Ground Water Resources of British Columbia
Chapter 10 — Ground Water Resources of the Plateaus and Highlands Ground Water Regions
10.3 ALBERTA PLATEAU
by
K. Ronneseth
PHYSIOGRAPHIC SETTING
Holland (1964) quotes that the Interior Plains in northeastern British Columbia are represented by the Alberta Plateau and its subdivision, the Nelson Lowland (Figures 8.2 and 8.7). Both comprise approximately 10% of the land area of British Columbia. Lying east of the Rocky Mountains, the region is underlain by sedimentary rocks which are flat lying and gently dipping. The Alberta Plateau, to be discussed in this section, are upland areas generally standing between 3,000 - 4,000 feet and are flat or gently rolling.

Figure 8.2 Ground water regions

Figure 8.7 Ground water regions of the Plateaus and Highlands
The region is drained and incised by the Liard and Peace Rivers and their tributaries. Peak discharge occurs at the time of maximum snow and/or glacial melt and is complimented by precipitation which reaches its maximum in the summer months. The drainage is often poorly organized in the upland areas where large areas of muskeg exist. Refer to Figure 8.7 for the names and locations of major rivers found in the study area.
The majority of the Plateau is heavily wooded except along the Peace River (below 760 m elevation) which is only lightly wooded and under cultivation.
BEDROCK GEOLOGY
The Alberta Plateau is the product of numerous cycles of broad subsidence, marine and freshwater sedimentation, emergence and erosion cycles. The geology includes a succession of strata that range from Cambrian to Upper Cretaceous in age. It is the Cretaceous rocks of the Mesozoic Era that outcrop in Plateau Region. The rock types of importance from a hydrogeological standpoint, are the Dunvegan Formation (sandstones, shales and siltstones; minor conglomerates; few thin coals; largely non-marine; over 365 m thick) of Upper Cretaceous age and the Fort St. John Group (predominantly shales of marine origin; mudstones, sandstones, conglomerates and minor siltstones; 1500 - 1800 m in thickness) of Lower Cretaceous age.
For further information on bedrock geology, refer to Kindle (1950); Irish (1958) and (1961); Muller (1961); Thompson (1977); and Stott (1968) and (1982).
SURFICIAL GEOLOGY
The initial pattern of topography was developed during the Tertiary Period by mass wastage and fluvial action. Post orogenic and recent uplifts accelerated these processes (Hughes, 1967). The regime and wasting of glacial ice during the Pleistocene further modified these landforms and are responsible for the majority of the unconsolidated deposit found within the study area today. It was this Quaternary activity which has played an important role in controlling movement, storage and availability of ground water (Mathews, 1978).
In the latter part of the Quaternary, the study area has experienced at least three major advances of Continental and Cordilleran ice. It was the Continental (or Laurentide) ice sheets which dominated the Plains region during the Pleistocene. The greatest extent of Cordilleran ice occurred about 15,000 years ago when it overrode the foothills, then extending eastward it probably abutted the Continental ice sheet occupying the plains regions. Much of the Plains region experienced cyclical deposition sequences of fluvial gravels during non-glacial periods; lacustrine sands, silts and clays resulting from aggradation and ponding of the Peace River by advancing Continental ice; till deposition by the ice itself; and then sands, silts and clays deposited in a series of ice damned lakes (named Lake Peace) during the retreating stages of Continental glaciation (Mathews, 1978).
As the eastern front of the Cordilleran ice retreated from the Plains, back to the Foothills and the Rocky Mountains, it was responsible for the deposition of tills, glacial fluvial sands and gravels and glaciolacustrine sediments in numerous localities throughout the Plains/Foothills region.
Throughout the study area, post glacial times saw many of the former deposits removed by the fluvial action of today's streams and rivers. Remnants of these interglacial and glacial sediments can still be viewed throughout the study area in the stream cut trenches. With a few exceptions, the courses of streams fell within the boundaries of the interglacial stream trenches (Mathews, 1978). Many of these boundaries, however, along with other stream channels are as yet buried under many of the Quaternary sediments. Table 10.1 provides a stratigraphic framework of unconsolidated deposits and a chronology of Quaternary events for the study area. For further information on surficial deposits, the reader is referred to Mathews (1978), Reimchen (1980) and Ronneseth (1983).
GROUND WATER POTENTIAL
As of 1988, approximately 900 water wells records are on file with the Provincial Government of B.C. for the area. The following information is based on a report (Ronneseth, 1983) where just over 700 water wells were investigated.
The water wells and test holes range in depth from 4 to 213 m and average 46 m deep. Of these wells about 40% are reported to be completed in bedrock, about 305 are reported to be completed in the surficial deposits and completion of the remaining 30% is not known.
Table 10.1 Stratigraphy and Pleistocene Events for the Plains Region of the Study Area
Years B.P.
(not to
scale) |
Major
Pleistocene
Event |
Major Surficial
Deposits |
Reported Thickness of Deposits |
10,000 |
Post glacial period |
Lacustrine Fluvial
Colluvial |
Modern alluvium: up to 20 metres, apex of alluvial fans up to 30 metres |
15,000 |
Last major continental ice advance |
Glaciofluvial
Glaciolacustrine
Till
Glaciolacustrine |
0 - 5 metres
0 - 90 metres
0 - 24 metres
0 - 122 metres |
27,000
45,000 |
Last interglacial interval |
Fluvial |
28 - 30 metres |
55,000 |
Continental glacial period |
Glaciolacustrine?*
Till
Glaciolacustrine |
?
0 - 15 metres |
65,000
75,000 |
Early interglacial interval |
Fluvial |
0 - 55 metres |
80,000 |
Early continental glacial period |
A few pebbles of eastern origin were found in the early interglacial fluvial gravels |
? |
95,000
225,000 |
Preglacial period? |
Fluvial |
Approximately 8 metres |
* Though it is probable that lacustrine sediments were laid down during the retreat of this ice, none have been recognized (Mathews, 1978)
** The accuracy of the dating is very subjective on dates earlier than 27,000 years B.P. The only radiometrically dated sample (up to 1978) was 27,400 to 580 years B.P. from a gravel pit near Taylor, B.C. (Mathews, 1978)
The yields of bedrock wells are known for one-quarter of the wells and range from a few pails per day to 6.3 L/s (litres per second) and average 0.63 L/s. A study of yields of bedrock wells also shows that wells obtaining water supplies from sandstone commonly produce about 50 percent more water than wells drawing ground water from shale, average 0.64 L/s and 0.44 L/s, respectively.
Well yields were reported for only 10 percent of wells completed in the surficial deposits and these range from a few pails per day up to 10.1 L/s. The wells completed in sand and gravel commonly have much higher yields, up to a maximum reported yield of 10.1 L/s, than wells completed in clay or silt with a maximum reported yield of 0.5 L/s.
POTENTIAL GROUND WATER PRODUCING REGIONS
Ground water appears favourable as a water supply source for specific regions within the study area.
Investigations to date identify certain sandstone units located in the Upper Cretaceous strata (primarily the Dunvegan Formation) which represents a bedrock aquifer with the potential of yielding up to 0.6 L/s of domestic ground water supplies (Mathews, 1955 and Callan, 1973). Other rock types which locally may have the potential to yield ground water supplies are sandstone and limestone formations such as those underlying the Dunvegan Formation. The possibility of obtaining greater quantities of ground water from the bedrock by deeper drilling should also be given consideration if other water supply options are limited.
Although the Cretaceous rocks of the study area represent potential aquifers for domestic water supplies, they are limited in their ability to meet irrigation, commercial/industrial or municipal water requirements. To fulfill such requirements would entail locating and developing a viable sand and gravel aquifer. Table 10.2 lists various unconsolidated surficial deposits found in the study area, their genetic origin, probably composition and the geomorphological feature they are normally associated with. This table has been divided into two sections; those deposits which make good aquifer materials and those which would make poor ones. The locations of these two categories can be found in Map . This map identifies potential aquifer regions as well as regions which may be sensitive to pollution sources because of the presence of overlying highly permeable materials. It should be understood, however, that these categories are general in nature and, as such, the permeability of the unconsolidated sediments can vary both areally and with depth. For example, viable aquifer sediments or conditions may be located beneath overlying low permeable materials and low permeable materials may underlie sediments which would make good aquifers.
Table 10.2 Unconsolidated Surficial Deposits
DEPOSIT |
COMPOSITION |
GEOMORPHOLOGICAL FEATURE |
Good Aquifer Materials
Recent alluvium
Terrace deposits
(interglacial and recent)
Fluvial glacial
Fluvial glacial
Colluvial
Eolian
|
Gravel, sand and minor silt
Gravel, sand and minor silt
Gravel and sand
Gravel and sand
Boulders, gravel, sand, silts and some clays
Fine sands and silts
|
At or near present stream level
River terraces
Deltaic features; aprons
Kames; spillway floor deposits; littoral and deltaic deposits; eakers
Fans; aprons
Parabolic dunes
|
Poor Aquifer Materials
Glaciolacustrine
Morainal
Organic
|
Clay, silt, minor sand and shoreline gravel
An assortment of dissimilar ingredients ranging from clay to boulders in size
Silt, sand, clay and peat
|
Pre and post glacial lake beds
Modern swamps, fens and ponds
|
|
Though ground water may be found in any of the sand and/or gravel deposits listed in Table 10.2, some of the littoral, deltaic and other deposits may be too thin to provide adequate storage for any purpose other than domestic supplies (Mathews, 1978). Sand and gravel deposits located on buried bedrock channels, larger fans and delta kames, and spillway floor deposits offer some potential of yielding greater than domestic quantities of ground water. The deposits which have the best potential for yielding high quantities of ground water are recent alluvium adjacent to present day streams and rivers, some stream cut terraces (where excessive drainage is not a problem) and interglacial gravels located at depth.
According to Mathews (1978), interglacial gravels (generally less than 100 m below the surface) supplied a moderate amount of potable subartesian water to the town of Fort St. John prior to 1952. He identified an area near Clayhurst from the Alberta border west to Golata Creek which may yield ground water from interglacial gravels similar to the Fort St. John aquifer gravels. Data collected by the Ground Water Section shows a confined gravel aquifer 20 to 45 m below ground surface in the Clayhurst area. In corroboration with Mathew's finding, there are five wells penetrating 5 to 18 m into the saturation zone and yielding from 1.3 to 6.3 L/s. Total aquifer thickness is not known. Three other wells completed in the Clayhurst area were also reported to be higher than average yielding wells for the Plateau region. Two of these well logs reported yields of 1.9 and 3.2 L/s from sandstone at a depth of 122 and 140 m, respectively. The third well log reported a yield of 6.3 L/s from the top of a sandstone formation 13 m below ground surface.
With clay being the overlying material, probable water source might either be a weathered and/or fractured zone in the upper portion of the sandstone formation or a layer of gravel may be lying upon the sandstone formation and was not identified because of the drilling method utilized.
Though the sustained yield for these two or more aquifer zones is unknown, it does exemplify that the Plains region may still have developable ground water supplies of consequence.
GROUND WATER QUALITY
The available data show the quality of ground water from aquifers in the bedrock and in the surficial deposits of the Alberta Plateau to be quite variable (Ronneseth, 1983).
The ground water found in bedrock may be described as mainly calcium and magnesium bicarbonate types with some calcium and magnesium sulfate and sodium bicarbonate types. The total dissolved solids (TDS) content of the ground water was not analyzed for most samples. The following numbers were estimated from available data.
In an area covered by Townships 85 to 87 and ranges 17 to 20, west of the 6th Meridian, to the north of the Peace River, TDS may range from over 2,000 mg/L (milligrams per litre) to about 6,600 mg/L. The ground waters may be described as mainly calcium and magnesium bicarbonate types.
South of Township 85 to Swan Lake on the British Columbia - Alberta border the TDS content of ground waters range from about 900 to 3,300 mg/L, with many probably less than 1,500 mg/L. The ground waters again may be described as mainly calcium and magnesium bicarbonate type, with some calcium and magnesium sulfate mostly in an area near Dawson Creek.
Ground water can be categorized as very hard to extremely hard north of Township 84 and in the Dawson Creek - Swan Lake area, commonly ranging from 1,000 to 2,5000 mg/L. Elsewhere ground water may be considered moderately hard to hard commonly ranging from about 100 to 500 mg/L. The iron content of ground water is quite variable throughout the area and is commonly greater than 1.0 mg/L. South of the Peace River and up to 0.6 mg/L north of this river.
From the incomplete data on chemical analyses for ground water in the surficial deposits, it would appear that the total dissolved solids content in ground waters may range from about 1,000 mg/L to about 2,500 mg/L north of the Peace River and from about 1,000 to 5,000 mg/L south of the Peace River. While the ground water may be described as mainly calcium and magnesium or sodium bicarbonate types, there are some sulfate types in the Dawson Creek - Swan Lake area and near Groundbirch. Ground water in the surficial deposits is less hard than in the bedrock. Bedrock ground water may be described as moderately hard to hard. The hardness ranges mainly from moderately hard at 200 to 600 mg/L to very hard at 1,000 to 2,000 mg/L. The concentration of iron ranges from about 1 to 10 mg/L south of the Peace River and up to 0.6 mg/L north of the Peace River.
POLLUTION OF GROUND WATER
The pollution of ground water is usually a local problem. Potential sources for ground water pollution include domestic septic tanks, the use of fertilizers, herbicides and pesticides, municipal sewage ponds, landfill sites, waste water from industrial plants, areas where storage, handling and transport of petroleum products and special wastes and the disposal of gas field brines.
Ground water occurs under confined or unconfined conditions. Unconfined or water table aquifers are areas where the potential for pollution may occur because of the occurrence of highly permeable materials (i.e. sands and gravels) overlying the water table. It would be advantageous to avoid disposing of wastes in areas where these conditions exist.
GROUND WATER USE
Available information suggests that ground water resources within the Plateau Region were historically developed to meet domestic, agricultural (primarily for watering stock animals), commercial/industrial, and municipal water use (Ronneseth, 1983). Of the 258 plotted wells (in 1983) which reported intended well water use, 70 percent were reported for domestic use, 23 percent for agriculture, 4.3 percent for commercial/industrial and 2.37 percent for municipal requirements. Water well records from 1980/81 report increased ground water development activity by the commercial/industrial sector such as oil field injection in the petroleum industry of the Plateau region. Of over 700 wells which are on file with the Ground Water Section, approximately 9 percent were reported to be either filled in, abandoned or put to some use other than as a water supply source; the reasons stated included cave-ins, inadequate yield and poor water quality.
SUMMARY
Cretaceous sedimentary rocks of the Mesozoic Era, outcrop in the Plateau region. Glacial and post-glacial activity are responsible for the majority of the unconsolidated deposits found within the study area today. Many post and inter-glacial valleys or bedrock channels are buried beneath extensive Quaternary sediments and these features may be significant from a hydrogeological viewpoint.
Ground water has been developed primarily to meet domestic, livestock, municipal, and industrial requirements. Economic growth in the area has resulted in increased ground water development for municipal and industrial needs.
Average water well depth in the Plateau region is 46 m.
Ground water is usually able to meet domestic requirements throughout the region. Sandstone units of the Cretaceous Period are probably the most significant from a hydrogeological standpoint. Fluvial gravels adjacent to present day streams, fluvioglacial outwash sands and/or gravels and interglacial fluvial gravels offer the best potential for yielding greater than domestic quantities of ground water.
Some deterrents to ground water development include: sand and/or gravel deposits too thin to provide adequate storage, excessive drainage occurring in stream-out terraces, and ground water of unsatisfactory quality and/or too deep to be economically viable.
The chemical quality of ground water may be described as mainly of a calcium and magnesium bicarbonate type, with some calcium and magnesium sulphate and sodium bicarbonate types as well. Total dissolved solids range from about 900 to 6600 mg/L and the hardness of ground water ranges from about 1000 to 2500 mg/L in the Plateau region. The iron content is often above the recommended limit of 0.3 mg/L throughout the area.
As the region experiences increasing economic growth, the demand for ground water and the possibility of pollution will increase. Since much of the ground water is developed from water table aquifers, sites for waste disposal to the ground should be carefully selected and monitored to minimize risk of ground water pollution. In areas of confined aquifer conditions, proper well construction and well abandonment procedures must be implemented.
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