<<

COGEL-02241; No of Pages 13 International Journal of Coal Geology xxx (2013) xxx–xxx

Contents lists available at ScienceDirect

International Journal of Coal Geology

journal homepage: www.elsevier.com/locate/ijcoalgeo

An overview of Canadian gas production and environmental concerns

Christine Rivard a,⁎,DenisLavoiea,RenéLefebvreb, Stephan Séjourné c, Charles Lamontagne d, Mathieu Duchesne a a Geological Survey of , Natural Resources Canada, 490 rue de la Couronne, Québec, QC G1K 9A9, Canada b Institut national de la recherche scientifique, Centre Eau Terre Environnement (INRS-ETE), 490 rue de la Couronne, Québec, QC G1K 9A9, Canada c Consulting geologist, 5725 rue Jeanne-Mance, Montréal, QC H2V 4K7, Canada d Ministère du Développement durable, de l'Environnement, de la Faune et des Parc du Québec (MDDEFP), 675 boul René Lévesque Est, 8e étage, boîte 03, Québec, QC G1R 5V7, Canada article info abstract

Article history: Production of hydrocarbons from Canadian started slowly in 2005 and has significantly increased since. Received 14 June 2013 is mainly being produced from shales in the Horn River Basin and from the Received in revised form 20 November 2013 Montney shales and siltstones, both located in northeastern and, to a lesser extent, in the Accepted 1 December 2013 Devonian in (). Other shales with natural gas potential are currently Available online xxxx being evaluated, including the Upper in southern and the Mississippian Frederick Brook Shale in (eastern Canada). Keywords: Canadian unconventional resources This paper describes the status of exploration and production in Canada, including discussions on Shale gas geological contexts of the main shale formations containing natural gas, water use for , the Overview types of hydraulic fracturing, public concerns and on-going research efforts. As the environmental debate Utica Shale concerning the shale gas industry is rather intense in Quebec, the Utica Shale context is presented in more detail. © 2013 Published by Elsevier B.V.

1. Introduction Shale gas formations targeted by industry are generally located more than 1 km deep and under pressures sufficient to allow natural flow. Natural gas is often considered a transition fuel for a low-carbon Vertical wells must progressively be deviated to the horizontal to economy because it is abundant, efficient, and cleaner burning than reach the target zone because the latter is typically relatively thin other fossil fuels. Over the past decade, shale has been heralded as the (50–100 m). Therefore, the horizontal part (termed a “lateral”) opti- new abundant source of natural gas in North America. The combination mizes natural gas recovery by allowing the borehole to be in contact of technological advancements in horizontal drilling and in multi-stage with the producing shale interval over significantly longer distances hydraulic fracturing (“fracking” in industry jargon) techniques, as well (and thus over a much larger surface area) compared to a vertical bore- as the progressive decline in conventional oil and gas reserves in hole. Almost all shale reservoirs must be fractured to extract economic North America, made shale gas the “energy game changer” over the amounts of gas because their permeability is extremely low, which last years. In addition, the fact that recoverable reserves of natural gas impedes gas flow towards the production well. To increase their perme- and oil in shales have been estimated to be large enough to potentially ability, shales are typically fractured with fluids injected under high free the United States from a decade-long dependence on oil imports, pressure, usually through a cemented liner or production casing that and replace nearly all coal-generated electricity (Soeder, 2013), has was selectively perforated. The fracking fluid used is specifictoeach probably largely contributed to making shale gas exploration and operator and differs from one shale formation to another, depending, production increasingly appealing in this country. The United States among other things, on the pressure gradient, brittleness (Poisson was the first to economically produce shale gas from the ratio and Young's modulus), clay content and overall mineralogy, hori- more than a decade ago; in 2013, there are over 40 000 producing zontal stresses, and gas to oil ratio (GOR). Historically, the most com- shale gas wells spread across 20 states. However, natural gas prices mon fracking fluid used by the shale gas industry has been slickwater have significantly decreased over the past several years, so that many (a simple mixture of water, proppants (usually sand), friction reducers shale dry gas plays (without liquid hydrocarbon production) are and other chemical additives) due to its low cost and effectiveness. currently at the lower limit of economic profitability. More recently, shale reservoirs appear to be increasingly stimulated with a hybrid treatment consisting of slickwater used in alternation with a cross-linked gel purposely designed for a specific viscosity, ⁎ Corresponding author. Tel.:+1 418 654 3173. with hybrid slickwater energized with N2 or CO2, or with hydrocarbons E-mail address: [email protected] (C. Rivard). such as gelled propane.

0166-5162/$ – see front matter © 2013 Published by Elsevier B.V. http://dx.doi.org/10.1016/j.coal.2013.12.004

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 2 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx

Micro-seismic events induced by fracking operations are now being shallow conventional hydrocarbons were targeted, mainly in overbur- routinely recorded on a fraction of the wells drilled in a new exploita- den (often at the bedrock/overburden contact). In western Canada, tion area using ultra-sensitive seismographs placed either in an adjacent the first gas discovery was accidentally made while drilling for water gas well, as a** buried array or as a surface array. These techniques allow near Medicine Hat, Alberta, in 1883. A second well was drilled the the estimation of fracture height and half-lengths from which a stimu- following year that produced enough gas to light and heat several build- lated reservoir volume can be calculated, which helps assess the effec- ings. The discovery of the world-class Leduc oil field in 1947 by Imperial tiveness of the stimulation. Generally, induced fractures are reported Oil made the Western Canada Sedimentary Basin the center of Canada's to extend less than 300 m vertically (Davies et al., 2012; Fisher and exploration and production. The industry started construct- Warpinski, 2012). ing a vast pipeline network in the 1950s, to start developing domestic Hydraulic fracturing has been used to stimulate production wells in and international markets. Canada is now the third largest producer of conventional oil and gas reservoirs (mostly in vertical wells) in North natural gas in the world (1720 billion m3 or 60 200 billion ft3 or Bcf America for more than 60 years. However, in the case of horizontal for 2012; National Energy Board, 2012) and the 4th largest exporter, shale gas wells, the stimulation process requires greater amounts of with the U.S. currently being its sole international market. water, sand and chemicals for a given well, and this mixture must be Canada's production of “primary” energy, i.e. energy found in nature injected at higher rates and pressures, and a much larger volume of before conversion or transformation, totalled 16 495 petajoules (PJ) in rock is involved compared to conventional reservoirs. Hence, more 2010. Fossil fuels accounted for the greatest share of this production, powerful equipment is required on site (pumper trucks) and much with crude oil representing 41.4%; natural gas, 36.5%; and coal, 9.2% more truck traffic for the transportation of water and sand is involved (NRCan, 2011). The remainder (12.9%) comes from renewable energy (if a local source is not available). Due to the horizontal drilling technol- sources. About 95% of the natural gas was produced from conventional ogy and multi-stage fracturing, these activities are taking place several sources, and the remaining 5% was from unconventional sources such times on multi-well pad sites, instead of taking place in multiple vertical as coal bed methane and shale gas. Recent exploration and exploitation wells on the surface. Environmental concerns are mainly related to of numerous shale gas plays in Canada have caused a sharp increase in seven issues that are themselves related to six main activities, as sum- both estimated in-place resources and natural gas reserves. The portion marized in Table 1. of shale gas in the Canadian energy production could significantly This paper presents the historical context and current state of shale increase in future years because of several factors, notably the large gas development in Canada (Section 2), geological contexts of main and continuous nature of unconventional reservoirs and declining con- Canadian shale plays containing dry gas (Section 3), facts on hydraulic ventional (oil and gas) production. There are indeed a number of shale fracturing (Section 4), water usage by this industry (Section 5), as well gas formations at various stages of exploration and development across as various research initiatives implemented to investigate different the country (British Columbia, Alberta, Yukon, , environmental issues mentioned above and to characterize the shale Quebec, New Brunswick and ). Fig. 1 shows the distribution formations themselves (Section 6). Then, public concerns (Section 7) of the main shale formations targeted by the industry. In many cases, and regulation related to drilling and fracturing (Section 8) are briefly these formations produce variable volumes of liquids associated with discussed. Finally, the historical background and social context of the natural gas. Because of higher viscosities and size of the molecules, Utica Shale (southern Quebec) are described in more detail. Although liquids are commonly produced from slightly coarser lithologies inter- only limited Utica Shale exploration has taken place, it has raised envi- bedded with the shales. As dry gas is currently not economical in ronmental concerns amongst the general public that have led to a tem- many cases, it is the production of liquids that is currently carrying the porary de facto moratorium on hydraulic fracturing in Quebec. cost of the shale gas development or exploration. The first shale gas production in Canada came from the Montney Play Trend ( and shale gas) in 2005 and the Horn River (exclu- 2. General context sively shale gas) in 2007, both located in northeastern BC, where drilling activities have rapidly expanded (Figs. 2 and 3). Industry interest for Over 500 000 oil and natural gas wells have been drilled to date in other Canadian shale and tight sand plays started around the same Canada, of which more than 375 000 are located in Alberta (CAPP, period in British Columbia, Alberta, New Brunswick and Quebec, as 2012). Petroleum development began in eastern Canada in 1858, illustrated in Fig. 2. As of the end of 2012, over 1100 wells have been where a 15.5 m (51 ft) oil well was dug (not drilled) in Oil Springs, either drilled for shale gas exploration and production or exploited for Ontario. This well became the first commercial oil well in North gas (gas also being a common by-product of or tight sand America. Natural gas was discovered in Ontario in 1859, but commercial wells) mostly in BC and AB. Fig. 2 provides the number of wells for gas was not produced in the province until 1889. In the late 1800s, some shale and tight sand gas in Canada,1 as well as estimates of shale gas production of natural gas from unconsolidated Quaternary sands for production in BC. Shale gas production for Alberta is not shown since local industrial purposes took place for a short period in the Trois- it represents less than 1% of BC production; Alberta shale gas production Rivières area (between Montreal and Quebec City, in southern Quebec). in 2011 corresponded to about 0.1% of total gas production in the prov- This very small reservoir was, however, rapidly depleted. At that time, ince. The AB shale and tight sand wells shown in Fig. 2 were largely drilled for liquids (condensates and oil); gas was a by-product. Fig. 3 shows the production increase of unconventional wells in BC over the last eight years. About 65 to 70% of total BC wells currently being drilled Table 1 target the (Fig. 1), especially its liquid-rich domain. Issues and activities of concern relative to the shale and tight gas industry (http:// www.rff.org/centers/energy_economics_and_policy/Pages/Shale-Matrices.aspx). This expansion of tight reservoir wells is not, however, without contro- versy, and this topic will be discussed later in the section. Nonetheless, Environmental concerns Activities compared to the U.S., unconventional gas development in Canada is 1. Water quantity 1. Site development and drilling preparation still in its nascent stages. 2. Water contamination 2. Drilling activities 3. Management of fracking and 3. Completion and hydraulic fracturing flowback fluid storage 4. Well operation and production 4. Radioactive wastes 5. Fracturing fluids, flowback, and 5. Nuisances (noise, trucking, light) produced water storage and disposal 1 British Columbia does not distinguish between shale and tight sand gas because they 6. Atmospheric emissions/air quality 6. Other activities (e.g. plugging and are part of a continuum of very low permeability reservoirs in which economic production 7. Induced seismicity abandonment) can only be achieved through hydraulic fracturing.

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx 3

Fig. 1. Shale gas formations in Canada containing dry gas. Shale-hosted petroleum reservoirs are known in all Canadian provinces (except for Prince Edward Island) and in two territories (Northwest Territories and Yukon). The most promising are found in 5 provinces: British Columbia (BC), Alberta (AB), Quebec (QC), New Brunswick (NB) and Nova Scotia (NS).

Most of the current drilling and production activities for shale gas success. There is no current exploration activity for shales in Nova and liquid-rich reside in northeast British Columbia Scotia. Quebec presently has a de facto moratorium on shale gas drilling (Fig. 1). Northern BC has now four active plays (Horn River Basin and and hydraulic fracturing and the last shale exploration activity in the St. Montney Play Trend and, to a lesser extent, the Cordova Embayment Lawrence Lowlands took place in December 2010. Because of low natu- and Liard Basin). Active plays in Alberta include the Duvernay and ral gas prices, industry activity in Alberta and is currently Montney shales. In New Brunswick, testing in the Frederick Brook focused on , conventional oil and gas, unconventional oil in the Shale has resulted in mixed results. This province, which was among extension in Saskatchewan of the prolific oil-rich U.S. Bakken play (part the first jurisdictions in North America to develop oil and gas, has been of the Williston Basin), and liquid-rich gas in the Duvernay shale in mainly active in tight sands gas since the 1990s. NB currently has one Alberta. producing shale gas well in the tight gas McCully field in the southern part of the province. In Nova Scotia, five vertical explo- 3. Geological overview of main Canadian shale gas targets ration wells were drilled in the Horton Bluff shale without reported The Canadian Phanerozoic successions comprise a significant num- ber of sedimentary basins with thin to thick organic-rich shale intervals (Hamblin, 2006). Of these, some are already at the gas production stage, and others are at various phases of exploration and definition of their potential to release economic volumes of natural gas. This section high- lights the main geological characteristics of some of the best-known

Fig. 2. Total number of wells drilled yearly for unconventional hydrocarbon (liquids and gas) resources in shales and tight sands per year in Canada and annual production of shale gas for British Columbia. Most wells were drilled in British Columbia (48.3%) and AB (48.2%), although gas represents a minor component in Alberta. Few wells are located in Quebec (2.3%), and the sum of wells in NB and NS equals 0.6%. Since total gas wells and gas production were provided for BC, the proportions shown in Fig. 3 were used to esti- mate these numbers for unconventional (shale and tight sand) gas only. Note: 106 m3/d Fig. 3. Proportion of unconventional (shale and tight sand) gas production compared to corresponds to 0.0355 Bcf/d. total gas production in BC (figures are from the BC Oil and Gas Commission).

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 4 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx producing and undeveloped shales. The geological character of the Regionally, the Duvernay Formation is 30 to 120 m thick and Upper Ordovician Utica Shale in Quebec is not presented here, because consists of three members, from base to top: 1) a black argillaceous it is discussed in detail in Lavoie et al., (2013, in this issue). Table 2 , 2) a black shale unit with carbonate detrital beds, and 3) a presents areal extents, estimated resources and estimated recoverable brown to black shale with argillaceous limestone (Switzer et al., reserves of gas in these selected shale gas formations or basins. 1994). In the East Shale Basin (Switzer et al., 1994), the slightly thicker Duvernay Formation is dominated by organic-rich lime mudstone. The 3.1. Upper Devonian Horn River Basin Shales Duvernay Formation in the West Shale Basin becomes less calcareous and more shale-rich from east to west. Depth from the surface to the The transition from the broad Middle to Late Devonian shallow ma- top of the Duvernay is about 1000 m near the eastern boundary to rine carbonate shelf of the Western Canada Sedimentary Basin (WCSB) about 5500 m in the west, this correlates directly with thermal matura- into a deeper shale-dominated domain occurs in the Horn River Basin tion data which documents a westward trend of increasing thermal ma- (Mossop et al., 2004). turity (ERCB/AGS, 2012). The Horn River Basin comprises three major Upper Devonian shale The Duvernay shales are dominated by marine-derived Type II units, from base to top; the Evie and Otter Park members of the Horn organic matter with total organic carbon (TOC) content comprised River Formation and the (Ferri et al., 2012). In between 0.1 and 11.1%; the highest values are generally found in the northeastern British Columbia, these three shale units form a roughly East Shale Basin (ERCB/AGS, 2012). Based on well logs and cuttings, 200 to 500 m thick succession that is either laterally equivalent (Horn the Duvernay Formation has an average porosity and permeability of River Formation) or overlies (Muskwa Formation) the Middle–Upper 6.5% and 394 nanodarcies, respectively (Dunn et al., 2012). Devonian carbonate platform and reefs of the Lower and Upper Keg River and Slave Point formations. In turn, the Upper Devonian shales 3.3. Lower Carboniferous Frederick Brook Member are overlain by the Mississippian shales of the Fort Simpson Formation (Ferri et al., 2012). The transgressive Muskwa Formation extends signif- The Frederick Brook member belongs to the Tournaisian (Early icantly into southwestern Alberta where it is known as the Duvernay Carboniferous) Albert Formation of the Horton Group (St. Peter and Formation. Johnson, 2009). The Horton Group is the first sedimentary unit to be Over most of the Horn River Basin, the Upper Devonian shales are deposited in the Maritimes Basin, a successor basin that formed after buried to depths of 2500 m and well within the dry gas window the Devonian Acadian Orogeny in eastern Canada (Hamblin and Rust, (National Energy Board, 2011). The black to dark gray colored shale 1989). Post-orogenic sedimentation of the Horton Group was domi- units in the Horn River Basin consist of marine Type II organic matter nated by alluvial to lacustrine environments (Martel and Gibling, with Total Organic Carbon (TOC) values up to 6% (British Columbia 1996). Ministry of Energy and Mines, 2005). The Evie and Muskwa shales are The Frederick Brook Member is a lacustrine shale overlain and un- siliceous and pyrite-rich whereas the Otter Park shale is more calcar- derlain by successions of sandstone, siltstone and shale (St. Peter and eous (National Energy Board, 2011). Porosity values can be relatively Johnson, 2009). The Frederick Brook lithofacies consist of laminated high, reaching up to 5% (British Columbia Ministry of Energy and Mines, kerogen-rich dolomitic mudstones, microlaminated kerogen-rich 2005), whereas average permeabilities range between 100 and 300 shales (oil shales) and kerogen-rich siltstones with minor sandstone nanodarcies (British Columbia Ministry of Energy and Mines, 2005). interbeds. St. Peter and Johnson (2009) estimated its maximum thick- ness to be around 350 m, although recent seismic data and drilling in 3.2. Upper Devonian Duvernay Formation the Moncton sub-basin (Corridor Resources Inc., 2009) suggest that a much thicker succession of 900 to 1100 m is locally developed. From The Duvernay Formation is an Upper Devonian shale-dominated burial depths of 3 to 4 km in the central part of the Moncton sub- succession that covers a significant part of west- of the basin, the unit shallows to 1 to 2 km at the sub-basin margin. Western Canada Sedimentary Basin (Mossop et al., 2004). The south- The Frederick Brook Member lacustrine shales are considered to ward transgressive shales of the Duvernay (from the platform margin have sourced the conventional oil and gas fields of Stony Creek and located to the north) did not kill reef growth in the WCSB but are McCully, respectively (St. Peter and Johnson, 2009). The organic matter found laterally equivalent and enclosing the oil-prolificLeducreefsfor in the shales are Type I algal material with subordinate Type III land- which they acted as source rocks (Allan and Creaney, 1991). derived organic matter (St. Peter and Johnson, 2009). The TOC values In west-central Alberta, the Duvernay shales are found in the East average 11% in the thermally immature areas (St. Peter and Johnson, Shale and West Shale basins (Switzer et al., 1994), both of which differ 2009) although, in the deeper, gas-prone part of the basin, TOC values in the geological setting and characteristics of the Duvernay Formation are between 1 and 2.5% (Corridor Resources Inc., 2009). The shales are (see below). In the WCSB, the Duvernay Formation overlies the Upper clay-rich (illite) with a similar volume-percent of quartz, diagenetic Devonian carbonate platform of the Cooking Lake Formation and the albite and carbonates (dolomite and calcite) (St. Peter and Johnson, formation is in turn overlain by the Upper Devonian Ireton Formation 2009). Well logs indicate that the gas-prone shales have porosities rang- of clastics and carbonates (Mossop et al., 2004). ing from 3 to 8% (Corridor Resources Inc., 2009). It is noteworthy that

Table 2 Extents and reserves of main shale gas formations and basins in Canada.

Shale gas formation or basin Approximate area (km2) Estimated potential (Tcfa) Estimated recoverable reserve (Tcfa)

Horn River (BC) 11 500 450 78 Montneyb (AB +BC) 25 549 +26000 2133 +(80–700) N.A. Duvernay (AB) 9850 443 N.A. Utica (QC) 10 000 100–300 22–47 Frederick Brook (NB) 1000 N75 N.A.

Note: Horn River data are from BC Ministry of Energy and Mines, National Energy Board (2011); Montney data are from the BC Ministry of Energy and Mines (2012) and Energy Resources Conservation Board (ERCB)/Alberta Geological Survey (AGS) (2012); Duvernay data are from ERCB/AGS (2012); Utica data from Duchaine et al. (2012); and Frederick Brook data from Corridor Resources Inc. (2009). Numbers in bold are related to Alberta (AB). a Tcf corresponds to trillion cubic feet (1012 ft3). 109 m3 corresponds to 0.0355 Tcf. b Montney Formation.

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx 5 one vertical shale gas well is currently producing gas from this shale unit related to chemical additives, methods of fracking and regulations by within the tight sandstone McCully gas field (St. Peter and Johnson, state, the province of British Colombia has recently implemented the 2009). website http://fracfocus.ca. As of January 1, 2012, disclosure of used additives on this website is required by the BC Oil and Gas Commission 3.4. The Lower to Middle Triassic Montney Formation (BCOGC); Alberta and New Brunswick have recently announced (April 2013) that they now have the same legal obligation. The Triassic succession of western Alberta and northeastern British All wastewater is collected and stored in enclosed tanks with Columbia was deposited on a passive margin marine shelf and slope secondary containment to avoid potential infiltration of slickwater or (Podruski et al., 1988) before the development of a foreland basin in saline flowback water into the soil in BC and AB. No unlined surface time. The Montney Formation unconformably overlies Upper ponds are currently being used in Canada. In BC, the vast majority of Paleozoic rocks and is overlain by the phosphatic interval at the base water is re-injected at depth in deep saline aquifers such as those in of the (Gibson and Barclay, 1989). the Debolt Formation. Seismic events induced by these injections are The Montney Formation lithofacies are dominated by shale and silt- also a concern for the population (see below). In eastern Canada, stone with varying degrees of dolomitization and as such, the Montney deep-well injection of flowback water has not been tested or done is not truly a shale gas unit. Fine-grained sandstones and coquinas are because of lack of understanding of potential deep-seated geological also present in the upper part of the siltstone-dominated succession storage capacity (QC) or is simply not authorized because of potential (Gibson and Barclay, 1989). The Montney Formation reflects a trans- leaks resulting from assumed permeability issues of cap rock units (NB). gressive–regressive third order cycle (Gibson and Barclay, 1989)with An increasing number of cases of small but perceivable earthquakes a lower major transgressive facies and maximum flooding succession have been reported in seismically quiescent areas where active subsur- (lower shale-siltstone interval) overlain by shallower and coarsening face high-pressure water injection, either for geothermal tests or upward facies. hydraulic fracturing, took place. Dense arrays of seismographs have The thickness of the Montney Formation increases westerly from been locally installed (e.g., northeastern BC) to decipher the source of 0 m (at the erosional margin of the basin) up to 300–400 m in both these tremors. In the case of the areas with shale gas development, Alberta and British Columbia and similarly, the depth to the top of the the issue is to distinguish deep crustal events from shallow events Montney increases in the same direction from approximately 500 m linked either to fracking programs or to wastewater re-injection in in the east to over 4000 m in the west. This variation in burial resulted deep aquifers. Preliminary results from the research in BC indicate in the development of oil to dry gas zones in an overall westerly trend. that hydraulic fracturing can lead to limited induced seismicity (BC Oil The Montney Formation consists of Type II/III organic matter and Gas Commission, 2012). No damage has been documented as a (Ibrahimbas and Riediger, 2005). The average TOC content of the result of induced seismicity associated with shale gas development Montney is 0.8%, with a range of 0.1 to 3.6%. The Montney siltstone sites. The highest magnitude recorded during hydraulic fracturing (the gas producing lithology) has low porosities (lower than 10%), activities in northeastern British Columbia is 3.8 on the Richter scale. although the associated sandstone porosity can be as high as 35%. The This corresponds to minor damage (event felt only by some people on Montney lithofacies are clay-poor (maximum 20%, BC Oil and Gas the Mercalli scale). From preliminary data, the time interval between Commission, 2012) and show a high content of quartz, carbonates and the start of the fracking program and the induced seismic event (magni- feldspars. In some areas of BC, the Montney is being actively developed tude 2 to 3.8) was between a few minutes to about one day (BC Oil and for liquids, with gas being a by-product. Gas Commission, 2012). In 2012 and 2013, GSC deployed arrays of seis- mographs in the Northwest Territories and New Brunswick, in areas of 4. Overview on fracturing eventual shale exploration and development. The stations are currently monitoring the regional large and fine-scale natural seismicity. Over 175 000 wells have been stimulated by hydraulic fracturing in In provinces where no large-scale oil and gas activities had yet taken Alberta alone (mainly vertical wells), with few reported incidents. How- place, several initiatives have been implemented at the provincial level ever, as mentioned above, multi-stage fracking in horizontal wells in the last 3–5 years, including working groups (NB), a strategic envi- involves higher injection pressures and rates and a larger quantity of ronmental assessment (QC) and even a specific hydraulic fracturing water. About 14 000 of these wells have been fracked so far across review committee (NS). In addition, public consultations and com- Canada, with most of them being located in relatively remote areas. munity information sessions were carried out in Quebec in 2010 However, this number includes all types of unconventional reservoirs (BAPE, 2011), leading to the recommendation of a Strategic Environ- (shale gas and liquid-rich shales, tight gas and tight oil, and coal bed mental Assessment (SEA) dedicated to issues related to shale gas devel- methane), not all of which require large amounts of water and high opment. During the SEA process, the Quebec Ministry of Environment pressures to frac. For instance, coal bed methane is typically fracked would only have considered authorizing fracking if the SEA Committee with nitrogen in Alberta. deemed it useful for gaining scientific knowledge. However, because In BC, slickwater is used in the Horn River Basin, while Montney no operator requested a permit to conduct such activities, the SEA liquid-rich gas shales and siltstones are mainly fracked with foams Committee proceeded with its studies by other means, which led (a mix of gas and water). In Alberta, slickwater, cross-linked fluids effectively to a 2-year moratorium on shale gas fracking in Quebec. (typically guar-based fluids cross-linked with boron ions), and a combi- This moratorium has recently been extended for the St. Lawrence Low- nation of the two have been used in the Duvernay Formation. In New lands until a new legal framework is set to specifically address hydro- Brunswick, LPG (predominantly gelled propane) was successfully used carbon activities. Additional public consultations (Bureau d'audiences in the first vertical shale gas well; the following two horizontal wells publiques sur l'environnement, BAPE) will be held on the SEA report used slickwater and were unsuccessful. Industry has mainly used conclusions in 2014. The SEA committee will end its mandate in Decem- slickwater fracturing and hybrid fracs (cross-linked fluids with guar ber 2013 and the BAPE will provide recommendations in 2014. Public gum) in the calcareous shales of the Utica so far, with the exception of consultations were also held in New Brunswick in 2012 and expressed one vertical well in a liquid-rich domain, where propane was used. concerns by stakeholders have certainly influenced the newly pub- Chemical additives used in hydraulic fracturing are one of the main lished (February 2013) guidelines to regulate the unconventional concerns for Canadians, even though proppants and chemical additives shale-hosted petroleum industry in the province (New Brunswick, in most slickwaters constitute less than 2–3% of the overall composition 2013). (Nash, 2010). To parallel the publically available U.S hydraulic fractur- Two incidents recently occurred in Alberta in relation to hydraulic ing chemical registry “fracfocus.org.”, which provides information fracturing operations. In September 2011 in , improper

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 6 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx completion work (perforated casing above the base of groundwater Water sourcing is a key issue for hydraulic fracturing in BC. In some protection, at a depth of 136 m) was found to be the cause of contami- locations, it is difficult to collect sufficient water for a high-volume nation of a near-surface water-bearing sandstone with gelled propane fracking program due to the highly variable stream flow conditions. In (ERCB, 2012a). However, the impacted zone was not a source of potable the Prairies (i.e. AB, SK and MB), water usage is also becoming problem- water. The base of groundwater protection in Alberta and British atic since several river basins in the southern regions have fully allocated Columbia is set at 600 m deep, unless the interface can be proven to surface waters. Initially, the industry preferred to use fresh water, but be shallower. In January 2012, a spill occurred in Innisfail due to inter- now companies can use brackish or even saline water for fracking pur- well bore communication, causing the release of about 500 barrels of poses. Saline water from the Debolt Formation (20 000–30 000 ppm of fracturing and formation fluid to the surface, affecting 4.5 ha. Frozen TDS) underlying the Horn River Basin is being used for fracking by some ground conditions prevented much of the fluid from seeping into the companies. However, this source of water contains H2S and other gases ground and the majority of the cleanup operations were complete with- (CO2,CH4) that must first be removed in a treatment facility, and the in 72 h (ERCB, 2012b). saline water must often be diluted. Regular friction reducers can be used to a salinity up to about 25 000 ppm. Above this salinity, pipes 5. Water use and infrastructure, as well as chemical additives (mainly friction reducers) have to be adapted to the higher salinity. The industry has Among available fracking techniques, slickwater hydraulic fractur- developed additives that work at salinities reaching up to 60 000 ppm ing is the one that uses the most water. It is, however, the least expen- (Ferguson et al., 2013) and 200 000 ppm is targeted, to reduce flowback sive method and has proven to be very effective, mainly because it water management and treatment as much as possible. maximizes the contact surface by generating complex fracture net- The depth to the base of fresh groundwater aquifers is, unfortu- works in the shale unit, especially in brittle rocks with higher silica or nately, poorly known across much of Canada. Water wells are typically carbonate content and lower clay content (Johnson and Jonson, 2012). too shallow to reach the base of fresh groundwater, while oil and gas Estimates from Johnson and Jonson (2012) using approximately 500 wells, targeting much deeper zones, have historically rarely included wells in seven formations and five different basins showed that there the systematic report of the water salinity for a given well, especially is an order of magnitude difference for water usage between foam and at relatively shallow depths. Alberta is the only province that has slickwater fracs: foam fracs in siltstone or shale formations use around defined this base, using the depth at which water exceeds 4000 ppm 200 m3 of water, while siliceous shale slickwater completions require of TDS. Work on the definition of the Base of Groundwater Protection 2500–5000 m3 per frac stage. For this reason, the cumulative water (BGP) started in the 1980s by Alberta Environment, based on a series usage for the Montney Play Trend was much lower than that of the of reference cross-sections; this product was further updated and Horn River Basin, even though more wells were drilled each year in adapted by AGS and is available on a self-serve database (https:// the former. www3.eub.gov.ab.ca/Eub//COM/BGP/UI/BGP-Main.aspx). In the Besides water quality issues, there is public concern related to water Prairies, groundwater is often brackish, or slightly salty, near the sur- quantity. It is difficult to estimate how much water will be required for face. In eastern Canada and BC, the base of fresh groundwater would each well until test sites have been studied. Quantities of fluids required likely be in the order of 200 to 300 m, except in coastal areas and in depend mainly on the geology, i.e. the lithology, petrophysical and areas where saline water from Quaternary sea invasions has not yet geomechanical properties of the rock and hence, the pressure necessary been leached out, where it could be shallower. For instance, there is a to fracture the shale, the shale depth, length of laterals, the stimulation 2200 km2 area in southern Quebec overlying, for its main part, the technique used, the number of frac stages per well and anticipated Utica Shale, which contains brackish water of Champlain Sea origin water returns (Johnson and Jonson, 2012). In addition, in order to that has not been leached away by recharge or fresh groundwater maximize efficiencies and minimize footprints, well pads are designed flow in the active zone (Beaudry et al., 2011). for many wells, which may be fractured consecutively, thereby increas- ing water demand over a short period of time. Typically in BC, there are 6. On-going research currently six or eight wells per drilling pad, but this number can go up to 21 on a given pad (for example, in the Horn River Basin). Water Although the regulation of shale gas development is primarily a issues could, therefore, mainly be related to the intensity of shale provincial jurisdiction in Canada, the Geological Survey of Canada has gas development. initiated in 2011 several new research projects focusing on various In BC, reported volumes of water use during a well hydraulic fractur- aspects of shale gas exploration and development in Canada, in collabo- ing range from 2000 m3 to over 100 000 m3 per well (i.e. approximately ration with the provinces and universities. These studies focus on two 66 to 3300 large tanker trucks, since a large water tank truck is able to themes: 1) evaluation of the gas resource (in place and recoverable) carry about 30 m3). Averages of 1900 to 7800 m3 for the Montney and geological characteristics of shale-hosted petroleum reservoirs, Play Trend and 34 900 m3 for the Horn River Basin were reported and 2) potential environmental issues related to hydraulic fracturing. by Johnson and Jonson (2012), while mean values of 10 000 to The first theme includes three studies. The first one aims at developing 25 000 m3 for the Montney Play Trend and 25 000 to 75 000 m3 for a methodology for in-place and recoverable gas resource assessment, the Horn River Basin are provided in Precht and Dempster (2012).In which will initially be tested on mature and frontier basins in Alberta, Alberta, an average of 50 000 m3 is estimated for slickwater fracturing British Columbia and Quebec. The second one focuses on geological (Precht and Dempster, 2012). In Nova Scotia, volumes for the two ver- characteristics of specific shale reservoirs in Canada and the U.S., so as tical wells that have been fracked so far were of 5900 and 6800 m3, to better understand the quality and behavior of these reservoirs, while in NB, volumes for the two horizontal wells were ~20000 m3.In using parameters that control their hydrocarbon storage capacity such Quebec, volumes ranged from several hundred cubic meters to as mineralogy, nature of organic matter and its porosity evolution 15 000 m3 and the average frac stage used 1500 m3. The U.S. literature through increasing thermal conditions. The third project studies the reports that drilling and hydraulic fracturing of shale gas wells together geological integrity of cap rock in three provinces of eastern Canada: typically use 7500 to 15 000 m3 (from 2 to 4 million gallons) of water Quebec, New Brunswick and Nova Scotia. (GWPC and ALL Consulting, 2009). The return water volume combining The second research theme on environmental aspects includes two produced and flowback water in BC varies from 15 to 70%. In the studies: one on potential impacts of shale gas development on ground- Montney, between 50 and 100% of water is recovered, while much water quality, so as to improve the understanding of a possible risk less water is being recovered in the Horn River Basin. In the Utica of of natural or artificially-induced link between the shale gas target Quebec, the average flowback recovery was 45%. (N1000 m deep) and surficial aquifers (b300 m), while the second

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx 7 aims at increasing the understanding of potential induced seismicity theoretical processes that may affect groundwater quality (e.g. fluid caused by injection for hydraulic fracturing purposes or for disposal by migration mechanisms using numerical simulations by McGill University injection of flowback wastewater (which includes the installation of and INRS, Gassiat et al., 2013). several seismographs as mentioned in Section 4). The groundwater In addition, other studies are being conducted that are indirectly project, which is described in Lavoie et al. (2013, this issue), focuses related to shale gas, including those carried out for water allocation or on a local study area in southern Quebec, while the induced seismicity identification of additional water sources to support gas development project is active in western Canada (BC, NWT), and has been expanded (e.g. AB and BC), those linked to optimal measurement of dissolved in eastern Canada (NB). All these projects are multi-partnered, includ- gas in groundwater, such as the collaborative project between Environ- ing active collaboration with the industry, provincial departments of ment Canada and the University of Calgary (Roy and Ryan, 2013), and natural resources, energy and environment, and universities. In parallel, those linked to potential impacts of oil development on aquifers such Environment Canada is carrying out a Canada-wide project on the as studies by the Institut national de la recherche scientifique (INRS) development of impact indicators of shale gas activities on groundwater in Gaspésie and Anticosti, QC (Peel et al., 2013; Raynauld et al., 2013). using laboratory work, field data as available, and modeling, while Also, many regional scale hydrogeological studies have been carried Health Canada, in collaboration with NB, has undertaken a study on out in Canada to support water management and aquifer protection air emissions to understand the potential impact that shale gas develop- over the last decade. These studies are crucial as they provide geological, ment may have on air quality in regions where such development may hydrogeological and often geochemical information and maps, and a occur. Life-cycle greenhouse gas emissions related to shale gas develop- better understanding of groundwater flow and aquifer vulnerability. ment have already been the focus of a national compilation ((S&T)2 The Groundwater Program of the Geological Survey of Canada (GSC) Consultants Inc., 2011). has been characterizing regional aquifer systems for the last 18 years. Research studies are also being carried out in many provinces, So far, the characterization of twelve regional aquifers has been com- typically in an academic/governmental collaboration. For instance, in pleted and seven others are underway across nine provinces; a total of Quebec, the SEA Committee is funding many studies, two of which are 30 key aquifer systems are targeted to be mapped and assessed by specific to 1) the theoretical numerical modeling of near-well gas 2024 (Rivera et al., 2003). All these projects are carried out in a collabo- migration and upward fluid migration by Université Laval (Nowamooz rative manner between the federal and provincial governments. et al., 2013a, 2013b) and 2) nature and concentration of natural back- A few provinces have undertaken regional hydrogeological charac- ground dissolved gas in groundwater in the St. Lawrence Platform led terization studies (QC, AB, SK, and BC). In Quebec and Alberta, programs by the Université du Québec à Montreal (UQAM) (Pinti et al., 2013). started in 2008 with tens of millions of dollars of funding. The Quebec These two studies will be completed by December 2013. In British Program (programme d'acquisition des connaissances en eau souterraine Columbia and Alberta, detailed research on shale resource characteriza- au Québec,PACES,http://www.mddep.gouv.qc.ca/eau/souterraines/ tion and on various development-associated environmental issues is in programmes/acquisition-connaissance.htm) presently involves six progress. The Alberta Geological Survey has undertaken in 2009 a study projects that are near completion and five others that will be completed on measurement and location of micro-earthquakes in the province, to by 2015. These multi-partner research projects are led by researchers at monitor natural and fracking-induced seismicity. Researchers from the Quebec universities. Some of the innovative aspects of the PACES University of Alberta are studying isotope reversals and gas maturation Program include 1) common databases, methodologies, and deliver- in various reservoirs, including those in the Appalachians and Western ables so that final results, tools, maps and cross-sections will be compa- Canada Sedimentary Basin (WCSB) (Tilley and Muehlenbachs, 2012; rable and/or have similar meanings and 2) the mandatory participation Tilley et al., 2011). The same research team also currently has a project of regional organizations such as regional municipalities and watershed aiming at understanding the origin of shallow natural gas in the organizations to ensure that what is being studied is of interest and Western Canada Sedimentary Basin using isotope chemistry. Alberta relevance to the region, and that knowledge, maps and tools are Environment commissioned a few years ago a study on chemical and transferred to users (for more information, see Ouellet et al., 2011; isotopic characterization of groundwater in Alberta using existing Séjourné et al., 2013). In 2011, The PACES Program was accelerated monitoring wells, which included dissolved and free gas, to establish a in order to cover all regions targeted by the shale gas industry, baseline against which future impacts on groundwater could be evalu- following recommendations from the public consultation process ated (Cheung and Mayer, 2007). In British Columbia, researchers from and needs of the SEA Committee. The Alberta Geological Survey Simon Fraser University in partnership with the BC Ministry of Forests, (AGS) has also initiated a vast and comprehensive groundwater Pro- Lands and Natural Resource Operations are presently working on two gram (Provincial Groundwater Inventory Program, http://www.ags. projects related to shale gas development in northeast BC. One focuses gov.ab.ca/groundwater/), which is divided into two components: on the characterization of the groundwater system and risk to ground- saline and non-saline aquifer systems. Non-saline aquifer studies are water quality in the Montney region. The second project will assess carried out in collaboration with Alberta Environment and Water and water supply/demand and projected climate change impacts in relation aims at mapping and understanding the province's groundwater to the overall water budget including interconnections between surface resources. The saline projects aim at mapping all major saline aquifers water and groundwater. In Ontario, and Saskatchewan, the of the province, from the crystalline basement to the lowermost aquifer geological features of shale gas and oil formations are currently being of the . However, AGS and the former Alberta Research characterized by the provinces. Regional scale initial appraisals of the Council had conducted hydrogeological mapping since 1968 and most numerous lesser known shale units in Canada are in progress in all (~85%) of the province has now been covered, except in the northeast- southern Canada jurisdictions, as well as at specific sites in the Canadian ern part (see Fig. 4). SK and BC have also characterized aquifers to differ- Arctic through provincial and territorial initiatives. New Brunswick has ent levels, mainly providing aquifer vulnerability indices and aquifer recently announced the creation of the New Brunswick Energy Institute classifications. BC has classified most aquifers in highly populated (http://nbenergyinstitute.ca/) composed of researchers from NB uni- areas, but these only cover ~15% of the province; vulnerability mapping versities and elsewhere, to ensure that credible independent research using the DRASTIC index was also carried out on and and monitoring are being carried out in support of energy files, includ- the Gulf Islands in collaboration with universities and the GSC. These ing shale gas exploration and production, and that findings are being aquifers are in the order of tens of km2 and thus, do not appear in communicated to the public. As well, government-academic projects Fig. 4. Of note, the northeastern part of BC has recently been the focus are being carried out to study in situ conditions prior to shale gas pro- of hydrogeological studies where aquifer classification was performed, duction (e.g. geochemistry of water wells near Sussex by the University based on limited available information. The Ontario Geological Survey of New Brunswick and Geological Survey of Canada, Al et al., 2013)and (OGS) is currently carrying out a baseline groundwater geochemistry

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 8 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx

Fig. 4. Location of regional aquifer studies in Canada. The area name, extent, and project duration are provided. Shale gas formations are shown as a background, to point out which aquifers above them have been studied so far. This map shows only study areas of 1500 km2 or larger, due to the size of the map. Saskatchewan has based its characterisation on 1:250 000 mapsheets. Alberta has also mainly worked with 1:250 000 mapsheets until recently; because most of the study delineations are not available in digitalformat,thecoverageshownis based on Lemay and Guha (2009). The inset presents a detailed overview of studied areas in southern Quebec. assessment of the major rock and overburden units, including dissolved Fig. 4) have exacerbated these concerns. Retrospectively, implementing gas (e.g. methane) analyses, in southern Ontario. OGS has also worked a large-scale new industry such as oil and gas in eastern Canada would along the Niagara Escarpment to characterize the carbonate have required much more preparation and prior public consultation. In aquifers. A few other studies were conducted by consultants and funded QC and NB, economic benefits for provincial jurisdictions no longer by a program implemented by a Federal Department (Agriculture and sway public opinion if there is a perception of environmental degrada- AgriFood Canada). The area covered by these studies are, however, tion should the industry be allowed to proceed (Québec, 2011). There typically smaller than 600 km2. is thus a strong need for a transfer of scientific information to the Fig. 4 shows the on-going and completed regional aquifer studies. stakeholders. Technology, scientific studies and regulations must also Only study areas larger than 1500 km2 were plotted at this scale. In be developed coherently to ensure a sustainable development and an total, more than 500 000 km2 are being or have been covered by adequate resource development framework. these hydrogeological characterization programs across Canada. Shale At a workshop on shale gas and the potential impacts of exploration gas formations are presented in background. This map shows that and development on groundwater held in November 2011 which gath- some significant gas- and liquid-producing shales (e.g. Horn River and ered mainly provincial hydrogeologists and governmental scientists, Montney, northeastern BC) have not yet been thoroughly studied in a the following main conclusions were reached (Rivard et al., 2012): hydrogeological context, mainly because they are located in remote, sparsely populated areas. • The use of brackish or saline water, which is not in conflict with other water uses, should be encouraged; 7. Public concerns and recommendations • Baseline studies should be carried out to ensure that groundwater is characterized prior to exploration; Public concerns and opposition to shale gas development exist, par- • Research studies must be carried out on potential upward migration ticularly in non-traditional hydrocarbon producing jurisdictions such as of fluids, through improperly cemented casing, improperly aban- Quebec (see Section 9) and New Brunswick. The fact that some shales doned wells, and existing and induced fracture networks; are located under populated and/or agricultural areas (e.g. Utica Shale • Monitoring programs should be developed for all stages of a shale well in Quebec) and below key Canadian aquifers (such as those shown in life cycle (pre-, syn- and post-fracturing and production);

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx 9

• Data from all sources need to be made available (publically or at least environmental issues (e.g. for water withdrawals, water and air quality, to provincial authorities). gas flaring and authorization or permits for fracking operations). In western provinces (BC, AB), authority has been delegated to single The Council of Canadian Academies (CCA), which is a private, non- organisms (BC Oil and Gas Commission and Alberta Energy Regulator, profit corporation funded by the Government of Canada to perform formerly ERCB) that govern most aspects of the industry. independent, expert assessments on important public issues, published In addition to a cemented surface casing to protect groundwater, a in 2009 a report on the sustainable management of groundwater in dual-barrier regulation is generally in effect and mandatory in the case Canada (Council of Canadian Academies, 2009). The CCA recommended of a new basin, formation or region, or if there is significant change that more efforts be focused on characterizing aquifers of populated in the fracking technique/design. However, a single barrier may be areas and on installing monitoring wells to ensure sustainable ground- approved under certain conditions, depending on the jurisdiction. At a water management, and that data should be publically available. The minimum, cement integrity must be confirmed visually by observing Council is currently working on a report on potential environmental cement returns at surface, and a cement bond-log must be performed impacts of shale gas development that should be published in early if no returns are observed at surface in AB, BC and NB. A leak-off test 2014. after drilling the cement shoe does not appear to be mandatory in all these provinces, but can be performed as a standard best practice, and 8. Regulation it is presently mandatory in SK, QC and NB. Casing and cement integrity must be verified before any hydraulic fracturing operation in NB and In Canada, provinces manage and generally own their onshore Alberta, while it is not mandatory in BC and SK (but these operations natural resources, including oil and gas, and are the custodians of can again be part of standard best practices). Quebec currently does surface water and groundwater. However, the federal government not have a specific regulation for hydraulic fracturing. However, even responsibilities assumed by the National Energy Board (NEB) and Natu- when legislation is in place to test the casing integrity, potential envi- ral Resources Canada include inter-provincial and international energy ronmental issues related to wellbore leakage remains, as these tests trade, cross-jurisdiction pipelines, exports/imports as well as natural can fail to detect cement defects (Jackson et al., 2013). Therefore, the resource regulation powers in the Canadian Arctic, offshore marine development of better engineering/technical methods is needed, areas and Aboriginal lands. In Quebec, the mining system is based on a including research and monitoring on cement curing, emplacement first come, first served basis (mining claims) and is currently in effect techniques and bonding; in parallel, detection and monitoring of the for onshore oil and gas exploration permits. Elsewhere in southern presence of fugitive gas, brine and flowback chemicals in shallow Canada, subsurface mineral rights for oil, gas and coal are obtained groundwater that could be indicative of leakage should also be carried through a bidding process for all areas open to exploration. In the Arctic out on a routine basis (Jackson et al., 2013). frontier area, exploration permits are typically awarded to the operator For these reasons and many others, environmental regulation needs with the best exploration program that commits to work obligations to be regularly updated following technological and scientific develop- and meets or exceeds all regulatory requirements, as a means to encour- ments and strengthened to best protect health and environment age exploration activities in remote places. (Rivard et al., 2012). For instance, groundwater monitoring wells are Almost everywhere in Canada, the exploration permit obtained not required at this time, except for coal bed methane operations. Com- includes the exclusive right to search for mineral and petroleum panies carry out baseline geochemical studies around their sites on a substances, but does not give ownership of surface rights (implying voluntary basis. Members of the Canadian Association of Petroleum that landowner permissions are required for surface access to acquire Producers (CAPP), which account for 90% of the petroleum production seismic data or conduct any other kind of exploration activities). A in Canada, pledged to uphold operating practices beyond current legal contract (surface lease) must be signed between the company and the regulations, such as assessing potential health and environmental risks landowner to drill a well (private or Crown, to the exception of Quebec, of each additive, and baseline groundwater testing (http://www.capp. where, strangely, no lease is required on public lands). However, in ca/aboutUs/mediaCentre/NewsReleases/Pages/ southwestern Ontario (near Lake Erie), landowners own both surface GuidingPrinciplesforHydraulicFracturing.aspx). The BC government and minerals. As in the U.S., Canada's energy policy is market oriented, installed 6 groundwater monitoring wells in the Montney Basin in i.e. gas price is based on supply, demand, transport and infrastructure 2011, and discussion are on-going to put provincial monitoring wells investments. Therefore, both Federal and Provincial governments have in the Horn River Basin. In Quebec, one of the SEA projects on sampling jurisdictional powers that are important in energy issues. In addition, dissolved gas across the St. Lawrence Lowlands (Pinti et al., 2013) Canada requires aboriginal consultation on decisions that may impact represents another provincial initiative. aboriginal rights or title on their lands. Some provinces have regulations that require permits for geophysi- 9. The Quebec Utica Shale case cal work and licences for wells, while others require specific permits to either drill, complete, hydraulically fracture, modify and or abandon a The case of the Utica Shale is discussed here because it is located in well. Lease agreements are required for surface land access, while with- Quebec, where a shale gas hydraulic fracking moratorium is currently drawal permits are required for water usage. There are also regulations in place and large-scale development has not occurred. This section that require drilling reports (including casing and cementing reports), presents information meant to provide insight into the much publicized borehole geophysical log data (rock evaluation), and well testing data societal context that led to strong public concerns, the de facto morato- (reservoir evaluation) in a timely fashion, which are made public imme- rium, and the end in 2010 of all shale gas exploration activities in the St. diately, or after a brief period of confidentiality (3 months to 3 years) Lawrence Lowlands. The Utica Shale is found along the St. Lawrence depending on the well category and province. Strong provincial and River, mostly on the south shore, as are about 90% of the people (as federal regulations govern operational practices to protect the environ- Montreal is part of the shale gas exploration area) and 90% of the ment including air quality, agricultural and forested area land use, parks, farmlands of Quebec. At the apex of the exploration rush in 2008, oper- wildlife habitats, fresh surface water and groundwater, although these ators acquired permits over (and beyond) the entire sedimentary suc- are not specific to the shale gas industry. cession of the St. Lawrence Platform (BAPE, 2011); the area covered In eastern Canada, regulations go through the Departments of Mines by exploration permits for the Utica Shale (shown in red in Fig. 5) and Energy for NB, of Natural Resources for QC, and of Energy for NS, for extends over ~20 000 km2, although it contains a zone northwest of exploration and drilling activities (e.g. for geophysical work, drilling, the St. Lawrence River that has limited potential for gas since the Utica and well completion) and through the Department of Environment for Shale actually outcrops on the north shore of the St. Lawrence and is

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 10 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx

Fig. 5. Spatial distribution of the Utica Shale thermal maturity (adapted from Séjourné et al., 2013).

usually too close to the surface to maintain adequate pressure. The area into storage reservoirs. Presently, there is no natural gas production in under permits for exploration includes the geological province of the St. Quebec. Lawrence Platform and the western reach of the outermost Appalachian Current exploration permits for oil and gas exploration in the entire domain (External Humber Zone; Lavoie, 2008), extending from Quebec Province of Quebec cover 31 160 km2 (7.7 million acres); most of the City south-westward to Montreal and southward towards the United permits appear to belong to joint ventures. In total, more than 450 States. The geological setting of the St. Lawrence Platform, as well as wells have been drilled in Quebec since the 1860s, of which 280 (62%) characteristics of the Utica Shale, are presented in detail in Lavoie are located in the St. Lawrence Platform. The Utica Shale subsurface et al. (2013, this issue). thermal domain is mostly dominated by dry gas conditions, although Gas seeps were identified in the 1950s–1960s on the northern side a liquid-rich (condensate and oil) zone is known in the NW area of of the St. Lawrence River (close to the very small reservoir exploited the St. Lawrence Platform (Fig. 5). Analyses available in the oil and in the late 1800s, see Section 2) and a small gas field in Quaternary gas database reveal that gas from the Utica Shale and overlying units sands was put into production from 1965 to 1976 (91 million m3 or (e.g., the conformably Utica-overlying Lorraine Group) is generally 3.2 Bcf, Pointe-du-Lac, near Trois-Rivières; Lavoie et al., 2009). Artisanal composed of at least 90% methane, the remainder being essentially gas wells were often drilled during this period and some of these are still composed of ethane, propane and carbon dioxide; little to no hydrogen being used for heating farm buildings. One conventional gas reservoir in sulfide has been reported (Séjourné et al., 2013). Ordovician dolostones was found by Shell in the early 1970s and pro- Industry still has to confirm the potential of the Utica Shale and its duction ceased in the early 1990s (163 million m3 or 5.7 Bcf; St. Flavien economical viability. Nevertheless, encouraging gas flow rates were gas field, 50 km south-west of Quebec City; Bertrand et al., 2003). Ther- reported in both vertical and horizontal wells. In 2006, two exploration mogenic gas from the Utica Shale was demonstrated to be present in the wells were drilled for a conventional gas target. This exploration St. Flavien field whereas a mixture of thermogenic and biogenic gas was program also had, as a secondary objective, to collect data to evaluate recognized in the Pointe-du-Lac reservoir (Lavoie et al., 2009; Saint- the shale for its geological character and shale gas potential. The two Antoine and Héroux, 1993). These two fields have since been converted first wells specifically targeting Utica shale gas were drilled in 2007.

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx 11

Twenty-five others were drilled between 2007 and 2010. In total, 18 of transporting chemicals used for fracking, or restrictions on injecting these wells were hydraulically fractured. In February 2010, an an- chemicals. Public concerns are mainly related to water contamination, nouncement was made that the St-Édouard-de-Lotbinière horizontal health impacts, nuisances (traffic and noise) and local economic im- well averaged 0.17 million m3/d (0.006 Bcf/d) of natural gas during pacts. Water quantity on the other hand, is usually not a problem. the first 21 days of the production test. However, due to several factors, Quebec receives over 1000 mm of annual precipitation and has many namely, the lack of hydrocarbon-oriented legislative and regulatory rivers and lakes; groundwater is, if not abundant everywhere, always frameworks together with the emplacement of very strict rules for sufficient to supply residential needs. In addition, there is a large saline fracking, including the need to receive social acceptability to conduct brackish groundwater zone in the northwestern part of the St. Lawrence any activity related to shale gas, resulted in the end of all exploration Platform (i.e. east and north of Montreal), as mentioned in Section 2.2, activities in the Utica Shale. One of the major permit holders subse- which could be used for this purpose since this groundwater has no quently wrote-off its investment in the Utica Shale in 2012. In the mean- other use. time, the low price of natural gas has led to a reorientation of industry, A brief historical background of gas exploration leading to the Utica which is generally now focusing its efforts on producing liquids (oil or Shale discovery and de facto moratorium can be summarized with the liquid-rich gas) and, in Quebec, interest has moved to Anticosti Island following timeline: where the Utica-coeval Upper Ordovician shale (the Macasty Shale) • 19th century: first industry reports of natural gas in Quaternary occurs in the oil and condensate thermal domains. The presence of a deposits overlying the Utica Shale. dense gas distribution network in the heart of the Utica play as well as • 1950s: First geological reports indicating gas in groundwater during a large local market represents, nonetheless, an economic advantage water well and oil & gas drilling. First suggestion to try hydraulic frac- since only short lateral connections from the well head to the pipelines turing on the Utica Shale in Quebec by Clark (1953). would be needed. • 1971–1992: Vertical and horizontal drilling in Villeroy (~45 km south- Few studies on the geological framework of the Utica Shale and west of Quebec City) for natural gas in fractured shales (Utica Shale overlying units have been conducted; the most comprehensive studies and Lorraine Group), no commercial production due to inadequate are from Thériault (2012a and b). Konstantinovskaya et al. (2012) technology at the time. focused on studying the actual stress regime in the St. Lawrence Plat- • 1973–2004: Drilling in Saint-Flavien (~30 km south-west of Quebec form and defined the conditions that would trigger reactivation of struc- City); 163 million m3 (5.7 Bcf) production from a conventional car- tural discontinuities, including faults. Séjourné et al. (2013),following bonate reservoir sourced by the Utica Shale; reservoir connected the initial deep seismic reinterpretation of Castonguay et al. (2006), through horizontal well drilling, now converted for gas storage. developed conceptual tectono-stratigraphic cross-sections of the Utica • 2006: Two companies (Talisman and Junex) drill wells through the Shale and overlying units that include the main geological constraints Utica Shale, targeting underlying conventional reservoirs; first wells (structural discontinuities, and depth/thickness variations) to be analyzed for shale gas potential in Quebec after the Villeroy of the region targeted by the industry for shale gas development. attempts. Séjourné et al. (2013) have also synthesized available information to • 2007: First two wells (Gastem) fully dedicated to test the potential of highlight regions or types of data with little or no information to guide the Utica Shale; first two hydraulic fracs on vertical wells (Forest Oil, future research work devoted, among other things, to evaluate the cap partner). rock integrity above the Utica Shale. These authors have compiled • 2008: First three horizontal wells drilled and frac-stimulated and first data from water wells and oil and gas wells. They present tables pro- public release of results and resource estimates (Forest Oil). viding areal extent, number of oil and gas wells, and the number of • 2009: First public protest: a letter is sent to the government by a group several types of analyses (e.g. gas and water shows, XRD, drill stem preoccupied mainly by air quality. Release of the movie Gasland. tests, production tests, and cores) available in each hydrogeological • 2010: Public hearings/consultations (BAPE) on shale gas development. study area being investigated within the PACES Program. This report • 2011: BAPE report. Announcement of new rules, permitting fracking mentions that some fluid analyses are available, but they have not under very strict conditions that contributed to the pause in industry been synthesized or statistically analyzed yet. Authors point out that activities and the de facto temporary moratorium. Creation of a strate- these analyses should significantly contribute to a regional hydro- gic environmental assessment committee (SEA). Start of hearings on geological assessment (such as the saline/fresh water interface depth Mining Law modifications. and location of dissolved gas in groundwater) and help constrain • 2013: The Quebec Ministry of Environment (MDDEFP, ministère du petrophysical models. They also underline the fact that the impact of Développement durable, de l'Environnement, de la Faune et des Parcs du the presence of many dykes on the regional fracturing conditions is Québec) released a draft regulation in May that should be adopted at poorly known and that there are no known under-pressurized reser- the end of 2013. voirs in this area. Reports from the Utica Shale operators indicate that • 2014: Forthcoming new hydrocarbon law and environmental regula- an overpressure regime is the norm, confirming that these deep shales tions announced by the Quebec Ministry of Natural Resources. are hydraulically isolated from the surface. Therefore, these authors conclude that, given the actual regional knowledge, surficial aquifers Mainly due to low gas prices and strong public concerns, shale gas should not be connected to the deep Utica Shale unit (in spite of numer- production seems unlikely in the near future in Quebec; moreover, the ous cases of gas in water wells reported since the 1950s), although the moratorium on fracking may last until 2018. On the other hand, shale presence of (undetected) structural discontinuities at the local scale oil exploration has commenced and hydraulic fracturing activities could alter these conditions. have been announced for the coming years on the largely unpopulated Public protest against shale gas development has led to the creation Anticosti Island. of nearly 100 local anti-shale gas protest groups. This opposition can be related to several factors: 1) shale gas is found in relatively populated 10. Conclusion areas; 2) Quebec does not have a history of large-scale oil and gas industry and has for years promoted its hydroelectricity as “green ener- There are abundant supplies of . Unconven- gy”; and 3) groundwater is an important water supply in this area, char- tional resources have doubled Canada's natural gas resource base and, acterized by numerous small municipalities. There were indeed in 2012 as exploration continues, this number could still increase. Presently, over 30 local (municipal or to regional levels) opposition groups, 3 large-scale production is occurring only in northeastern British Colum- provincial protest groups and 63 municipalities that have announced bia, where the population is sparse. Four plays are in production, of motions pertaining to no drill zones around water wells, limits on which the Horn River Basin and the Montney Play Trend are the most

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 12 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx productive. Modest exploitation of dry gas occurs in the Duvernay Basin, OIL AND GAS REPORTS 2011-1. http://www.em.gov.bc.ca/OG/Documents/ HornRiverEMA_2.pdf. Formation (Alberta), where liquids are also being produced at increas- BC Ministry of Energy and Mines, 2012. Summary of shale gas activities in Northeast ing rates. In British Columbia, the unconventional gas production repre- British Columbia 2011. Geoscience and Strategic Initiatives Branch, Oil and Gas sents nearly 60% of the total natural gas production in the province and Division. Oil and Gas report 2012-1, 19 p. BC Oil and Gas Commission, 2012. Investigation of observed seismicity in the Horn River about 90% of the drilling activity, while shale gas production in Alberta Basin. 29 pp. Available at: http://www.bcogc.ca/publications/reports. represents only about 0.1% of the total provincial gas production and Beaudry, C., Malet, X., Lefebvre, R., Rivard, C., 2011. Délimitation des eaux souterraines usually represents a by-product of the liquid production. Very few saumâtres en Montérégie Est, Québec, Canada. Commission géologique du Canada, shale wells have been drilled in eastern Canada so far. Nonetheless, Dossier public 6960. http://dx.doi.org/10.4095/289123 (26 pp.). Bertrand, R., Chagnon, A., Duchaîne, Y., Lavoie, D., Malo, M., Savard, M.M., 2003. one well is currently producing in the McCully Field (southern New Sedimentologic, diagenetic and tectonic evolution of the Saint-Flavien gas reservoir Brunswick) from the Frederick Brook Member shale (since 2008). Con- at the structural front of the Quebec Appalachians. Bull. Can. Petrol. Geol. 51, – tinued exploration and development of natural gas from the Frederick 126 154. British Columbia Ministry of Energy and Mines, 2005. Gas Shale Potential of Devonian Strata, Brook Shale is planned in the future with renewed drilling and fracking northeastern British Columbia. Petroleum Geology Special Paper 2005-1 (1 CD). in the McCully gas field area in order to determine feasibility of com- CAPP, 2012. Library and statistics/tables. http://www.capp.ca/library/statistics/handbook/ mercial development. The Quebec Utica Shale economic production pages/statisticalTables.aspx?sectionNo=1. Castonguay, S., Dietrich, J., Shinduke, R., Laliberté, J.-Y., 2006. Nouveau regard sur potential is still to be determined, but promising results were obtained l'architecture de la plate-forme du Saint-Laurent et des Appalaches du sud du Québec from 2006 to 2010. A moratorium on shale gas exploration and hydrau- par le retraitement des profils de sismique réflexion M-2001, M-2002 et M-2003, lic fracturing is, however, currently in place in southern Quebec. Geological Survey of Canada, Open File 5328. Cheung, K., Mayer, B., 2007. Chemical and isotopic characterization of shallow Hydrocarbon exploration and production operations involve var- groundwater from selected monitoring wells in Alberta: Part I: 2006–2007, prepared ious surface and subsurface risks of degrading groundwater quality for Alberta Environment. 76 pp. http://environment.gov.ab.ca/info/library/8148.pdf. and these hazards need to be assessed and minimized. Driven by im- Clark, T.H., 1953. Geological log of the Lozo & Joseph well # 1. SIGPEG, report 1953OA076- 02. (6 pp. Available at: internet http://sigpeg.mrnf.gouv.qc.ca). proved operational techniques and strategies, competition for water Corridor Resources Inc., 2009. Corridor reports results of independent shale gas resource access and public concerns, the industry is evolving toward increasingly study (Press Release, June 26, 2009). environmentally-conscious practices (e.g. use of saline water and Council of Canadian Academies, 2009. The sustainable management of groundwater in “green” additives, groundwater monitoring, flowback and produced Canada. 254 pp. 978-1-926558-11-0 (http://www.scienceadvice.ca/en/publications/ assessments.aspx). water recycling, disclosure of fracking fluid additives), although these Davies, R.J., Mathias, S.A., Moss, J., Hustoft, S., Newport, L., 2012. Hydraulic fractures: how requirements, in many cases, are not regulated yet. Many research far can they go? Mar. Pet. Geol. 37, 1–6. projects at different scales and on various topics related to environmen- Duchaine, Y., Tourigny, Y., Beaudoin, G., Dupuis, C., 2012. Potentiel en gaz naturel dans le Groupe d'Utica, Québec. Rapport d'étude P-1_a_UL. 85 pp. accessible at: http://ees- tal issues of shale gas have been initiated in the last few years at the gazdeschiste.gouv.qc.ca/wordpress/wp-content/uploads/2012/11/Rapport-etude-P- Canadian federal and provincial levels, as well as in universities. These 1_a_UL.pdf. should provide an impartial scientific base to support the sustainable Dunn,L.,Schmidt,G.,Hammermaster,K.,Brown,M.,Bernard,R.,Wen,E.,Befus,R.,Gardiner, S., 2012. The Duvernay Formation (Devonian): sedimentology and reservoir charac- use of groundwater related to shale gas development. terization of a shale gas/liquids play in Alberta, Canada. Canadian Society of Petro- leum Geologists, Annual Convention, Calgary (http://www.cspg.org/documents/ Conventions/Archives/Annual/2012/core/280_GC2012_The_Duvernay_Formation. Acknowledgments pdf). ERCB, 2012a. ERCB Investigation Report: Caltex Energy Inc., hydraulic fracturing incident, The authors would like to thank the following individuals for their 16-27-068-10W6M, September 22, 2011. http://www.ercb.ca/reports/IR_20121220_ Caltex.pdf. help and willingness to provide information and access to data and ERCB, 2012b. Midway Energy Ltd. hydraulic fracturing incident: interwellbore communi- statistics for this publication: Annie Daigle from the NB Department of cation January 13, 2012. ERCB Investigation Report. Red Deer Field Centre (http:// Environment; John Drage and Adam MacDonald from the NS Depart- www.ercb.ca/reports/IR_20121212_Midway.pdf.). ERCB/AGS, 2012. Summary of Alberta's shale- and siltstone-hosted hydrocarbon resource ments of Natural Resources and Energy, respectively; Dr. Kevin Parks, potential. Open File report 2012-06. (126 pp.). Tony Lemay, Andrew Beaton, Marie-Anne Kirsh, and Dean Rockosh Ferguson, M.L., Eichelberger, P.B. Hallock, Qiu, J.K., Roell, R.L., 2013. Innovative friction from the Alberta Energy Regulator (AER, formerly ERCB); Christopher reducer provides improved performance and greater flexibility in recycling highly Adams and Fillippo Ferri from BC Ministry of Energy (Mines and Natural mineralized produced brines, Society of Petroleum Engineers (SPE). 978-1-61399- 259-3 (abstract available at: http://www.onepetro.org/mslib/app/Preview.do? Gas); Kei Lo from the SK Water security Agency; Dan Cowan from the paperNumber=SPE-164535-MS&societyCode=SPE). Energy Sector of Natural Resources Canada; Sylvain Gagné of UQAM, Ferri, F., Hickin, A.S., Reyes, J., 2012. Horn River Basin-equivalent strata in Besa River Dan Palombi from the Alberta Geological Survey, and Mike Wei of the Formation shale, Northeastern British Columbia (NTS 094K/15). Geoscience Reports 2012. British Columbia Ministry of Energy and Mines, pp. 1–15. BC Water Protection and Sustainability Branch. Special thanks go to Fisher, K., Warpinski, N., 2012. Hydraulic-fracture-height growth: real data. SPE Prod & François Létourneau for his work on the figures, to Dr. Alfonso Rivera Oper 27 (1), 8–19 (SPE-145949-PA. http://dx.doi.org/10.2118/145949-PA). from the GSC-QC for his review of the text on on-going research at the Gassiat, C., Gleeson, T., Lefebvre, R., McKenzie, J., 2013. Hydraulic fracturing in faulted sedimentary basins: numerical simulation of potential long term con- GSC, and to Marianne Molgat from for her valuable tamination of shallow aquifers. Water Resour. Res. http://dx.doi.org/10.1002/ comments and information. The authors also wish to thank Dr. Steve 2013WR014287. Grasby (GSC-Calgary) for his careful internal review, as well as the Gibson, D.W., Barclay, J.E., 1989. Middle Absaroka Sequence, The Triassic Stable Craton. In: Ricketts, B.D. (Ed.), Western Canada sedimentary basin, a case history. Canadian Guest Editor, Daniel J. Soeder, and an anonymous reviewer for their Society of Petroleum Geologists, Special Paper, 30, pp. 219–231. valuable comments. GWPC & ALL Consulting, 2009. Modern shale gas development in the United States: a primer. U.S. DOE. (96 pp. http://www.netl.doe.gov/technologies/oil-gas/publications/ epreports/shale_gas_primer_2009.pdf). References Hamblin, A.P., 2006. The “Shale Gas” concept in Canada: a preliminary inventory of possibilities. Geological Survey of Canada, Open File 5384. (103 pp.). (S&T)2 Consultants Inc., 2011. Shale gas update for GHGENIUS. 26 pp. available at http:// Hamblin, A.P., Rust, B.R., 1989. Tectono-sedimentary analysis of alternate-polarity half- www.ghgenius.ca/reports.php. graben basin-fill successions: Late Devonian–Early Carboniferous Horton Group, Al, T.A., Leblanc, J., Phillips, S., 2013. A study of groundwater quality from domestic wells Cape Breton Island, Nova Scotia. Basin Res. 2, 239–255. in the Sussex and Elgin regions, New Brunswick: with comparison to deep formation Ibrahimbas, A., Riediger, C., 2005. Thermal maturity and implications for shale gas poten- water and gas from the McCully Gas Field. Geological Survey of Canada, Open File tial in northeastern British Columbia and northwestern Alberta. Seventh Unconven- 7449. http://dx.doi.org/10.4095/292762 (40 pp.). tional Gas Conference, Calgary, Alberta. Allan, J., Creaney, S., 1991. Oil families of the Western Canada Basin. Bull. Can. Petrol. Geol. Jackson, R.E., Gorody, A.W., Mayer, B., Roy, J.W., Ryan, M.C., Van Stempvoort, D.R., 2013. 39, 107–122. Groundwater protection and unconventional gas extraction: the critical need for BAPE, 2011. Développement durable de l'industrie des gaz de schiste au Québec. Rapport field-based hydrogeological research. Ground Water 51 (4), 488–510. 273 d'enquête et d'audience publique. (28 février 2011, 323 pp.). Johnson, E.G., Jonson, L.A., 2012. Hydraulic fracture water usage in northeast British BC Ministry of Energy and Mines, National Energy Board, 2011. Ultimate potential for Columbia: locations, volumes and trends. Geoscience Reports 2012. British Columbia unconventional natural gas in Northeastern British Columbia's Horn River Ministry of Energy and Mines, pp. 39–63.

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004 C. Rivard et al. / International Journal of Coal Geology xxx (2013) xxx–xxx 13

Konstantinovskaya, E., Malo, M., Castillo, D.A., 2012. Present-day stress analysis of the St. Podruski, J.A., Barclay, J.E., Hamblin, A.P., Lee, P.J., Osadetz, K.G., Procter, R.M., Taylor, G.C., Lawrence Lowlands sedimentary basin (Canada) and implications for caprock 1988. Conventional Oil Resources of Western Canada. Geological Survey of Canada,

integrity during CO2 injection operations. Tectonophysics 518–521, 119–137. Paper. paper no. 87-26, (149 pp.). Lavoie, D., 2008. Appalachian foreland basin in Canada. In: Hsü, K.J., Miall, A.D. (Eds.), Precht, P., Dempster, D., 2012. Jurisdictional Review of Hydraulic Fracturing Regulation. Sedimentary basins of the World. Vol. 5 Sedimentary basins of the World—USA and Final report for Nova Scotia Hydraulic Fracturing Review Committee. Nova Scotia Canada. Elsevier Science, pp. 65–103. Department of Energy and Nova Scotia Environment (http://www.gov.ns.ca/nse/ Lavoie, D., Dietrich, J., Pinet, N., Castonguay, S., Hannigan, P., Hamblin, T., Giles, P.S., 2009. pollutionprevention/docs/Consultation.Hydraulic.Fracturing-Jurisdictional.Review. Hydrocarbon resource assessment, Paleozoic basins of eastern Canada. Open File pdf). 6174, Geological Survey of Canada (275 pages). Québec, 2011. Gestion gouvernementale de l'exploration et de l'exploitation des gaz de Lavoie, D., Chen, Z., Thériault, R., Séjourné, S., Lefebvre, R., Malet, X., 2013. Hydrocarbon schiste, Rapport du Vérificateur général du Québec à l'Assemblée nationale pour Resources in the Upper Ordovician Black Shales in Quebec (Eastern Canada): From l'année 2010–2011. Rapport du commissaire au développement durable. (36 pp., Gas/Condensate in the Utica to Oil in the Macasty. (http://www.searchanddiscovery. http://www.vgq.qc.ca/fr/fr_publications/fr_rapport-annuel/fr_2010-2011-CDD/ com/documents/2013/50856lavoie/ndx_lavoie.pdf.). fr_Rapport2010-2011-CDD-Chap03.pdf). Lavoie, D., Rivard, C., Lefebvre, R., Séjourné, S., Thériault, R., Duchesne, M.J., Ahad, J., Wang, Raynauld, M., Crow, H., Fagnan, N., Lefebvre, R., Gloaguen, E., Molson, J.W., Benoit, N., B., Benoit, N., Lamontagne, C., 2014. Geological and hydrogeological assessments of 2013. Caractérisation des conditions hydrogéologiques au-dessus du réservoir the upper Ordovician Utica Shale in southern Québec: the cornerstone of the evalua- pétrolier d'Haldimand, Gaspé, Québec. GeoMontreal2013, conference proceeding, tion of potential groundwater risks. Int. J. Coal Geol. (Special issue on potential envi- 66th Canadian Geotechnical Conference and the 11th Joint CGS/IAH-CNC Groundwa- ronmental impacts of unconventional fossil energy development, in this issue, (add ter Conference, Montreal, Quebec, Canada, Sept. 29 to Oct. 3, 2013. pages)). Rivard, C., Molson, J.W., Soeder, D.J., Johnson, E.G., Grasby, S.E., Wang, B., Rivera, A., 2012. Lemay, T.G., Guha, S., 2009. Compilation of Alberta groundwater information from A review of the November 24–25, 2011 shale gas workshop, Calgary, Alberta—2. existing maps and data sources. ERCB/AGS Open File Report 2009-02, ISBN 978-0- Groundwater Resources, Geological Survey of Canada, Open File 7096. http:// 7785-6969-5 (http://www.ags.gov.ab.ca/publications/OFR/PDF/OFR_2009_02.pdf). dx.doi.org/10.4095/290257 (205 pp.). Martel, A.T., Gibling, M.R., 1996. Stratigraphy and tectonic history of the Upper Devonian Rivera, A., Crowe, A., Kohut, A., Rudolph, D., Baker, C., Pupek, D., Shaheen, N., Lewis, M., to Lower Carboniferous Horton Bluff Formation, Nova Scotia. Atl. Geol. 32, 13–38. Parks, K., 2003. Canadian Framework for Collaboration on Groundwater. In: Natural Mossop, G.D., Wallace-Dudley, K.E., Smith, G.G., Harrison, J.C., 2004. Sedimentary Basins of Resources Canada, Government of Canada (Ed.), (ftp://ftp2.cits.rncan.gc.ca/pub/ Canada. Geological Survey of Canada, Open File 4673. geott/ess_pubs/214/214620/gid_214620.pdf.). Nash, K.M., 2010. Shale Gas Development. Nova Science Publishers, Inc., , USA Roy, J.M., Ryan, M.C., 2013. Effects of unconventional gas development on groundwater: a (161 pp.). call for total dissolved gas pressure field measurements. Goundwater 51 (4), National Energy Board, 2011. ultimate potential for unconventional natural Gas in North- 480:482–480:. eastern British Columbia's Horn River Basin. Oil and Gas report 2011-1. (39 pp.). Saint-Antoine, P., Héroux, Y., 1993. Genèse du gaz naturel de la région de Trois-Rivières, National Energy Board, 2012. Marketable natural gas production in Canada. http://www. basses-terres du Saint-Laurent et de Saint-Flavien, Appalaches, Québec, Canada. one-neb.gc.ca/clf-nsi/rnrgynfmtn/sttstc/mrktblntrlgsprdctn/mrktblntrlgsprdctn-eng. Can. J. Earth Sci. 30, 1881–1885. html. Séjourné, S., Lefebvre, R., Malet, X., Lavoie, D., 2013. Synthèse géologique et New Brunswick, 2013. Responsible environmental management of oil and natural gas hydrogéologique du Shale d'Utica et des unités sus-jacentes (Lorraine, Queenston et activities in New Brunswick Rules for Industry. 99 pp. http://www2.gnb.ca/content/ dépôts meubles), Basses-Terres du Saint-Laurent, Province de Québec. Commission dam/gnb/Corporate/pdf/ShaleGas/en/RulesforIndustry.pdf. géologique du Canada, Dossier Public 7338 (165 pp.). Nowamooz, A., Lemieux, J.M., Molson, J., Therrien, R., 2013a. Numerical investigation of Soeder, D., 2013. Groundwater Protection During Shale Gas Development. Abstract, methane and formation fluid leakage along shale gas extraction wells: application Americana, Salon international des technologies environnementales, 19–21 mars to the St-Lawrence Lowland basin. GeoMontreal 2013, 66th Canadian Geotechnical 2013, Montreal, Québec, Canada. Conference and the 11th Joint CGS/IAH-CNC Groundwater Conference, Montreal, St. Peter, C.J., Johnson, S.C., 2009. Stratigraphy and structural history of the Late Paleozoic Quebec, Canada, Sept. 29 to Oct. 3, 2013. Maritimes basin in southeastern New Brunswick, Canada. New Brunswick Department Nowamooz, A., Lemieux, J.M., Therrien, R., 2013b. Modélisation numérique de la of Natural Resources; Minerals, Policy and Planning Division. Memoir 3 (348 pp.). migration du méthane dans les Basses-Terres du Saint-Laurent. Étude E3-10 du Switzer, S.B., Holland, W.G., Christie, D.S., Graf, G.C., Hedinger, A.S., McAuley, R.J., plan de réalisation de l'évaluation environnementale stratégique sur les gaz de Wierzbicki, R.A., Packard, J.J., 1994. Devonian Woodbend-Winterburn strata of the schiste, internal report.Département de géologie et de génie géologique, Université Western Canada Sedimentary Basin. Geological Atlas of the Western Canada Sedi- Laval (100 pp.). mentary Basin, G.D. Mossop and I. Shetsen (comps.). Canadian Society of Petroleum NRCan, 2011. Energy. websites http://www.nrcan.gc.ca/statistics-facts/energy/895. Geologists and Alberta Research Council, pp. 165–202. Ouellet, M., Lamontagne, C., Labbé, J.-Y., 2011. Le programme d'acquisition de connaissances Thériault, R., 2012a. Caractérisation du Shale d'Utica et du Groupe de Lorraine, Basses- sur les eaux souterraines du Québec et ses retombées. Geohydro2011, Joint IAH-CNC, Terres du Saint-Laurent-Partie 2: Interprétation géologique. Ministère des Ressources CANQUA and AHQ conference, Quebec City, Canada, August 28–31, 2011 (7 pp.). naturelles et de la Faune, SIGEOM, DV 2012-04 (80 pp.). Peel, M., Lefebvre, R., Gloaguen, E., Lauzon, J.-M., 2013. Hydrogeological assessment of Thériault, R., 2012b. Caractérisation du Shale d'Utica et du Groupe de Lorraine, Basses- western Anticosti Island related to shale oil exploitation, extended abstract. Terres du Saint-Laurent-Partie 1: Compilation des données. Ministère des Ressources GeoMontreal2013, 66th Canadian Geotechnical Conference and the 11th Joint CGS/ naturelles et de la Faune, SIGEOM, DV 2012-03. (212 pp.). IAH-CNC Groundwater Conference, Montreal, Quebec, Canada, Sept. 29 to Oct. 3, 2013. Tilley, B.J., Muehlenbachs, K., 2012. Isotope reversals and universal stages and trends of Pinti, D.L., Gelinas, Y., Larocque, M., Barnetche, D., Retailleau, S., Moritz, A., Helie, J.F., gas maturation in sealed, self-contained petroleum systems. Chem. Geol. 339, Lefebvre, R., 2013. Concentrations, sources et mécanismes de migration préférentielle 194–204. des gaz d'origine naturelle (méthane, hélium, radon) dans les eaux souterraines des Tilley, B.J., McLellan, S., Hiebert, S., Quartero, B., Veilleux, B., Muehlenbachs, K., 2011. Gas Basses-Terres du Saint-Laurent. Report of study E3-9 for the Comité d'évaluation isotope reversals in fractured gas reservoirs of the western Canadian Foothills: environnementale stratégique pour le gaz de schiste au Québec (94 pp.). mature shale gases in disguise. AAPG Bull. 95, 1399–1422.

Please cite this article as: Rivard, C., et al., An overview of Canadian shale gas production and environmental concerns, Int. J. Coal Geol. (2013), http://dx.doi.org/10.1016/j.coal.2013.12.004