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An assessment of drinking water quality for Alberta communities in the Peace, Athabasca and Slave River Basins


Year: 1996

Abstract:
The World Health Organization (WHO, 1993) states that: "Water is essential to sustain life and a satisfactory supply must be made to achieve a drinking water quality as high as practicable" The primary purpose of drinking water treatment is the protection of public health. The quantity of drinking water and the efficiency of treatment can be assessed through comparison to guidelines. In Canada, the applicable document is the Guidelines for Canadian Drinking Water Quality (1993) which has been adopted as minimum drinking water quality for licensed facilities in the province of Alberta. Most other developed countries have similar guidelines or regulations. The World Health Organization has also developed "Guidelines for Drinking Water Quality" (WHO, 1993) with a primary aim of protecting public health. To assess drinking water quality in the Northern River Basin Study area results obtained from existing information and that obtained during this study were compared to both sets of guidelines discussed above. Of the sites investigated many were licensed facilities by Alberta Environmental Protection (AEP) and are required to meet as a minimum the Guidelines for Canadian Drinking Water. Other sites although not licensed by AEP still supply water to consumers, who tend to assure the water is of potable quality. As stated in the guidelines for Canadian Drinking Water: "The guidelines and recommendations listed herein are intended to apply to all drinking water supplies, public and private. ... Judicious use of the guidelines will result in the provision of drinking water which is both wholesome and protective of public health." As a result both licensed and unlicensed facilities were assessed based on comparison to guidelines. Based on site visits to 38 facilities, water quality analyses completed for the site visit and analysis of existing water quality information a number of conclusions can be made on the drinking water quality in the Northern River Basin Study area. 1. Small facilities in the study area tend to produce poorer water quality than larger facilities. This was found to be the case in terms of microbiological quality, turbidity (a good overall measure o f treatment performance), and historical THM data. 2. As stated by the World Health Organization (1993): "Infectious diseases caused by pathogenic bacteria, viruses and protozoa or by parasites are the most common and wide spread health risk associated with drinking water." As it is not possible or feasible to test for all pathogenic organisms, microbiological quality of drinking water is assessed based on indicator organisms. If these indicator organisms are present in the finished drinking water it then must be assumed that pathogens could also be present. The most common microbiological indicator used in drinking water is the coliform group of organisms. Due to difficulties in sampling, transporting and analysis a single coliform positive sample may not truly reflect the microbial quality of the drinking water. As a result the Guidelines for Canadian Drinking Water Quality (GCDWQ,1993) state that not more than 10% of samples taken should be coliform positive. The WHO (1993) uses a more stringent guideline of not more than 5% be coliform positive. As the number of samples in small facilities are not great the 10% value was used in this study to assess microbial water quality to avoid unwarranted concerns to be raised for a facility based on a couple of bad samples. Analysis of a large database obtained from AEP of coliform results from communities in the Northern River Basin Study area was completed. This database consisted ofroughly 270,00 total and 270,000 fecal coliform analyzes taken over the last seven years. O f the smallest facilities, watering points, 30% o f them exceeded the 10% coliform positive guideline. If one includes samples which are considered poor by the GCDWQ (1993) this increases to 45%. Of particular concern was the finding that a number of facilities had high coliform positive percentages for all of the seven years the data was analyzed. The occurrence of fecal streptococci, another indicator of fecal contamination, in 6 of the 28 surface water sites visited adds additional concern on the microbiological quality of water in many communities in the NRBS area. 3. It was also found that small facilities in the study area tended to have higher turbidity than larger communities. Although turbidity is only a measure of the clarity of water, high turbidity has been shown to negatively impact the performance of disinfection. In addition the most effective method of removal of protozoan cysts such as Giardia and Cryptospordium is through physical-chemical treatment processes for which there performance can be related to turbidity removal. The importance of turbidity as a parameter to indicate microbial quality is evident in the USEPA using turbidity to justify pathogen removal credits in their most recent standard. In these standards, maximum credits are earned with turbidity of < 0.5 NTU 95% of the time. Results from existing data indicated that surface water facilities serving populations less than 500 have a significantly higher turbidity than facilities serving populations greater than 500. Because these samples were obtained from the distribution system and the small number of samples collected, compliance with guidelines could not be assessed. During the site visits 6 of the 38 sites had turbidity greater than 1 NTU, which in included the two watering points visited. These grab samples cannot be compared to standards which specify the maximum average turbidity 95% of the time must be below 1 NTU but they indicate that there may be problems at these sites. 4. Chemical parameters associated with raw water quality were found to be below guideline values based both on existing data and site visit data. However, for disinfection by-products (THMs) which are produced during treatment, the site visit data found, that 60% (12 Of21) ofthe surface water sites exceeded the guideline value of lOOug/L for THM. Analysis of existing data for THMs was complicated by the fact that most samples taken occurred under the old value of 350ug/L. The analysis did show however, if levels remained unchanged, 20 of the 62 sites analyzed by AEP would have difficulty meeting the lower standard value that is now in place. 5. Observation from site visits tended to indicate that much of the difficulties associated with small facilities may be related to operation of the facilities. Generally this can be related to the allotted time the operator is given to operate the facility, with smaller facilities having less time than larger facilities. The attitude of the people in decision making positions related to water treatment may also be an important factor. Operation performance may also be related to training as in larger facilities the majority or sole duty ofthe operator is to run the facility. As a result the opportunity for these operators to receive training is much greater. In small facilities, the operation of the treatment facility may be one of numerous tasks the operator may have to do. As many other tasks may be part of their daily routine the opportunity and incentive for these operators for training tends to be less. 6. Based on results of this study, remedial action is required in many small communities in the Northern River Basin Study area to bring the drinking water into compliance with current standards which are based on the protection of public health. Many communities are currently drinking water that may not meet Guidelines for Canadian Drinking Water Quality. Areas of concern are both the microbiological quality of the water and high levels of disinfection by-products. Of these the microbiological quality of the drinking water is by far of greatest concern. Many of the small communities showed higher than acceptable levels of indicator organisms as well as high turbidity. The occurrence of both would indicate that if pathogenic organisms are present in the raw water source they probably will not be removed by the treatment system. In the time needed for remedial actions to rectify the problems it is of utmost importance that consumers of water be notified immediately as to the status of their drinking water with respect to standards along with recommendations of prudent courses of action available to them. In the case of microbiological problems that are not rectified consumers should be advised to boil their drinking water as recommended in Guidelines for Canadian Drinking W ater Quality (1993) and W orld Health Organization (1993).

An assessment of hydro-ecological changes at two closed-drainage basins in the Peace-Athabasca Delta, Alberta, Canada


Author(s): Sinnatamby, R. N.

Year: 2006

Abstract:
Diatom analyses were carried out on sediment cores collected from two low-lying, closed-drainage basins (PAD 9 - 58°46.46' N, 111°19.48' W; PAD 12 - 58°57.29' , 111°19.74' ) in the Peace sector of the Peace-Athabasca Delta (PAD), Alberta, Canada, to provide >1000 year long records of hydro-ecological change. Results from diatom analyses were compared with macrofossil and stable isotope records from the same cores and assessed within the framework of an Athabasca River headwater climate record inferred from isotope dendroclimate data. Results from PAD 9 and PAD 12 sediment cores indicated closed-drainage conditions during the Medieval Warm Period (MWP) and the post-Little Ice Age and high water conditions during the Little Ice Age (LIA). High water levels at PAD 9 and PAD 12 reflected high water conditions on Lake Athabasca and the Rivière des Rochers or possibly the Peace River during the LIA (∼AD 1600-1900). High water conditions were also observed at low-lying sites in the central and southern regions of the PAD (PAD 31 and PAD 37), and corresponded with evidence of high streamflows on the North Saskatchewan River. In contrast, desiccation evident at PAD 5, a site largely isolated from river influence, reflected atmospherically dry conditions during the LIA. Consistent with changes observed at PAD 5, sediment records at PAD 15, an oxbow lake off the Revillion Coupé, demonstrated low flood frequency during the early to mid-1700s. Increased water levels evident at low-lying sites located in proximity to the central open-drainage network of lakes and rivers were likely due to higher flows on the Athabasca River and potentially on the Peace River. High flows on rivers of the PAD may be attributed to snowmelt-dominated runoff during the LIA relative to the rainfall-dominated runoff during MWP (prior to ∼AD 1600) and the post-LIA period (∼AD 1900 to present).

An assessment of non-conventional drinking water in the Peace, Athabasca and Slave River basins


Year: 1997

Abstract:
It is estimated that approximately 25 % of the residents of the Northern River Basins Study area do not receive their drinking water from conventional drinking water treatment facilities. Therefore, these people rely on alternative sources for their drinking water supply. This report assesses the utilization and quality of the different non-conventional sources of drinking water that are used by people that do not consume conventionally treated water. Some of the non-conventional drinking water supplies utilized in the NRBS area include: (1) self-hauled treated water; (2) untreated surface water; (3) dugout water; (4) groundwater; (5) environmental sources of water such as snow, rain, and birch tree water; (6) bottled water; and (7) water treated by a variety of point-of-use technologies. There were four main research components in the assessment of these non- conventional drinking water supplies. First, the results of an in-depth review of the literature available on non-conventional drinking water sources, drinking water quality and the correlation of drinking water and health is presented in the first part ofthis report. Although the literature was limited on the actual consumption and quality of most of the non-conventional sources of drinking water consumed in the study area, substantial information exists on conventional drinking water quality as well as considerable information on several point-of-use treatment technologies. Essentially, the best type of point-of-use treatment depends on the raw water source. Perhaps the best point-of-use treatment method to use on water o f unknown quality is to boil it. The recommended boiling time in the literature varies considerably from simply heating the water to 50°C to vigorous boiling for 15 minutes. However, the majority of the authors cited a full boil for 1 minute as being sufficient to inactivate most pathogens. Besides boiling, there are numerous other point-of-use treatment technologies that employ disinfection (ultraviolet disinfection, ozonation, chlorination, iodination) and mechanical particle removal processes (such as sedimentation and filtration). The best available technology depends on the raw water source and likely incorporates more than one process to provide multiple barriers to ensure adequate drinking water quality. The second component of research regarding non-conventional drinking water in the Northern River Basins Study are was to visit selected NRBS communities and interview residents regarding their non-conventional drinking water practices. Remote areas around Fort Chipewyan, John D’Or Prairie, Fox Lake and Atikameg were visited and residents were asked about the sources and utilization on non-conventional drinking water supplies, as well as their overall drinking water quality concerns. It was through these informal interviews that most of the information was collected on the types of non-conventional drinking water used and how it was treated, if at all, prior to consumption. Many of the people interviewed discussed the deterioration of some of the surface water sources in the study area, but the majority of the concerns presented regarding drinking water quality in this study was in regards to the addition of chlorine in the conventional drinking water treatment process. Based on this, it was found that some people who do have conventionally treated water delivered to their home, collect a non-conventional supply of water for consumption such as from a nearby lake or river. This water has been called “special drinking water” by those consumers. It was also based on these findings that a series of population sub-groups that may be particularly pre-disposed to consuming non-conventional drinking water was postulated. First, those that live in remote areas not i serviced by conventional drinking water facilities are obvious consumers of non-conventional drinking water supplies. Second, some NRBS residents may be traditional consumers of alternative drinking water supplies. Many elderly residents may be included in this second group. Third, NRBS residents may consume non-conventional drinking water as a result of cultural activities such as living off the land expeditions or other wilderness activities. And the final group includes those individuals that consume non-conventional drinking water supplies for health reasons. This may include people that drink bottled water for its perceived health benefits as well as those that consume special drinking water to avoid the taste and smell o f chlorine in conventionally treated water. Third, during these field trips, samples of non-conventional drinking water were collected and these samples were analyzed for various physical, chemical and microbiological parameters. The non- conventional samples collected included untreated lake, river and creek water, spring water, groundwater well water, snow water, bottled water, and one sample of water treated with a point-of- use filter. Although the number of samples collected was limited and does not allow for absolute conclusions, several trends can be hypothesized. It was found that untreated surface water did not meet many of the physical, chemical and microbial guidelines in the GCDWQ. Although the groundwater samples collected met the microbiological limits in the GCDWQ, some physical and chemical parameters may be exceeded. The bottled water samples were found to have a very high background bacterial count and the point of use device tested was found to have actually contributed coliforms to the influent water supply. The fourth component in the assessment of non-conventional drinking water supplies in the Northern River Basins Study area was to pursue research on the effectiveness on some of the portable point-of- use drinking water treatment filters on the market. The reason for this was because there is a very limited body o f literature regarding these devices, and the claims made by the manufacturers suggest that these units are suitable to provide a safe supply of drinking water for wilderness campers and travelers. For the rigorous laboratory testing of these units, three filters were chosen to represent the larger market. The filters were chosen based on the type of filter media (carbon media, plastic media and silver impregnated ceramic media were selected), the price range (least expensive to most expensive were tested), and each unit was from a different manufacturer. The filters were subjected to an influent test water with a high turbidity, high bacterial count and a high particle count. It was found that only the silver impregnated ceramic filter was capable of reducing the turbidity, bacterial count and particle levels to below recommended levels for supplying a safe drinking water. However, further microbiological tests on this unit are required before it can be recommended for utilization in the study area.

An examination of the toxic properties of water extracts in the vicinity of an oil sand extraction site


Year: 2011

Abstract:
The industrial extraction of oil sands (OS) in northern Alberta, Canada, has raised concerns about the quality of the Athabasca River. The purpose of this study was to examine the toxic properties of various water extracts on Oncorhynchus mykiss trout hepatocytes. The water samples were fractionated on a reverse-phase C(18) cartridge and the levels of light-, medium- and heavy-weight polycyclic aromatic hydrocarbons (PAHs) were determined by fluorescence spectroscopy. Primary cultures of trout hepatocytes were exposed for 48 h at 15 °C to increasing concentrations of the C(18) extract corresponding to 0.02, 0.1, 0.5 and 2.5X concentrations from upstream/downstream sites in the Athabasca River, lake and groundwater samples, OS tailings and interceptor well-water samples. Changes in cell viability, phase I and phase II biotransformation enzymes (cytochrome P4501A and glutathione S-transferase activities), oxidative damage (lipid peroxidation LPO) and genotoxicity (single and double DNA strand breaks) were monitored in post-exposure cells. The water samples decreased cell viability and increased all the above endpoints at thresholds of between 0.02 and 0.1X the water concentration. The most responsive biomarker was DNA damage but it also offered the least discrimination among sites. LPO was higher at sites downstream of the industrial operations compared to upstream sites. A decision tree analysis was performed to formulate a set of rules by which to identify the distinctive properties of each type of water samples. The analysis revealed that OS tailings and interceptor waters were characterized by an increased concentration in light PAHs (>42 μg L(-1)) and this fraction represented more than 85% of the total PAHs. These samples also inhibited GST activity, which could compromise the elimination of genotoxic PAHs present in the system. An analysis of groundwater samples revealed a contamination pattern similar to that for OS tailings. There is a need for more research into specific biomarkers of toxicity from OS tailings compounds such as naphthenic acids, light PAHs among others, which are a characteristic fingerprint of OS extraction activities.

An intensive study of the fish fauna of the Muskeg River watershed of northeastern Alberta Vol I (Interim report)


Author(s): Bond, W. A., & Machniak K.

Year: 1977

Abstract:
The fish fauna of the Muskeg River was studied during spring and summer, 1976. Migrations of non-resident fish from the Athabasca River into the Muskeg River watershed were monitored through the use of a two-way counting fence between 28 April and 30 July. A total of 6153 fish were passed through the upstream trap of which white suckers (46%) and longnose suckers (46%) comprised the vast majority. Arctic grayling (5%) and northern pike (2%) accounted for most of the remainder. After spawning in the lower reaches of the Muskeg River, migrant suckers of both species returned to the Athabasca River. Arctic grayling, however, remained in the tributary throughout the summer. Floy tags applied to 2269 migrant fish yielded a 1.2% return rate for fish recaptured outside the Muskeg watershed. Small fish collections made throughout the summer demonstrated the importance of the lower Muskeg drainage as a rearing area for young of-the year white suckers, longnose suckers and Arctic grayling. Lake chub, slimy sculpin and brook stickleback were the most abundant forage fish species.

An intensive surface water quality study of the Muskeg river watershed. Volume 1, Water chemistry


Author(s): Akena, A. M.

Year: 1979

Abstract:
This document is part of a series of research reports that describes the results of investigations funded under the Alberta Oil Sands Environmental Research Program, which was established by agreements of the Governments of Alberta and Canada in February 1975. This ten year program was designed to direct and co-ordinate research projects concerned with the environmental effects of development of the Athabasca Oil Sands in Alberta. This report documents and appraises baseline water chemical quality conditions of a lake and streams within the Muskeg River Watershed.

An overview of streamflows and lake levels for the Peace, Athabasca and Slave River basins


Author(s): Choles, J., Aitken W., & DeBoer A.

Year: 1996

Abstract:
This report provides a summary of flow and lake level information for water bodies in the Peace, Athabasca and Slave river basins to provide a hydrologic background far many of the other reports published by the Northern River Basins Study. The trends in river flows for both the main stems and significant tributaries, and for lake levels, for both natural and regulated conditions were examined. Ice processes were discussed along with some of the environmental effects. Regulation on the Peace River has altered the hydrologic regime of both the Peace and Slave Rivers, as well as the ice regime on the Peace River as far downstream as Fort Vermilion. Lake Athabasca and Great Slave Lake levels have also been affected by the changes in the Peace River flow regime.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2005-2006 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2005 and 2006 and land use and land cover classification data derived from 2006 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2005 to 2006, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2006-2007 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2006 and 2007 and land use and land cover classification data derived from 2007 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2006 to 2007, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2007-2008 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2007 and 2008 and land use and land cover classification data derived from 2008 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2007 to 2008, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2008-2009 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2008 and 2009 and land use and land cover classification data derived from 2009 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2008 to 2009, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2009-2010 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2009 and 2010 and land use and land cover classification data derived from 2010 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2009 to 2010, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2010-2011 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2010 and 2011 and land use and land cover classification data derived from 2011 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2010 to 2011, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2011-2012 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2011 and 2012 and land use and land cover classification data derived from 2012 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2011 to 2012, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Land Disturbance Classification Results in the Cold Lake Oil Sands Area Derived from 2012-2013 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2012 and 2013 and land use and land cover classification data derived from 2013 were used to produce this dataset. The land use and land cover changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation loss data from 2012 to 2013, classified into 9 classes: 1 - exposed land/cut blocks/harvested areas, 3 - transitional bare surfaces, 4 - mixed developed areas, 5 - developed areas, 6 - shoal, 7 - shrub land, 8 - grassland and 9 - agricultural areas. These categories can be used as baseline data for planning, managing and monitoring surface infrastructure needs and impacts.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2005-2006 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2005 and 2006 and Land Use and Land Cover (LULC) classification data derived from 2006 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2005 to 2006, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2006-2007 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2006 and 2007 and Land Use and Land Cover (LULC) classification data derived from 2007 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2006 to 2007, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2007-2008 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2007 and 2008 and Land Use and Land Cover (LULC) classification data derived from 2008 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2007 to 2008, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2008-2009 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2008 and 2009 and Land Use and Land Cover (LULC) classification data derived from 2009 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2008 to 2009, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2009-2010 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2009 and 2010 and Land Use and Land Cover (LULC) classification data derived from 2010 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2009 to 2010, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2010-2011 Landsat imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2010 and 2011 and Land Use and Land Cover (LULC) classification data derived from 2011 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2010 to 2011, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2011-2012 Landsat imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2011 and 2012 and Land Use and Land Cover (LULC) classification data derived from 2012 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2011 to 2012, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Annual Vegetation Recovery Classification Results in the Cold Lake Oil Sands Area Derived from 2012-2013 Landsat Imagery (Image data, Tiff format)


Year: 2009

Abstract:
The Cold Lake oil sands area - Township 56 to 69, Range 1 to 11, west of the 4th Meridian, falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on the ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and to collect the information necessary to understand cumulative effects. Landsat multispectral imagery for 2012 and 2013 and Land Use and Land Cover (LULC) classification data derived from 2013 were used to produce this dataset. The LULC changes include vegetation loss from anthropogenic disturbances, such as infrastructure related to oil and gas exploration, forestry and agriculture, and vegetation recovery from these disturbances. This digital data release contains the vegetation recovery data from 2012 to 2013, classified into 6 classes: 1 - shrub land, 2 - grassland, 3 - agricultural areas, 4 - coniferous forest, 5 - broadleaf forest and 6 - mixed forest.

Anthropogenic Footprints of the Cold Lake Oil Sands Area from 2005 to 2013 Landsat Imagery (GIS data, polygon features)


Year: 2009

Abstract:
The Cold Lake Oil Sands area, Twp. 56 to 69, Rge. 1 to 11, W 4th Mer., falls within the Lower Athabasca Regional Plan (LARP). As part of Alberta's Land-use Framework, LARP was developed in 2012 to set the stage for robust growth, vibrant communities and a healthy environment within the region. One of its implementation objectives is to balance the economic development of oil sands and impacts on ecosystem and environment. This is to be achieved through enhanced science-based monitoring for improved characterization of the environment and collection of the information necessary to understand cumulative effects. The anthropogenic footprints shapefile contains a compilation of developed and mixed developed footprint classes extracted from the land-use/land-cover classifications data from 2005 to 2013, published by Alberta Geological Survey. They can be used as a baseline for planning, managing and monitoring surface infrastructure needs and impacts.

Appendix 3.8: Traditional land use environmental setting report update


Year: 2013

Abstract:
The purpose of this Traditional Land Use (TLU) Environmental Setting Report (ESR) is to summarize TLU information relating to Shell Canada Energy’s (Shell’s) Pierre River Mine (PRM) Project that has become available since the Jackpine Mine Expansion and Pierre River Mine Environmental Impact Assessment (EIA) was submitted in 2007. Information sources used to prepare the ESR are listed in Section 1.2. When preparing a concise review based on multiple, lengthy literature sources, it may be necessary to paraphrase, summarize and interpret TLU information from the source material. Due to this practical limitation, it is recommended that the Joint Review Panel, and other reviewers, further examine the referenced source material in its entirety to have a fulsome perspective of the TLU information provided in those documents.

Aquatic biophysical inventory of major tributaries in the AOSERP study area. Volume 1: Summary report


Year: 1980

Abstract:
This report summarizes and compares the physical charac- teristics of nine streams within five watersheds (Firebag, Muskeg, Steepbank, MacKay, and Ells) in the AOSERP study area. The distri- butions and relative abundances of fish in each stream and watershed are also described and related to the physical characteristics that tend to promote or limit sport fish production. The system of reach classification and biophysical measurements developed by Chamberlin and Humphries (1977) was used throughout the present study. The detailed results of this study are presented in the accompanying atlas that forms Volume II of this report (Walder et al. 1980). From 16 to 24 species of fish were found in each watershed. Forage fish (lake chub, pearl dace, longnose dace, trout-perch, brook stickleback, slimy sculpin) and white and longnose suckers were the most abundant fish in every stream or river studied. The most important and widespread sport fish present were (in order of decreasing abundance) arctic grayling, northern pike, and walleye. Other species of sport fish (burbot, lake whitefish, mountain whitefish, yellow perch, Dolly Varden, and goldeye) were found in small numbers, and were almost always confined to the lower reaches of the rivers in proximity to the Athabasca River. A good correlation was found between physical characteristics of streams and the distributions and abundances of fish. Present information suggests that the following general ratings for sport fish potential can be applied to the five water- sheds that were studied: Firebag River watershed, excellent; Muskeg River watershed, poor to moderate; Steepbank River, moderate; MacKay River watershed, poor to p.ossibly moderate; and Ells River, excellent. These ratings are based only-on comparisons among the studied watersheds; they do not consider productivity of other water-or beyond the boundaries of the AOSERP study area.

Aquatic biophysical inventory of major tributaries in the AOSERP study area. Volume I: Summary report


Year: 1980

Abstract:
This report summarizes and compares the physical characteristics of nine streams within five watersheds (Firebag, Muskeg, Steepbank, MacKay, and Ells) in the AOSERP study area. The distributions and relative abundances of fish in each stream and watershed are also described and related to the physical characteristics that tend to promote or limit sport fish production. The system of reach classification and biophysical measurements developed by Chamberlin and Humphries (1977) was used throughout the present study. The detailed results of this study are presented in the accompanying atlas that forms Volume II of this report (Walder et al. 1980). From 16 to 24 species of fish were found in each watershed. Forage fish (lake chub, pearl dace, longnose dace, trout-perch, brook stickleback, slimy sculpin) and white and longnose suckers were the most abundant fish in every stream or river studied. The most important and widespread sport fish present were (in order of decreasing abundance) arctic grayling, northern pike, and walleye. Other species of sport fish (burbot, lake whitefish, mountain whitefish, yellow perch, Dolly Varden, and goldeye) were found in small numbers, and were almost always confined to the lower reaches of the rivers in proximity to the Athabasca River. A good correlation was found between physical characteristics of streams and the distributions and abundances of fish. Present information suggests that the following general ratings for sport fish potential can be applied to the five watersheds that were studied: Firebag River watershed, excellent; Muskeg River watershed, poor to moderate; Steepbank River, moderate; MacKay River watershed, poor to possibly moderate; and Ells River, excellent. These ratings are based only-on comparisons among the studied watersheds; they do not consider productivity of other watersheds within or beyond the boundaries of the AOSERP study area.

Aquatic reclamation in the Athabasca, Canada, oil sands: Naphthenate and salt effects on phytoplankton communities


Year: 2001

Abstract:
Microcosm experiments with natural indigenous phytoplankton communities were conducted to assess the effects of waters from oil sands extraction processes, emphasizing the naphthenate and salt constituents. Process waters of varying ages (zero to eight years) remediation histories, and chemical composition were obtained from outdoor mesocosms and inoculated with phytoplankton assemblages from a reference lake in the study area. Community composition measures, including percentage model affinity (PMA) and canonical correspondence analysis (CCA), revealed significant community effects of water from systems less than five years old, with naphthenate concentrations greater than 20 mg/L, compared to water from the reference lake. Canonical correspondence analysis, PMA, and regression analyses further showed that naphthenate concentration was significantly correlated with community structure. Using CCA, groups of taxa characteristic of waters with > 20 mg/L naphthenates (including Botryococcus braunii, Gloeococcus schroeteri, Cosmarium depressum, Chrysococcus rufescens, Chromulina spp., Ochromonas spp., and Keratococcus spp.) were identified. Salinity, as reflected in conductivity, was positively correlated with naphthenate concentration and itself appeared to influence the community structure. The results confirmed an important role for naphthenates in ecological effects of process waters from oil sands mining, but the influence of covarying factors such as salinity requires further investigation.

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