Abstract
AbstractViruses and bacteria which are characterized by finite lives in the subsurface are rapidly transported via fractures and cavities in fractured and karst aquifers. Here, we demonstrate how the coupling of a robust outcrop characterization and hydrogeophysical borehole testing is essential for prediction of contaminant velocities and hence wellhead protection areas. To show this, we use the dolostones of the Permian Magnesian Limestone aquifer in NE England, where we incorporated such information in a groundwater flow and particle tracking model. Within this aquifer, flow in relatively narrow (mechanical aperture of ~ 10−1–1 mm) fractures is coupled with that in pipe cavities (~ 0.20-m diameter) following normal faults. Karstic cavities and narrow fractures are hydraulically very different. Thus, the solutional features are represented within the model by a pipe network (which accounts for turbulence) embedded within an equivalent porous medium representing Darcian flowing fractures. Incorporation of fault conduits in a groundwater model shows that they strongly influence particle tracking results. Despite this, away from faulted areas, the effective flow porosity of the equivalent porous medium remains a crucial parameter. Here, we recommend as most appropriate a relatively low value of effective porosity (of 2.8 × 10−4) based on borehole hydrogeophysical testing. This contrasts with earlier studies using particle tracking analyses on analogous carbonate aquifers, which used much higher values of effective porosity, typically ~ 102 times higher than our value, resulting in highly non-conservative estimates of aquifer vulnerability. Low values of effective flow porosities yield modelled flow velocities ranging from ~ 100 up to ~ 500 m/day in un-faulted areas. However, the high fracturing density and presence of karstic cavities yield modelled flow velocities up to ~ 9000 m/day in fault zones. The combination of such flow velocities along particle traces results in 400-day particle traces up to 8-km length, implying the need for large well protection areas and high aquifer vulnerability to slowly degrading contaminants.
Funder
Natural Environment Research Council
Publisher
Springer Science and Business Media LLC
Subject
Health, Toxicology and Mutagenesis,Pollution,Environmental Chemistry,General Medicine
Reference107 articles.
1. Abesser C, Lewis M (2015) A semi-quantitative technique for mapping potential aquifer productivity on the national scale: example of England and Wales (UK). Hydrogeol J 23(8):1677–1694
2. Aldrick RJ (1978) The hydrogeology of the Magnesian Limestones in Yorkshire between the River Wharfe and the River Aire. Quart J Engineer Geol Hydrogeol 11(2):193–201
3. Allen DJ, Brewerton LM, Coleby BR, Gibbs MA, Lewis A, MacDonald SJ, Wagstaff AT, Williams LJ (1997) The physical properties of major aquifers in England and Wales. Technical Report WD/97/34, 157-287. British Geological Survey, Nottingham, England (UK)
4. Allen DJ, Bloomfield JP, Gibbs BR, Wagstaff SJ, (1998) Fracturing and the hydrogeology of the Permo-Triassic sandstones in England and Wales. Technical Report 97/34, 1-89. BGS, Nottingham, Engalnd (UK)
5. Allimendinger RW, Cardozo N, Fisher D (2012) Structural geology algorithms: vectors and tensors. Cambridge University Press, Cambridge
Cited by
29 articles.
订阅此论文施引文献
订阅此论文施引文献,注册后可以免费订阅5篇论文的施引文献,订阅后可以查看论文全部施引文献