Abstract

This paper proposes a novel deterministic methodology for estimating the optimal sampling frequency (SF) of water quality monitoring systems. The proposed methodology is based on employing two-dimensional contaminant transport simulation models to determine the minimum SF, taking into consideration all the potential changes in the boundary conditions of a water body. Two-dimensional contaminant transport simulation models (RMA4) were implemented to estimate the distribution patterns of some effective physiochemical parameters within the Al-Hammar Marsh in the southern part of Iraq for 30 cases of potential boundary conditions. Using geographical information system (GIS) tools, a spatiotemporal analysis approach was applied to the results of the RMA4 models to determine the minimum SF of the monitoring stations with a monitoring accuracy (MA) level of detectable change in contaminant concentration ranging from the standard level to 50% (stepwise 5%). For the study area, the proposed methodology specified a minimum and maximum SF for each monitoring station (MS) that ranged between 12 and 33 times per year, respectively. An exponential relationship between SF and MA was obtained. This relationship shows that increasing the MA to ±10%, ±25%, and ±50% increases the SF by approximately 14%, 28%, and 93%, respectively. However, the proposed methodology includes all the potential values and cases of flow and contaminant transport boundary conditions, which increases the certainty of monitoring the system and the efficiency of the SF schedule. Moreover, the proposed methodology can be effectively applied to all types of surface water resources.

Highlights

  • Water pollution is a growing menace to natural ecosystems and human life

  • This paper aims to present a new deterministic approach for employing the features and facilities of the hydrodynamic simulation models of contaminants transport to specify the optimal sampling frequency (SF) for each

  • The verification process was performed to evaluate the certainty of using the roughness–depth relationship of the marsh bed given by Manning’s roughness coefficient (Figure 3), which was recommended by Alhamdani [34], and the accuracy of the implemented RMA2 model of the marsh

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Summary

Introduction

The distribution of pollution within a water resource system is characterized by significant spatial and temporal variations due to differences in hydrological conditions and pollution sources. Overcoming this challenge requires a better understanding of the spatial and temporal variations in the distribution of contaminants within aquatic systems [1]. Obtaining the optimal design of water quality monitoring networks (WQMNs) is a very complex process due to the large number of factors that must be considered, such as monitoring objectives, water quality parameters, monitoring station locations, and sampling frequency (SF) [2]. The optimal design of a WQMN, taking into consideration the SF and all issues related to the improvement of monitoring program efficiency, Hydrology 2019, 6, 94; doi:10.3390/hydrology6040094 www.mdpi.com/journal/hydrology

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