Strontium-90 (90 Sr) is the major long-lived radionuclide derived from the chernobyl accident, and is still being detected in the heavily contaminated catchments of the chernobyl exclusion Zone. this study examines the long-term decrease in the dissolved-phase 90 Sr concentration and the concentrationdischarge (90 Sr-Q) relationship in stream water since the accident. We show that the slow decline in 90 Sr follows a double-exponential function, and that there is a clear relationship between 90 Sr and Q. This study is the first to reveal that the log(90 Sr)-log(Q) slope has been gradually decreasing since the accident. this trend persists after decay correction. thus, it is not caused by the physical decay of 90 Sr and environmental diffusion, but implies that the concentration formation processes in stream water have been changing over a long period. We propose a hydrochemical model to explain the timedependency of the 90 Sr-Q relationship. this paper presents a mathematical implementation of the new concept and describes the model assumptions. our model accurately represents both the long-term 90 Sr trend in stream water and the time-dependency of the 90 Sr-Q relationship. Although this paper considers a small catchment in chernobyl, the conceptual model is shown to be applicable to other accidental releases of radionuclides. It has been 34 years since the Chernobyl nuclear power plant (CNPP) accident in Ukraine (Fig. 1), when large amounts of radionuclides were released into the environment. At present, high levels of dissolved-phase strontium-90 (90 Sr) are still being detected in the small catchment streams inside the Chernobyl Exclusion Zone (CEZ) (Fig. 2b). The main long-term source of exchangeable and available 90 Sr in the CEZ soils is micron-sized "fuel particles" (FP) that are gradually dissolving. These are derived from the accidental release from CNPP Unit 4 on 26 April, 1986, and were formed by the mechanical destruction of nuclear fuel. The dissolution rate of FP in CEZ soils varies from several percent to several tens of percent of the activity inventory per year, depending on the degree of oxidation of the particle UO 2 matrix and the ambient geochemical conditions (e.g. soil solution pH and oxygen availability) 1-6. The 90 Sr from small streams in the CEZ is discharged into the main Pripyat river, which is a critical component of the Dnieper river-reservoir system, one of the largest surface water systems in Europe 7. Through this river system, 90 Sr is also transported to the Kiev metropolitan area in Ukraine. Therefore, predicting and evaluating the radionuclide flux within the water system, and using models to evaluate the potential radiological consequences to the downstream population, remain important tasks.