A wastewater treatment plant may substantially reduce a methamphetamine concentration while still releasing measurable residues. A 2025 Iranian study provides a practical example of why “removal,” “destruction” and “not detected” should remain separate terms.
What did investigators collect?
Asadi and colleagues sampled influent and effluent at three wastewater treatment plants serving Kermanshah, Hamadan and Sanandaj. Collections covered cold and warm seasons, with three sampling occasions in one week during each seasonal period. Wastewater samples were 12-hour composites, built from aliquots every 15 minutes. Receiving-river samples were grab samples.
Solid-phase extraction and liquid chromatography–tandem mass spectrometry measured specific drugs and metabolites. These were environmental water specimens, not human blood or urine. River grabs also have different temporal coverage from the composite wastewater samples.
How was removal calculated?
The study calculated removal as 100 multiplied by the difference between mean influent and mean effluent concentration, divided by mean influent concentration. It was therefore a concentration-based comparison in ng/L.
For example, cold-season methamphetamine means at Sanandaj were 129 ± 100 ng/L in influent and 3.4 ± 2.7 ng/L in effluent, reported as mean ± standard deviation. Those means correspond to an approximately 97.4% decrease. The effluent still contained measured methamphetamine. A large percentage decrease and a positive effluent result can both be correct.
In the warm season at the same plant, the corresponding means were 50.9 ± 66.2 and 29.2 ± 35.6 ng/L, an approximately 42.6% decrease calculated from the reported means. The large variability and limited sampling make a single universal treatment-performance percentage inappropriate.
What does an effluent result below detection establish?
Cold-season methamphetamine at Hamadan was reported below the detection limit in effluent, with a mean influent concentration of 98.7 ± 136 ng/L. Below detection is not a measured concentration of zero. A calculated removal approaching 100% depends in part on how censored concentrations are handled.
The paper reports analytical detection and quantitation limits across the assay panel, but those limits should not be treated as ecological safety thresholds. Demonstrating that an instrument cannot detect the parent drug at its reporting limit is a different task from demonstrating no biologically relevant residual exposure.
Did the experiment establish complete chemical destruction?
No. A decline in the dissolved parent-drug concentration can reflect degradation, transformation, partitioning or other processes. The concentration equation alone is not a complete mass balance across water, solids and transformation products. This study did not establish mineralization of every removed methamphetamine molecule.
Operational conditions also mattered. The authors excluded cold-season Kermanshah results from their removal-efficiency presentation because that plant was not operating at steady state during repairs. That exclusion prevents treating every sampled plant-season as an equivalent test of routine performance.
Can river concentrations be assigned solely to the plant?
The study detected methamphetamine at selected river locations, including upstream locations. A downstream measurement is evidence of occurrence at that sampling point, but does not isolate the plant’s contribution from other inputs, dilution and transport. Repeated sampling and source-specific measurements would strengthen source attribution.
The findings justify examining treatment performance and environmental fate. They do not establish human impairment from environmental exposure, identify individual drug users or calculate a safe drinking-water concentration. This article’s percentage calculations describe the reported concentration means, not an independently validated treatment guarantee.
Source
Asadi A et al. Illicit drug use derived from wastewater-based epidemiology in Iran, their removal during wastewater treatment, and occurrence in receiving waters. Heliyon. 2025;11:e42516. doi:10.1016/j.heliyon.2025.e42516. Observational environmental sampling evidence.