Abstract

The study was conducted at two sites in Sondu-Miriu basin between November 2010 and May 2011, using runoff plots to determine the temporal variation of sediments, organic matter, solids and surface runoff from agricultural land uses. At Kabianga, lower sediment and surface runoff values were observed in natural vegetation while runoff was generally higher in April-May 2011 wet season. While there were significantly lower sediment concentrations and higher runoff volumes, organic content was significantly lower in April-May 2011. Principal Components Analysis correlated surface runoff and erosion to seasonal land use activities particularly during wet seasons depicting the influence of hydrology on surface runoff pollution. In Sondu, sediment concentrations were lower in natural vegetation. Surface runoff was higher in January-March 2011 in natural vegetation but lowest in cropped systems during April-May, 2011. Solids and organic matter were significantly higher in November-December 2011 (p<0.05). PCA linked surface runoff quality to changes in hydrological periods which influenced the nature, quality and quantity of material transported via surface runoff. PCA for River Sondu-Miriu at Kabianga suggested ionic pollution by dissolved substances (r = 0.77-0.99, p<0.01) and sediment load introduced via surface runoff during wet seasons. In Sondu, PCA associated ionic pollutants and sediment loads to hydrological changes relating to seasonality (r = -0.75-0.99, p<0.01). Temporal variations in surface runoff volumes, water quality and sediment load correlated significantly to hydroperiods in Sondu-Miriu basin. Hydrological changes impacted highly in agricultural land uses with reduced land cover which increased surface runoff accompanied by higher sediment loads.

Highlights

  • There is increasing awareness of the need to protect natural resources in order to meet present and future requirements

  • To gravimetrically determine the Organic Matter (OM) content in the samples, oven-dried and weighed Total Suspended Solids (TSS) residue in the filters were ignited to a constant weight in a muffle furnace at 500-550°C for 1-2 h after which the AshFree Dry Weight (AFDW) was measured

  • Total Solids (TS) was estimated by evaporating duplicates of a well-mixed 50 mL sample in a weighed dish and drying to a constant weight in an oven at 103-105°C

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Summary

Introduction

There is increasing awareness of the need to protect natural resources in order to meet present and future requirements. Excessive or enhanced soil erosion due to poor land management can result in both on and off-site impacts detrimental to a wide range of receptors. The soil resource can be severely depleted when the rate of erosion exceeds that of natural soil formation. This loss often corresponds to the most agriculturally important topsoil and any fertilizer or pesticide application, causing subsequent reductions in agricultural productivity. Soil erosion is a hazard traditionally associated with agriculture and often occurs in tropical and semi-arid areas (Collins and Owens, 2006)

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