultra-trace detection, matrix interference, robustness and inter-laboratory variability, and the need for simultaneous determination of multiple nitrosamines and precursors30,12. In-product formation during storage - driven by residual nitrite, moisture and microenvironmental pH - further complicates predictive modelling and demands long-term stability evaluation. Water treatment's dual role as remover and potential generator of precursors, including material degradation that releases amines, requires deeper mechanistic understanding.


Looking ahead, predictive modelling that integrates chemical kinetics, water chemistry, process parameters and analytics - supported by in silico approaches - could identify high-risk cases and guide intervention16. Lower-leachable polymers and advanced adsorbents may reduce precursor introduction, while scientifically justified nitrite limits for pharmaceutical water and harmonised global expectations would strengthen risk management7. Real-time monitoring and process analytical technology could enable dynamic control during manufacture. Progress will require integrating mechanistic insight, modern analytics and regulatory harmonisation across disciplines.



Conclusion


Nitrosamine impurities are a complex, evolving challenge shaped by chemical reactivity, material variability and process conditions. Nitrite has emerged as a central determinant, particularly in aqueous environments where it readily generates reactive nitrosating species, and water functions as a dynamic medium that transports and transforms precursors rather than a mere solvent. Even trace nitrite from water, excipients or degradation can yield measurable nitrosamines under favourable conditions, and pH, temperature, moisture, treatment processes and system design all add complexity. The absence of explicit nitrite limits in pharmaceutical water specifications is a critical regulatory gap. Analytical advances have improved detection, but consistent ultra-trace quantification across complex matrices remains difficult. Effective mitigation requires an integrated, lifecycle approach combining water-quality control, raw-material management, process optimisation and real-time monitoring, with targeted control of nitrite across all sources. Predictive models, advanced analytics and harmonised, scientifically justified limits will be pivotal in strengthening nitrosamine risk management and ensuring the safety, quality and compliance of pharmaceutical products.


Abbreviations

NDMA - N-nitrosodimethylamine

N2O3 - dinitrogen trioxide

HNO2 - nitrous acid

GC-MS - gas chromatography-mass spectrometry

LC-MS - liquid chromatography-mass spectrometry

LC-MS/MS - liquid chromatography-tandem mass spectrometry

HRMS - high-resolution mass spectrometry

MRM - multiple reaction monitoring

SPE - solid-phase extraction

LLE - liquid-liquid extraction

IC - ion chromatography

LOD - limit of detection

LOQ - limit of quantification

NDSRI - N-nitrosamine drug substance-related impurity

IPEC - International Pharmaceutical Excipients Council

WHO - World Health Organization

FDA - US Food and Drug Administration

EMA - European Medicines Agency

RO - reverse osmosis


Funding: This research received no external funding.

Conflict of interest: The authors declare no conflict of interest.

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Authors

Santosh Bhende, Atul Phatak, Pravin Chaudhari


Corresponding Author: Santosh Bhende

Department of Pharmaceutics, PES's Modern College of Pharmacy,

Nigdi, Savitribai Phule Pune University, Pune, Maharashtra, India.

                                                                                

                                           Email:   info@pesmcopnigdi.edu.in     

                                          Telephone:  +91 7575801816



Authors and positions

Santosh Bhende (corresponding author) - [Research Scholar, Pharmaceutics]

Atul Phatak - [Head of Dept., Pharmaceutics]

Pravin Chaudhari - [Head of Research Centre]

Department of Pharmaceutics, PES's Modern College of Pharmacy, Nigdi, Savitribai Phule Pune University, Pune, Maharashtra, India.



 
 
 

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