Abstract

Models are necessary tools for watershed management. However, applying watershed models is time consuming and requires technical knowledge, including model selection and validation. The objective of this study is to assess two commonly used watershed models and their parameter sensitivity to reduce model loadings and to gain a better understanding of the model performances. The Hydrological Simulation Program-Fortran (HSPF) model and Storm Water Management Model (SWMM) were applied to a mostly forested Taiwanese reservoir watershed with pollution from tea plantations. Statistical analysis showed that both models are suitable for the studied watershed, but the performances of the flow and water quality simulations are different. The mean flow simulated by SWMM was lower than the experimental observations. The HSPF model performed better, possibly because the soil in the study area is highly permeable and the HSPF model has more precise soil layer calculations. SWMM may underestimate the total phosphorous (TP) and suspended solid (SS) loads following small storm events in highly permeable watersheds. The Latin Hypercube-One factor At a Time (LH-OAT) method was used to determine the parameter sensitivity of the HSPF model and SWMM. In both of the models, the parameters related to infiltration and soil characteristics strongly affected the flow simulation, except when using the Horton infiltration method in the SWMM. Manning’s roughness coefficient for pervious areas was more sensitive in SWMM than in the HSPF model because SWMM has fewer parameters.

Highlights

  • Nonpoint source (NPS) pollution occurs when storm runoff carries pollutants accumulated on surfaces to receiving water bodies

  • We evaluated 15 hydrology parameters for the Hydrological Simulation Program-Fortran (HSPF) model and 6 parameters for Storm Water Management Model (SWMM); each parameter was divided into 20 intervals for the Latin Hypercube-One factor At a Time (LH-OAT) method

  • [15,22]: The observed flow data included continuous daily flow measurements, and the observed water quality data consisted of monthlyOmonitoring

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Summary

Introduction

Nonpoint source (NPS) pollution occurs when storm runoff carries pollutants accumulated on surfaces to receiving water bodies. When sediment and nutrients in runoff accumulate in deep water bodies, such as reservoirs and lakes, eutrophication can occur. NPS pollution control is important for reservoir and lake watershed management. Without a sufficient number of samples, it is impossible to determine the effects of NPS pollution on the water quality of a receiving water body. Additional measures are required to assess the generation and distribution of NPS pollution, such as the use of NPS models [1]. Many watershed models can simulate hydrology and water quality, but their underlying calculations differ. It is unrealistic to test all of the possible candidate models for one case

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