Abstract

Groundwater from the Triassic Sherwood Sandstone aquifer of the English East Midlands shows a well-documented evolution in chemistry and residence time as it flows downgradient from shallow unconfined conditions to greater depths, confined by Mercia Mudstone. The flow path covers a lateral distance of some 40 km and depths approaching 800 m. The presence of fresh groundwater (Cl = 15 mg/L, Na = 17 mg/L, SO4 = 144 mg/L, TDS = 500 mg/L) of likely Pleistocene age can be demonstrated down to about 500 m depth in the aquifer, some 10 km downgradient of its confined/unconfined interface. This is amongst the deepest fresh groundwater identified in the UK. Beyond that zone, salinity increases in response to dissolution of gypsum or anhydrite, giving Ca-SO4 groundwater. Further downgradient still, saline groundwater (TDS = 10 g/L) is encountered in the deepest part of the confined aquifer. Downgradient geochemical evolution and increasing residence time are also observed in the South Yorkshire section of the aquifer, to the north of the East Midlands flow path. Here, analogous sequential geochemical changes are observed, controlled by carbonate and sulphate mineral reactions, redox changes and silicate hydrolysis, with evidence of increased inputs of e.g. Na, Cl and SO4 from modern pollution at shallow depths in the unconfined aquifer. Redox conditions are more variable in the western part of the South Yorkshire aquifer, due to local confinement or semi-confinement by fine-grained Quaternary deposits overlying the Sherwood Sandstone. Ratios of δ13C in this section of aquifer increase from −14‰ at outcrop to −11‰ in Mercia-Mudstone-confined conditions as a result of gradual equilibration with aquifer carbonate under closed-system conditions. Ratios of δ18O and δ2H become more depleted, reaching −9‰ and −61‰ respectively, suggesting recharge under climatic conditions significantly cooler than the modern era. Increasing residence time is also indicated by increasing concentrations of a number of trace elements (e.g. Li, Rb, Sr, Mo). These transitions are also observed vertically within investigated boreholes in unconfined and semi-confined sections of the aquifer. Deep groundwater (160–170 m depth) from a borehole within the unconfined aquifer of South Yorkshire has δ18O and δ2H ratios as depleted as −9.2‰ and −67‰ respectively. Such depth stratification indicates that good-quality palaeowater, likely of Pleistocene age, can exist at depth even in the unconfined Sherwood Sandstone aquifer, and that vertical hydraulic conductivity is much lower than lateral. A paucity of boreholes in the Mercia-Mudstone-confined section of the South Yorkshire aquifer makes estimation of the lateral extent of fresh groundwater there more problematic, though brackish groundwater (Cl = 1300 mg/L, TDS = 5.5 g/L) has been identified 12 km east of the aquifer's confined margin.

Highlights

  • Research on regional groundwater resources and quality in the UK has often focussed on shallow aquifer systems, because of greater access and use, and greater potential vulnerability to contamination from surface activities

  • This paper extends the area of aquifer investigation further north into South Yorkshire (Doncaster area), to an area which has received comparatively little attention

  • South Yorkshire groundwater confined below Mercia Mudstone Group (MMG) is distinguished

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Summary

Introduction

Research on regional groundwater resources and quality in the UK has often focussed on shallow aquifer systems (less than around 100 m depth), because of greater access and use, and greater potential vulnerability to contamination from surface activities. Understanding of groundwater quality and groundwater residence times in deeper aquifers is important for establishing groundwater flow paths, rates and potential pollutant pathways and for determining the three-dimensional extent of groundwater bodies that require protection in accordance with European legislation. The East Midlands section of the aquifer is well-documented in terms of groundwater quality and age estimation (e.g. Andrews et al, 1984; Andrews and Lee, 1979; Bath et al, 1979; Bath et al, 1987; Edmunds et al, 1982; Edmunds and Smedley, 2000). It has a recognised flow path that spans some 40 km laterally and extends in depth to around 800 m below ground level (Edmunds and Smedley, 2000), albeit with saline groundwater in the deepest parts of the aquifer at its easterly onshore extent. This paper outlines key regional and depth variations in water chemistry in the aquifer, along with likely controlling processes and residence times estimated from stable isotopes and diagnostic trace elements. The study summarises the hydrogeochemical data available to estimate the regional extent of the fresh groundwater body and the constraints on its distribution

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