Related Experiment Video
Updated: Jan 8, 2026

A General Method for Detecting Nitrosamide Formation in the In Vitro Metabolism of Nitrosamines by Cytochrome P450s
Published on: September 25, 2017
Occurrence, formation, and treatment implications of N-Nitrosamine risks in harvested waters
Mingizem Gashaw Seid1, Aseom Son1, Wondesen Workneh Ejerssa2
1Center for Water Cycle Research, Korea Institute of Science and Technology, Seoul 02792, Republic of Korea.
Abstract:
With growing freshwater scarcity, alternative sources such as harvested rainwater, atmospheric water, and stormwater are attracting increasing attention. However, their use may pose health risks due to contamination and the formation of carcinogenic N-Nitrosamines. This study systematically evaluated the occurrence and formation potentials (FPs) of nine N-Nitrosamines detected in harvested waters. Five N-Nitrosamines-N-Nitrosodimethylamine, N-Nitrosodiethylamine, N-Nitrosomorpholine, N-Nitrosopyrrolidine, and N-Nitrosodibutylamine-were consistently detected (2.2-23.1 ng L⁻¹) or formed during chloramination at concentrations ranging from 3.7 to 40 ng L⁻¹ , while N-Nitrosomethylethylamine, N-Nitrosodipropylamine, and N-Nitrosodiphenylamine were detected exclusively in stormwater samples. N-Nitrosopiperidine appeared only sporadically at low levels in rainwater. Spatiotemporal variability was most pronounced in stormwater, where first-flush events caused sharp increases. Correlation analysis indicated that N-Nitrosamine-FPs were strongly influenced by metals and bromide, and were closely associated with secondary amines and hydrophilic dissolved organic nitrogen fractions. Estimated lifetime cancer risks from chloraminated waters (2.69 × 10⁻⁵ to 1.08 × 10⁻⁴) exceeded the USEPA negligible risk level of 1.0 × 10⁻⁶ by 27-370 times. Pretreatment strategies prior to chloramination showed contrasting performances. Sand filtration achieved little removal, while Mn(VII) and UV/NH2Cl sometimes increased N-Nitrosamine-FPs. In contrast, UV/HOCl achieved up to 90 % reduction under environmentally relevant conditions (oxidant dose ≤ 4 mg L⁻¹, UV fluence > 700 mJ cm⁻²), outperforming UV/H2O2, Fe(VI), and powdered activated carbon. Overall, harvested waters represent a significant N-Nitrosamine risk, but effective pretreatments can substantially mitigate formation. These findings highlight the need for integrated treatment and disinfection strategies to ensure safe water harvesting and reuse.
Related Concept Videos
2° Amines to N-Nitrosamines: Reaction with NaNO2
Physical Properties of Amines
Types of Toxins
Air pollutants, primarily gases, pose significant threats to respiratory health, leading to conditions like hypoxia, lung cancer, and in extreme cases, death.
Environmental pollutants like...
1° Amines to Diazonium or Aryldiazonium Salts: Diazotization with NaNO2 Overview
The nitrous acid is unstable. Hence, it is formed in situ from a solution of sodium nitrite and cold aqueous acids such as hydrochloric or sulfuric acid. In an acidic solution, the –OH group of nitrous acid undergoes protonation to give oxonium ion, followed by...
Comparative Excretory Systems
Inorganic Nitrogen Assimilation

