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Determination of iopromide in environmental waters by ion chromatography-ICP-MS

Applications | 2012 | Agilent TechnologiesInstrumentation
ICP/MS
Industries
Environmental
Manufacturer
Agilent Technologies

Summary

Importance of Topic


The widespread use of the iodinated contrast medium iopromide in medical imaging has led to its persistence and detection in surface waters and wastewater. Its hydrophilic and nonionic nature prevents efficient removal by conventional treatment processes, making accurate monitoring essential. Moreover, during disinfection, iodinated compounds can form toxic byproducts at levels of regulatory concern, underscoring the need for reliable trace analysis.

Objectives and Overview


This study aimed to develop and validate a sensitive, robust method for quantifying sub-ppb levels of iopromide in environmental waters. By coupling ion chromatography (IC) with inductively coupled plasma mass spectrometry (ICP-MS), the work seeks to establish method detection limits, demonstrate long-term stability under high-matrix conditions, and apply the approach to real river and wastewater samples.

Methodology and Instrumentation


Environmental water samples were collected from rivers and effluents in California and prefiltered. Automated solid-phase extraction (SPE) with hydrophilic-lipophilic balance cartridges concentrated analytes from 1 L of sample. Elution used methanol and methanol/MTBE solvents, followed by evaporation and reconstitution. Chromatographic separation employed a Dionex AG16 guard column and AS16 analytical column with a NaOH gradient (2–90 mM) at 1 mL/min and 500 μL injection volume. ICP-MS detection used an Agilent 7700x with High Matrix Introduction (HMI) interface and helium collision cell to reduce polyatomic interferences on iodine (m/z 127).

Main Results and Discussion


The method achieved a lower method reporting limit of 0.1 ppb in extracts (≈2 ppt in water samples) with linear calibration over four orders of magnitude (0.1–1000 ppb). Continuous 24 h operation showed stable recoveries within 10% of expected values. Real samples contained iopromide from low ppt to hundreds of ppb, confirming environmental prevalence. Additionally, several unknown iodinated peaks were observed; compound-independent calibration based on iodine response allowed quantification of these species as iodine equivalents, revealing potential novel contaminants.

Benefits and Practical Applications


  • Sensitive detection of trace iopromide and other iodinated species.
  • Robust long-term operation with nonvolatile eluents via HMI interface.
  • Effective interference removal using helium collision mode.
  • Capability to quantify unknown iodinated compounds through compound-independent calibration.
  • Applicability to environmental monitoring, wastewater impact assessment, and disinfection byproduct studies.

Future Trends and Opportunities


Advances may include high-resolution mass spectrometry for structural identification of unknown iodinated compounds, integration of online SPE for higher throughput, expansion to other iodinated pharmaceuticals, and routine monitoring of iodinated disinfection byproducts. Regulatory interest in I-DBPs may drive method standardization and wider adoption in environmental laboratories.

Conclusion


The coupling of ion chromatography with ICP-MS using an HMI interface and collision cell delivers a highly sensitive, reproducible protocol for quantifying iopromide in environmental waters. With low detection limits, extended runtime, and the ability to detect unknown iodinated species, this method offers a valuable tool for environmental monitoring and risk assessment.

Reference


  • Steger-Hartmann T et al. Investigations into the environmental fate and effects of iopromide. Water Research 2002, 36(1):266–274.
  • Ternes TA and Hirsch R. Occurrence and behavior of x-ray contrast media in sewage facilities and the aquatic environment. Environmental Science & Technology 2000, 34(13):2741–2748.
  • Carballa M et al. Behavior of pharmaceuticals, cosmetics and hormones in a sewage treatment plant. Water Research 2004, 38(12):2918–2926.
  • Kormos JL, Schulz M and Ternes TA. Occurrence of iodinated x-ray contrast media and their biotransformation products in the urban water cycle. Environmental Science & Technology 2011, 45(20):8723–8732.
  • Drewes JE, Fox P and Jekel M. Occurrence of iodinated x-ray contrast media in domestic effluents and their fate during indirect potable reuse. Journal of Environmental Science and Health Part A 2001, 36(9):1633–1645.
  • Drewes JE et al. Fate of pharmaceuticals during ground water recharge. Ground Water Monitoring & Remediation 2003, 23(3):64–72.
  • Snyder SA et al. Role of membranes and activated carbon in the removal of endocrine disruptors and pharmaceuticals. Desalination 2007, 202(1–3):156–181.
  • Dickenson ERV et al. Indicator compounds for assessment of wastewater effluent contributions to flow and water quality. Water Research 2011, 45(3):1199–1212.
  • Duirk SE et al. Formation of toxic iodinated disinfection byproducts from compounds used in medical imaging. Environmental Science & Technology 2011, 45(16):6845–6854.
  • Schulz M et al. Transformation of the x-ray contrast medium iopromide in soil and wastewater treatment. Environmental Science & Technology 2008, 42(19):7207–7217.
  • Richardson SD et al. Occurrence and mammalian cell toxicity of iodinated disinfection byproducts in drinking water. Environmental Science & Technology 2008, 42(22):8330–8338.
  • Richardson SD et al. Occurrence, genotoxicity, and carcinogenicity of regulated and emerging disinfection byproducts. Mutation Research Reviews in Mutation Research 2007, 636(1–3):178–242.
  • Smith EM et al. Comparison of byproduct formation in waters treated with chlorine and iodine. Environmental Science & Technology 2010, 44(22):8446–8452.
  • Putschew A, Schittko S and Jekel M. Quantification of triiodinated benzene derivatives by LC-ESI-MS/MS. Journal of Chromatography A 2001, 930(1–2):127–134.
  • Hirsch R et al. A sensitive method for the determination of iodine containing diagnostic agents using LC-ESI-MS/MS. Fresenius Journal of Analytical Chemistry 2000, 366(8):835–841.
  • Ternes TA. Analytical methods for the determination of pharmaceuticals in aqueous environmental samples. Trends in Analytical Chemistry 2001, 20(8):419–434.
  • Vanderford BJ et al. Assessment of sample preservation for pharmaceuticals, personal care products, and steroids in water. Analytical and Bioanalytical Chemistry 2011, 399(6):2227–2234.

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