Barred Owl Conservation Management Plan 2016-2021 - Alberta Species at Risk Conservation Management Plan No. 14
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Barred Owl
Conservation Management Plan
2016-2021
Alberta Species at Risk Conservation Management Plan No. 14
Barred Owl
Conservation Management Plan
2016-2021
Prepared by:
Mike Russell
February 2016
ISBN 978-1-4601-2656-1 (PDF)
ISSN: 1922-9984
Cover photo: Gordon Court
For copies of this report, visit the Species at Risk Program web site at:
http://aep.alberta.ca/fish-wildlife/species-at-risk/default.aspx
This publication may be cited as:
Alberta Environment and Parks. 2016. Barred Owl Conservation Management Plan 2016-2021.
Alberta Environment and Parks. Species at Risk Conservation Management Plan No. 14.
Edmonton, AB. 10 pp.
ii
PREFACE
Albertans are fortunate to share their province with a diversity of wild species. A small number
of these species are classified as Species of Special Concern because they have characteristics
that make them particularly sensitive to human activities or natural events. Special conservation
measures are necessary to ensure that these species do not become Endangered or Threatened.
Conservation management plans are developed for Species of Special Concern to provide
guidance for land and resource management decisions that affect the species and their habitat.
These plans are intended to be a resource tool for provincial and regional fish and wildlife, land
and resource management staff in Alberta Environment and Parks and other government
departments.
Conservation management plans provide background information including species biology,
threats to species and habitat, and inventory/monitoring history. Plans also provide a goal,
objectives, and actions (management recommendations). Management recommendations are
typically categorised into inventory and monitoring needs; habitat management and
conservation; education and communication; and additional management considerations as
required.
Conservation management plans are generally prepared by an Alberta Environment and Parks
fish and wildlife biologist who has been designated as the provincial species lead. Writers from
outside the department are occasionally sought to prepare plans for species for which there is
little in-house expertise. In order to ensure accuracy and utility, each plan is reviewed by a
species expert and a designated provincial representative from forestry or land management
programs. In some cases there may be additional reviewers from staff, industry, and other
agencies.
Conservation management plans are internal guidance documents. They are implemented under
the guidance of the species lead and are “living” documents that can be revised at any time as
required. Conservation management plans are more succinct than the recovery plans that are
prepared for Endangered and Threatened species and do not involve participation of a multi-
stakeholder team.
Conservation management plans are approved by the Director of Species at Risk, Non-Game and
Wildlife Disease Policy. Plans will be reviewed annually by the species lead and updated if
necessary, and a more in-depth review will occur five years after a plan’s approval.
iiiTABLE OF CONTENTS
PREFACE ...................................................................................................................................... iii
ACKNOWLEDGEMENTS ............................................................................................................ v
EXECUTIVE SUMMARY ...........................................................Error! Bookmark not defined.
1.0 INTRODUCTION ................................................................................................................. 1
1.1 Breeding Biology and Habitat Requirements ....................................................................... 1
1.2 Threats to the Population ...................................................................................................... 4
1.3 Inventory and Monitoring History ........................................................................................ 4
2.0 GOALS AND OBJECTIVES ................................................................................................ 5
2.1 Goals ..................................................................................................................................... 5
2.2 Objectives ............................................................................................................................. 5
3.0 MANAGEMENT PLAN ....................................................................................................... 6
3.1 Monitoring and Assessment .................................................................................................. 6
3.2 Research and Management ................................................................................................... 6
3.3 Habitat Management ............................................................................................................. 6
3.4 Industrial Recommendations ................................................................................................ 7
3.5 Education and Communication ............................................................................................. 8
3.6 Regulation and Policy ........................................................................................................... 8
4.0 SUMMARY ........................................................................................................................... 9
5.0 LITERATURE CITED ........................................................................................................ 10
TABLE OF FIGURES
Figure 1. Records from targeted barred owl survey stations .......................................................... 2
Figure 2. Current estimate of barred owl distribution within Alberta ............................................ 3
ivEXECUTIVE SUMMARY
The barred owl (Strix varia) is a Species of Special Concern in Alberta because it requires large
tracts of old mixedwood forests and is subject to increased predation risk as these forests become
more fragmented in Alberta. The increasing demand for forest resources and the expanding
industrial footprint in the province threatens the persistence of habitat for the barred owl. Some
populations of barred owls are expected to decline as old mixedwood forest declines and
becomes more fragmented.
The barred owl occupies a wide extent of ecological regions in Alberta where the forests are old
and there is a mix of large deciduous trees and snags and old conifer forest. Barred owls nest in
the cavities of large balsam poplar (Populus balsamifera) and trembling aspen (Populus
tremuloides) formed by the decay and damage caused by natural processes. There are a number
of species that also rely on intact old mixedwood forest whose status is listed as Sensitive or
Species of Special Concern. Barred owls have much larger territories than many of these species
and therefore are considered suitable as an indicator, focal species or perhaps even an umbrella
species for a wider assemblage of species that rely on old mixedwood forests. Further evaluation
of this consideration that barred owls are a useful and suitable indicator of the larger assemblage
of species that rely on old mixedwood forest is recommended.
This plan recommends managing for barred owl habitat at multiple scales by tracking habitat
using existing barred owl models at landscape scales while also addressing objectives for habitat
management at the operational, or stand-level scale. There are several habitat models that can be
used to project changes across scenarios of industrial development and resource utilization
habitat at the scale of the landscape. Examples of habitat management at operational scales
include: implementing a habitat avoidance approach to site selection for industrial development,
the retention of old forest patches, snags and structure within stands, and avoiding disturbance
during the nesting period.
ACKNOWLEDGEMENTS
Several people provided input and/or reviewed comments throughout the various stages of plan
development, including: Dave Stepnisky, Lisa Wilkinson, Michelle Bacon, Jessica Lockhart, and
Sandi Robertson (Alberta Environment and Parks).
v1.0 INTRODUCTION
The barred owl (Strix varia) is identified as a Species of Special Concern in Alberta. Barred owl
populations, estimated to be less than 2000 breeding individuals (Alberta Sustainable Resource
Development 2010), occur in mixedwood boreal, foothills and aspen parkland forests throughout
the province. Often used as an indicator of old mixedwood forest in Canada, loss and
degradation of mature forest habitat presents the highest concern for barred owl populations in
Alberta.
1.1 Breeding Biology and Habitat Requirements
Barred owls are widely distributed in old mixedwood forest throughout North America. In
Alberta, barred owls inhabit mature forests in the mixedwood boreal, Rocky Mountain foothills
and aspen parkland ecoregions (Figure 1). Barred owls are highly territorial, typically
monogamous, and pairs maintain their territory in successive years. The average home range size
of barred owls in Alberta is typically 300ha in forested regions (Olsen 1999, Russell unpublished
data).
The nesting period starts in early spring and lasts until late May. Eggs are laid in late March or
early April, and a brood of 1-5 young hatches approximately 30 days later. Owlets are mostly
flightless for 12 weeks but leave the nest after only 4-5 weeks. During this pre-flight period,
owlets reduce their risk of predation by climbing leaning trees and perching high above the
ground, often in cover. Consequently, maintaining structural diversity in stands, such as partially
fallen trees and snags, will allow young owls to climb to safe perches. In addition, sites with
more diversity in composition and vertical structure make it more difficult for potential predators
to see the vulnerable young owls. Young owls are capable of sustained flight at 12 weeks at
which time they become more self-sufficient. Young disperse at approximately 4-5 months of
age (Mazur and James 2000, Alberta Sustainable Resource Development 2005).
Due to their nesting and foraging strategies, barred owls require specific habitat features. Barred
owls prefer unfragmented, mature and old growth mixedwood forest because of the greater
availability of nesting cavities in old snags and the high availability and variety of prey (Mazur
and James 2000, Priestley 2004, Alberta Sustainable Resource Development 2005). Tall trees or
snags with large diameters, such as balsam poplar (Populus baslsamifera) and aspen (P.
termuloides), are typically used as nest sites (Olsen et al. 2006). Barred owls nest in natural
cavities that are formed from disease or broken branches, or in the tops or hollow “chimneys” of
broken snags. The succession process that establishes these natural nest cavities takes over a
century after a forest is disturbed and the appropriate nest structures (e.g. snags) have a finite
lifetime as they degrade or fall down. Hence, effective management of barred owl nesting habitat
should focus on retaining mature forest with many large diameter trees to better ensure that
appropriate nesting cavities are available through time.
Barred owls are an indicator or umbrella species for old growth boreal forests because they are
non-migratory, have large home ranges, and require old forest within their territories for nesting
(Olsen et al. 2006, Russell 2008). Protecting blocks of undisturbed forest with mature upland
mixedwood overstory, large diameter snags, and more complex understory will benefit barred
owl habitat as well as the potential to protect a wide assemblage of other species including Bay-breasted warbler (Dendroica castanea), Canada warbler (Wilsonia canadensis), Black-throated
green warbler (Setophaga virens), American marten (Martes americana), Myotis bats (Myotis
sp.) and other old mixedwood dependent species.
Figure 1. Records from targeted barred owl survey stations where barred owls were detected or not
detected and all FWMIS locations of barred owls (presence only) from the Fish and Wildlife Management
Information System maintained by Alberta Environment and Parks. The Natural Regions and Subregions
are provided in the background to demonstrate the basis of range delineation.
2Figure 2. Current estimate of barred owl distribution within Alberta.
31.2 Threats to the Population
1.2.1 Loss of Old Growth Forest Habitat
Loss and fragmentation of old growth forest resulting from anthropogenic disturbances such as
forestry and industrial development are the greatest threats to barred owls in Alberta. Forestry
operations and fire impact forest age structure and composition, while energy and road
development reduce forest amount, often permanently, and fragment otherwise contiguous tracts
of habitat. Barred owls nest in cavities in old deciduous trees, typically over 100 years old, which
have a large diameter (minimum dbh of 36 cm). In addition, they require old forest for roosting
and foraging during both the breeding and non-breeding periods. Present forest management
practices in Alberta aim to harvest deciduous trees at an average of 60 years of age and
coniferous trees at an average of 80 years of age. Current forestry practices that target older
forest stands for preferential harvest result in the loss of large diameter snags (Priestly 2004,
Olsen et al. 2006, Fish and Wildlife Division 2008). While large tree retention, or buffers around
existing nest sites may mitigate for short-term impacts to breeding owls, solely protecting nest
sites in single, large diameter trees will not provide adequate management for barred owl habitat.
Barred owls hold large territories and require contiguous tracts of mature forest throughout their
home ranges. Management should therefore occur at both the local and landscape scale in order
to ensure long-term habitat supply for the entire life cycle (not just nest features) for this owl
species.
1.2.2 Increased Predation Risk
Barred owls may become more susceptible to increased competition and depredation by other
raptors in highly disturbed habitat. The fragmented landscape and increased edge habitat that
result from dispersed clearcuts and energy developments provides greater opportunities for larger
predators such as great horned owls (Bubo virginianus) to establish territories. Their presence
negatively impacts barred owl populations due to increased predation risk and competition for
food resources (Fish and Wildlife Division 2008, Olsen 1999, Russell 2008).
1.3 Inventory and Monitoring History
The abundance, distribution and habitat requirements of barred owl in Alberta have been well
documented. Barred owl occurrence and distribution in Alberta between 1912 and 1999 was
compiled with records from published literature, museum collections, banding records and
personal communications. Two hundred and ninety-seven occurrence reports were included in
the 87-year summary although only 46 nests were located (Priestly 2004). Six intensive studies
have been conducted on the barred owl in Alberta (Takats 1998; Olsen 1999; Grossman 2003;
Piorecky 2003; Russell 2008; Alberta Sustainable Resource Development- Grande Prairie 2009-
2011, unpublished). Takats examined distribution and abundance of barred owls in the Foothills
Model Forest (1998). The impacts of harvest regimes in north-central Alberta were studied by
Olsen (1999). Barred owl presence and abundance at the landscape scale was analyzed relative to
biophysical characteristics of the forest in east-central Alberta (Grossman 2003) and the Foothills
Natural Region (Piorecky 2003). Habitat selection across numerous spatial scales in a forest
patch within an agricultural landscape was modeled by Russell (2008). Barred owl presence and
4abundance was surveyed within the northern boreal by the Joint Oil Sands Monitoring Program
(2013) and existing habitat models were evaluated for this region (AEMERA 2015).
In recent years, efforts to collect long-term trend data on the population status of barred owl in
Alberta have been coordinated by provincial monitoring initiatives such as the Alberta Nocturnal
Owl Survey and Alberta Biodiversity Monitoring Institute. The Alberta Nocturnal Owl Survey is
a provincial survey largely conducted by volunteer citizen scientists to conduct auditory
nocturnal owl surveys with the goal of collecting long term trend information on owls. The
Alberta Nocturnal Owl Survey began as a full program in 2002 and continues to this day
(Beaverhill Bird Observatory 2013). The Alberta Biodiversity Monitoring Institute (ABMI) has
anecdotally recorded barred owls as part of their songbird bird monitoring initiatives, and have
expanded their program to include owl monitoring. The historical surveys conducted by ABMI
tend to be poor at detecting nocturnal owl species, as such, the ABMI staff and advisors are in
the process of creating nocturnal monitoring protocols that will improve data collection for long
term monitoring of species such as the barred owl (E. Bayne pers. comm.).
The current population estimate of barred owls in Alberta is unknown, although some estimates
have been extrapolated from the available information. The report listing barred owl as a Species
of Special Concern states “the species is considered to be relatively rare and likely exceeds 1000
individuals” (Fish and Wildlife Division 2008), while the Wild Species General Status Listing
of 2010 suggests less than 2000 breeding individuals in Alberta (Alberta Sustainable Resource
Development 2010).
2.0 GOALS AND OBJECTIVES
The following goals and objectives are based on current knowledge of barred owls.
2.1 Goals
Maintain current barred owl population and distribution, and improve habitat availability to
ensure species survival.
2.2 Objectives
• Review and evaluate the available Resource Selection Function (RSF) and Habitat
Suitability Index (HSI) models (Olsen 1999, Russell 2008, Fisher et al. 2009, Piorecky
2003), for various regions of Alberta. The resulting model(s) should be validated using
local data when available and implemented in landscape plans (including but not limited
to Forest Management Plans and Landuse Framework Plans)
• Inform the public and industry about the importance of preserving barred owl habitat
(e.g. old snags, mixedwood), and create educational material to aid in identifying barred
owl nests.
• Implement land use guidelines to reduce disturbance within barred owl habitat and
especially during the nesting period.
• Continue to encourage research aimed at understanding landscape requirements of barred
owls relative to demographic performance and long-term persistence.
53.0 MANAGEMENT PLAN
3.1 Monitoring and Assessment
Barred owls respond reliably to the broadcasts of conspecific vocalizations (Takats 1998, Olsen
1999, Grossman 2003, Piorecky 2003, Russell 2008), and as such call playback surveys can be
used to effectively monitor trends in this species. In order to track trends in barred owl
populations in the long-term, sampling of areas across the province should be conducted using
recognized call playback survey methodology. Future efforts should focus on:
• Ensuring surveys aimed at detecting barred owls are incorporated in provincial
monitoring initiatives (i.e. Alberta Biodiversity Monitoring Program).
• Ensuring that standard methodologies are adopted and agreed upon for any research
program and/or long-term monitoring program being initiated in Alberta.
3.2 Research and Management
Areas in the northeastern and northwestern parts of Alberta where there is a high industrial
footprint are lacking data about occupancy and population trends of barred owls. Efforts to
increase survey effort in the north have been initiated (Joint Oil Sands Monitoring Program,
Alberta Environmental Monitoring, Evaluation and Reporting Agency, and the University of
Alberta) and will continue to provide information on the distribution and relative density of
barred owls in the boreal mixedwood and highland ecological subregions.
Habitat models for barred owls in the Calling Lake (Olsen 1999), Athabasca (Russell 2008),
Eastern Slopes (Piorecky 2003), and Lower Athabasca (Fisher et al. 2009) regions of Alberta
have been developed. Efforts to test and validate these models across a large portion of barred
owl range in Alberta are ongoing.
The validation of existing barred owl habitat models has shown that not all of the predicted
potential territories are occupied and the demographic performance of these territories are not
homogenous. In order to improve and refine existing models, it will be important to collect
information on demographic vital rates and long term measures of occupancy (persistence)
within territories. The resultant information will facilitate more precise differentiation between
poor territories (sinks) and productive territories (sources). Improving the resolution in habitat
state between the existing habitat models will provide more effective management for the species
and possibly other old mixedwood habitat associates.
3.3 Habitat Management
Maintaining blocks of high quality mature forest where there are abundant snags for nests will
ensure availability of suitable habitat for barred owls. Such habitat must be managed in a
spatially explicit manner and retention targets and forest management planning should reflect
this. If habitat models are used to ensure that contiguous tracts of intact forest are retained for
barred owl management purposes, the spill-over effects for other old mixedwood dependent
wildlife species will also be realized. It is important to note that although the maintenance of
snags and old poplars is vital for ensuring suitable nesting structures for barred owls, it will not
be effective without proper landscape management. In other words, managing nesting structures
6will only be successful at maintaining owls on the landscape if the larger landscape (required for
foraging and cover) is maintained in suitable condition for the barred owl. Habitat management
must address the succession of stand types and management practices across time and therefore
is best achieved through the incorporation of industrial recommendations into long-term plans
(see section 3.4).
3.4 Industrial Recommendations
3.4.1 Forestry:
Without proper planning, forestry activities can severely deplete and damage barred owl habitat
by increased fragmentation, loss of nest trees and inappropriate retention strategies. Any harvest
clearing that does occur within older forested habitats should use mitigation strategies with the
goal of retaining important habitat features for barred owls when the harvested forest
regenerates. These operational mitigation items include (but are not limited to) the following:
• Timing of Harvest Activities should aim to avoid critical nesting and fledgling
periods (March 14 to July 15).
• Within-block retention should aim to retain the integrity of large diameter snags and
decadent poplar overstory trees >34dbh. These trees and snags could again become
valuable nesting structures when the adjacent forest regenerates. In addition,
unmerchantable timber (e.g. birch, small aspen, and small spruce) should be retained
if they are adjacent to large balsam trees or snags being retained. Larger clumps or
patches of trees adjacent to larger trees and snags will be more likely to provide
nesting habitat.
• Roads should be temporary in nature, in order to ensure reduced risk of road mortality
in the future and reduced fragmentation of the habitat when the adjacent forest
regenerates.
Although stand level mitigation (as outlined above) is an important tool in management,
landscape level harvest strategies that address habitat composition (i.e. amount) and
configuration (i.e. fragmentation) will be key in ensuring long term persistence of barred owl
populations. To effectively identify the amount and patterns of suitable habitat required for
barred owls on the landscape, barred owl habitat models are being developed by Wildlife
Management staff in cooperation with the Forest Management Branch of Environment and
Parks. The following recommendations are in place to ensure that barred owls are
considered at the landscape level in relation to forest management:
• At the Forest Management Planning stage, an analysis of barred owl habitat should be
incorporated into the planning process. A suggested method to complete this task is
to use the most relevant barred owl model for the FMA in question (this can be
determined in consultation with the Wildlife Biologist and Forest Management
Branch staff) and model barred owl habitat availability at the scale of the home range
for each scenario run of the Spatial Harvest Sequence and Timber Supply Analysis.
The outputs should be compared with each other and with the pre-harvest landscape
conditions to evaluate impacts of the proposed landscape level harvest plan on barred
owls.
73.4.2 Oil & Gas, or other industrial developments:
Oil and gas development can impact barred owls by causing loss and fragmentation of habitat (at
the landscape scale), loss of nest trees, and road associated mortalities. The alignment of
infrastructure (road, pipeline, well pad clearance) should favour younger stands and avoid old
mixedwood stands where possible. All new infrastructure should follow the policies outlined in
the Enhanced Approval Process Integrated Standards and Guidelines (EAPISG), available on the
Environment and Parks website) (e.g. no roads should be constructed to parallel each other
within 250m). Known nest sites, or those discovered during a wildlife sweep (See 100.8.1 in the
EAPISG) should be buffered a minimum of 100m and up to 500m depending on the level of
activity and timing (see EAPISG). A pre-development survey is recommended to identify any
old snags or large poplars that have high nesting potential for owls, so that they can be avoided
by the development if disturbances are planned within an area of old forest (guidelines for
conducting essential habitat surveys for boreal raptors are provided in the ESRD Sensitive
Species Guidelines 2013). Reclamation of well pads and roads in suitable stands should avoid
seeding and instead implement planting of the composition of surrounding cover types.
3.4.3 Agricultural development:
Agricultural development within suitable barred owl habitat should be minimized to prevent
habitat loss and land conversion that favours species that prey on or compete with barred owl
(e.g. great horned owls), and to avoid cattle knocking over standing dead trees that are important
for nesting. Range improvements (e.g. clearings, dugouts) should be avoided near old
mixedwood forest stands, where possible. If grazing occurs near barred owl habitat, provide
attractants (e.g. salt blocks, water) and shade for cattle away from the forest edge or fence out old
mixedwood areas. Strategies to prevent cattle from rubbing against the structure should be
implemented when a nest site is identified. For example, fencing off a buffer zone around the
nesting tree may provide sufficient protection for nesting barred owls.
3.5 Education and Communication
Barred owls are an important indicator species for boreal forest health, and maintaining their
habitat results in the persistence of habitat for numerous other species as well. Sharing this
information through education and stewardship programs for stakeholders and the general public
will greatly benefit conservation of habitat and ensure species resiliency. Stewardship programs
should emphasize the challenge of balancing the many interests associated with old mixedwood
forest management in the boreal and foothills regions. Citizens should be engaged through public
outreach about the value of this sensitive species and the role they play in the boreal forest.
Environmental consultants, oil and gas employees and forestry employees need to have access to
tools that will help identify barred owl nest sites and breeding habitat to ensure they are properly
identified, located, and mapped. With this in mind, an educational brochure has been created by
Environment and Parks, in cooperation with the Alberta Forest Products Association. This
brochure is available through the Alberta Forest Products Association offices and most Fish and
Wildlife offices within forested regions of Alberta.
3.6 Regulation and Policy
Barred owls are a protected species under Alberta’s Wildlife Act. In addition, as a Species of
Special Concern in Alberta, there is a higher degree of interest in ensuring that monitoring
activities and actions to maintain habitat are closely evaluated into the future. The status of
8barred owls in Alberta should be reviewed regularly (as part of the Species at Risk Program) to
ensure that, if populations are determined to be in further decline, actions are taken to
appropriately amend status and policy in relation to this species.
The Land Use Framework is a significant government initiative that has the ability to set
objectives and track biodiversity indicators. It is important that as these Landuse Framework
plans developed throughout the forested regions of the province, barred owls are included in
planning either indirectly (through habitat targets for old mixedwood obligate species) or directly
(through setting targets specific to barred owls and monitoring these indicators over time) to
ensure that barred owl populations persist on the landscape into the future.
Policies are presently in place to ensure that Forest Management Planning captures non-timber
values through the Forest Management Planning process and creation of VOITs (Values,
Objectives, Indicators, and Targets) to track these commitments. In many recent plans, barred
owl habitat has been selected as a key habitat feature to track in order to meet non-timber
objectives for old mixed wood obligate species. Work should continue to ensure that planning
documents, as part of the Forest Management Planning process used by companies across the
province, capture barred owl habitat either directly or indirectly.
4.0 SUMMARY
As a species that nests in cavities within older boreal forest landscapes, the long term persistence
of barred owl populations in Alberta is highly dependent on maintenance of old mixed-wood
forest and the structure within. Industrial activities such as forest harvesting and oil and gas
development threaten suitable barred owl habitat through either direct removal of old mixed-
wood habitat and/or fragmentation of the landscape.
To manage for this species into the long-term, key action items to pursue as part of this
management plan include:
• Assurance that monitoring programs can adequately track trends in barred owl
populations.
• Assurance that research and monitoring programs focus on gaps in data in the North
East and North West portions of Alberta, as well as focus on demographic
performance in alternate habitat areas (determining source/sinks)
• Assurance that old mixed-wood forests are maintained on the landscape through
Forest Management Planning initiatives, stand-level mitigation associated with forest
management activities, and pre-planning/mitigation for oil and gas activities.
• Assurance that educational materials are made available to the public and private
sectors to ensure that that individuals working and recreating in barred owl habitats
are aware of the important features for this species.
Monitoring and research initiatives will need to inform policy and regulations into the future. If
barred owl populations are seen to decline over time, then more aggressive landscape planning
and legislation will be required to ensure that habitat is maintained for this species for future
generations of Albertans to appreciate.
95.0 LITERATURE CITED
Alberta Sustainable Resource Development. 2010. The general status of Alberta wild species 2010.
Alberta Sustainable Resource Development, Fish and Wildlife Service, Edmonton. URL:
http://www.srd.alberta.ca/FishWildlife/SpeciesAtRisk/GeneralStatusOfAlbertaWildSpecies/Defa
ult.aspx.
Alberta Sustainable Resource Development. 2008. Report of Alberta’s Endangered Species Conservation
Committee: June 2006. Alberta Sustainable Resource Development, Fish and Wildlife Division,
Edmonton AB. 44 pp.
Alberta Sustainable Resource Development. 2005. Status of the barred owl (Strix varia) in Alberta.
Alberta Sustainable Resource Development, Fish and Wildlife Division, and Alberta
Conservation Association, Wildlife Status Report No. 56, Edmonton, AB. 15 pp.
Alberta Environment and Sustainable Resource Development. 2013. Sensitive Species Inventory
Guidelines. April 2013. http://esrd.alberta.ca/fish-wildlife/wildlife-management/sensitive-species-
inventory-guidelines.aspx
Alberta Environmental Monitoring, Reporting and Evaluation Agency. 2015. Validating Barred
Owl Habitat Models for the Oil Sands Monitoring Region of Alberta. July 2015.
Beaverhill Bird Observatory. Nocturnal Owl Monitoring Survey.
http://www.beaverhillbirds.com/owl_surveys.php Accessed on January 7th, 2013.
Fisher, J. T., B. Eaton, and D. A. Kirk. 2009. Species-at-risk indicator habitat model: Barred Owl (Strix
varia), Lower Athabasca Regional Plan. Alberta Research Council Inc., Vegreville, Alberta.
Grossman, S. R. 2003. Owl responses to habitat change at the landscape and regional scale and effects of
weather in east central Alberta. MSc. thesis. University of Alberta (Canada).
Mazur, K. M., and P. C. James. 2000. Barred Owl (Strix varia). The Birds of North America Online (A.
Poole, Ed.). Ithaca: Cornell Lab of Ornithology; Retrieved from the Birds of North American
online: http://bna.birds.cornell.edu/bna/species/508
Olsen, B. T. 1999. Breeding habitat ecology of the barred owl (Strix varia) at three spatial scales in the
boreal mixedwood forest of north-central Alberta. MSc. thesis, University of Alberta (Canada).
Olsen, B. T., S. J. Hannon, and G.S. Court. 2006. Short-term response of breeding barred owls to forestry
in a boreal mixedwood forest landscape. Avian Conservation and Ecology 1:1. [online] URL:
http://www.ace-eco.org/vol1/iss3/art1.
Piorecky, M. D. 2003. Distribution, abundance and habitat selection of northern pygmy and barred owls
along the eastern slopes of the Alberta Rocky Mountains. MSc. thesis. University of Calgary
(Canada).
Priestley, L.T. 2004. The barred owl, Strix varia in Alberta: distribution and status. Canadian Field
Naturalist 118 (2): 215-224.
10Russell, M. S. 2008. Habitat selection of barred owls (Strix varia) across multiple spatial scales in a
boreal agricultural landscape in north-central Alberta. MSc. thesis. University of Alberta
(Canada).
Takats, D. L. 1998. Barred owl habitat use and distribution in the Foothills Model Forest. MSc. thesis,
University of Alberta (Canada).
11List of Titles in the Alberta Species at Risk Conservation Management Plan Series
(as of February 2016)
No. 1 Long-toed Salamander Conservation Management Plan.
No. 2 Sprague’s Pipit Conservation Management Plan, 2010-2015.
No. 3 Long-billed Curlew Conservation Management Plan, 2010-2015.
No. 4 Harlequin Duck Conservation Management Plan, 2010-2015.
No. 5 Weidemeyer’s Admiral Conservation Management Plan, 2012-2017
No. 6 Western Small-footed Bat Conservation Management Plan, 2012-2017
No. 7 White-winged Scoter Conservation Management Plan, 2012-2017
No. 8 Bull Trout Conservation Management Plan, 2012-2017
No. 9 Prairie Falcon Conservation Management Plan, 2012-2017.
No. 10 Black-throated Green Warbler, Bay-breasted and Cape May Warbler Conservation Management
Plan, 2014-2019.
No. 11 Great Plains Toad Conservation Management Plan, 2015-2020.
No. 12 Prairie Rattlesnake Conservation Management Plan, 2015-2020.
No. 13 Hare-footed Locoweed Conservation Management Plan, 2016-2021.
No. 14 Barred Owl Conservation Management Plan, 2016-2021.You can also read
