A Combined Pumping Test and Heat Extraction/Recirculation Trial in an Abandoned Haematite Ore Mine Shaft, Egremont, Cumbria, UK
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Banks, David, Steven, Jonathan K., Berry, John, Burnside, Neil and Boyce, Adrian J. (2019) A combined pumping test and heat extraction/recirculation trial in an abandoned haematite ore mine shaft, Egremont, Cumbria, UK. Sustainable Water Resources Management, 5 (1). pp. 51-69. Downloaded from: http://insight.cumbria.ac.uk/id/eprint/5016/ Usage of any items from the University of Cumbria’s institutional repository ‘Insight’ must conform to the following fair usage guidelines. 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Alternatively contact the University of Cumbria Repository Editor by emailing [email protected]. Sustain. Water Resour. Manag. (2019) 5:51–69 DOI 10.1007/s40899-017-0165-9 ORIGINAL ARTICLE A combined pumping test and heat extraction/recirculation trial in an abandoned haematite ore mine shaft, Egremont, Cumbria, UK 1,2 3 4 2 David Banks • Jonathan K. Steven • John Berry • Neil Burnside • Adrian J. Boyce5 Received: 31 May 2016 / Accepted: 17 July 2017 / Published online: 8 August 2017 Ó The Author(s) 2017. This article is an open access publication Abstract A pumping test at rates of up to 50 L s-1 was potential hydraulic impacts on the overlying St Bees carried out in the 256 m-deep Florence Shaft of the Sandstone aquifer. The practice of recirculating thermally Beckermet–Winscales–Florence haematite ore mine in spent water in the Florence Shaft produced only a rather Cumbria, UK, between 8th January and 25th March 2015. modest additional thermal benefit. Drawdowns in mine water level did not exceed 4 m and the entire interconnected mine complex behaved as a single Keywords Haematite iron ore Á Heat pump Á Geothermal reservoir. Pumping did, however, induce drawdowns of energy Á Mine shaft Á Mine water Á Arsenic around 1 m in the St. Bees Sandstone aquifer overlying the Carboniferous Limestone host rock. During a second phase of the pumping test, a proportion of the 11.3–12 °C mine Introduction water was directed through a heat pump, which extracted up to 103 kW heat from the water and recirculated it back It is well established that heat (for space heating or cooling, to the top of the shaft. Provided that an issue with elevated domestic hot water, or industrial processes) can be extracted arsenic concentrations (20–30 lgL-1) can be resolved, the from or rejected to a flow of groundwater via the use of a heat Florence mine could provide not only a valuable resource pump. The use of groundwater for this purpose is advanta- of high-quality water for industrial or even potable uses, it geous, because its temperature is usually constant through- could also provide several hundred to several thousand kW out the year, at a level slightly above the annual average air of ground sourced heating and/or cooling, if a suitable de- temperature (for shallow groundwater), and typically mand can be identified. The ultimate constraint would be increasing at a rate of 1–3 °C per 100 m depth (Kavanaugh and Rafferty 1997; Banks 2012). Groundwater is thus usu- This article is part of the special issue on Sustainable Resource ally significantly warmer than outdoor air in winter and Management: Water Practice Issues. significantly cooler in summer (making it an ideal source of winter heating and summer cooling). The water contained in & David Banks abandoned, flooded mines is usually, in origin, groundwater. [email protected] However, the use of such mine water for heating and cooling 1 Holymoor Consultancy Ltd., 360 Ashgate Road, Chesterfield, offers a number of additional advantages: Derbyshire S40 4BW, UK • The workings and void space of the abandoned mine 2 School of Engineering, University of Glasgow, James Watt represent an enormous storage of water and heat. This Building (South), Glasgow G12 8QQ, UK can be seasonally manipulated to store warm water or 3 Groundwater and Geothermal Services Ltd., 1 Tree Terrace, cold water (Minewater Project 2008). Tree Road, Brampton, Cumbria CA8 1TY, UK • The tunnels and workings of the mine represent high 4 University of Cumbria, Energus, Lillyhall, Workington, transmissivity flow pathways, which, if intercepted by a Cumbria CA14 4JW, UK borehole or shaft, can sometimes yield many tens or 5 Scottish Universities Environmental Research Centre, hundreds of L s-1 of water. East Kilbride G75 0QF, UK 123 52 Sustain. Water Resour. Manag. (2019) 5:51–69 • The workings may already be accessible for pumping exchanger, which thus extracts heat from or rejects heat to via the existing abandoned shafts (no drilling costs). the mine water. • Mine water is often regarded as a potentially costly In an open loop system, the mine water is abstracted environmental liability (Banks and Banks 2001; Bailey (often pumped from a borehole or shaft) and is passed et al. 2016). Its use for low-carbon heating and cooling through a heat exchanger (which may, in turn, be thermally allows it to be transmuted into an environmental and coupled to a heat pump). The amount of heat extracted (H_ ) economic asset. is governed by the mine water yield (Q) and the tempera- • Many abandoned mine sites are ripe for redevelopment ture change at the heat exchanger (DThe), as described by for commercial or residential purposes, with heating the following equation: and cooling demands. _ H ¼ Q Á DThe Á qw Á cw ð1Þ Mine water has been used for several decades for _ -1 heating and cooling; reviews have been provided by Banks where H is the heat power available (J s or W), qw is the -1 et al. (2003, 2004), Watzlaf and Ackman (2006), Hall et al. water’s density (kg L ), cw is the water’s specific heat -1 -1 -1 (2011), Preene and Younger (2014), Ramos et al. (2015), capacity (J kg K ), Q is the water flow rate (L s ), and Bracke and Bussmann (2015) and Banks et al. (2017). qw Á cw is the water’s volumetric heat capacity (= c. -1 -1 Among a number of mine water, heat pump systems 4190 J L K ). operating worldwide can be listed: Park Hills, Missouri, Having passed through the heat pump/exchanger, the USA (Watzlaf and Ackman 2006; DOE 2015), Springhill, thermally spent water (i.e., cool water, if heat has been Nova Scotia, Canada (Jessop 1995; Jessop et al. 1995; extracted) needs to be disposed of legally and sustainably. Raymond et al. 2008), Marywood University, Pennsylva- The water may simply be rejected to a surface water nia, USA (Korb 2012), several in Saxony, Germany recipient (river or sea) if the quality is good enough (e.g., at (Ramos et al. 2015), Henderson molybdenum mine, Barredo coal mine shaft, Northern Spain—Loredo et al. Empire, Colorado, USA (Watzlaf and Ackman 2006), 2011; Ordo´n˜ez et al. 2012; Jardo´n et al. 2013). Often, Saturn coal mine, Czeladz, Poland (Malolepszy et al. 2005; however, the water will require treatment (e.g., to remove Tokarz and Mucha 2013), and Novoshakhtinsk, Russia iron, manganese, or acidity) prior to disposal to surface (Rostov Regional Government 2011; Ramos et al. 2015). water, as at the pilot heat pump scheme at Caphouse col- At a MW (megawatt) scale, one can mention the hospital liery in Yorkshire, UK (Athresh et al. 2016; Burnside et al. and university heating/cooling system sourced from Bar- 2016a). Alternatively, the treatment costs can be avoided redo coal mine shaft at Mieres, Asturias, northern Spain by reinjecting the thermally spent water back to the mine (Loredo et al. 2011; Ordo´n˜ez et al. 2012; Jardo´n et al. system via another (sufficiently distant) shaft or borehole, 2013; Banks 2017) and the Heerlen scheme, The Nether- or to a superjacent or subjacent aquifer unit. Examples of lands (Minewater Project 2008; Ferket et al. 2011; Ver- this type of scheme include Lumphinnans, Fife, and Shet- hoeven et al. 2014; Banks 2017). tleston, eastern Glasgow, Scotland (Banks et al. 2009). In the UK, however, the few operational mine water heat Reinjection is also practiced at Heerlen, The Netherlands pump schemes are either at a pilot stage or at a very modest (Minewater Project 2008; Ferket et al. 2011; Verhoeven scale (not exceeding several tens of kW thermal output): et al. 2014). For reinjection to be sustainable, dissolved Shettleston, Glasgow, and Lumphinnans, Fife (Banks et al. iron and manganese should remain in solution (in practice, 2009), Dawdon, County Durham (Watson 2012; Bailey this means avoiding exposure to oxygen); otherwise, rein- et al. 2013), Caphouse mining museum, near Wakefield jection wells can rapidly become clogged (Banks et al. (Athresh et al. 2016; Burnside et al. 2016a; Banks et al. 2009). 2017) Markham, near Bolsover (Athresh et al. 2015; A final option is to reinject all or part of the thermally Burnside et al.