16/04/2022
Abstract
Grassland birds in North America face many problems as a result of habitat loss and fragmentation; understanding their habitat requirements is critical for their conservation and management. The sharp-tailed grouse (Tympanuchus phasianellus) can be found throughout North American grasslands and is a species of economic and cultural importance, but it has experienced population declines over the last few decades. A large part of sharp-tailed grouse life history is focused on and around lekking grounds, which makes leks an essential feature for sharp-tailed grouse management. We used information from 596 leks and landcover predictors within 1-km and 5-km squares to perform Habitat Suitability Index modeling for sharp-tailed grouse on the Northern Great Plains in Saskatchewan, Canada. The proportion of grasslands at the 5-km scale and the 1-km scale were the two most important factors affecting lek occurrence (permutation importance = 34.8% and 26.9%, respectively). In every case, the 5-km scale predictors were ranked as having a more significant influence on lek occurrence than the 1-km scale. Other factors of importance included topographic roughness (9.7% permutation importance), and the proportion of human disturbance at the 5-km scale (5% permutation importance). Our study highlights the importance of large patches of grassland to support the occurrence of sharp-tailed grouse leks, and that a diverse set of habitat features are needed for sharp-tailed grouse management.
Introduction
Temperate grasslands are considered one of the most endangered biomes on earth [1], with land conversion for agricultural use as the primary driver of grassland loss [2]. In Canada, only 25–30% of original grasslands still exist [3]. The quality of remaining grasslands is also affected by a variety of land uses that can decrease their habitat quality without necessarily destroying them. These land uses include unsustainable grazing, and energy extraction and distribution infrastructure needed to distribute energy from extraction sites, which can add additional anthropogenic features to the landscape including fencing, wells, turbines, transmission lines, and roads [3]. The presence, operation, and maintenance of these features and practices can create additional challenges for grassland species, including sensory disturbances and increased mortality [4–6]. Unfortunately, how these additional anthropogenic features and practices affect many grassland species is not fully understood.
Habitat specialists seem to be particularly at risk due to anthropogenic habitat changes, and the consequences of habitat loss and degradation are easier to predict for specialists compared to generalists [7]. The sharp-tailed grouse (Tympanuchus phasianellus) can be found in grasslands and in open areas within the boreal forest across North America [8]; however, due to its lack of preference for specific vegetation species communities within these open habitats, it has typically been classified as a habitat generalist [8]. Despite being classified as a habitat generalist, sharp-tailed grouse have experienced population declines in certain regions over the last few decades, particularly at the southern and western edges of their range [9, 10]. Habitat loss and fragmentation are likely principal factors causing the declines of these sharp-tailed grouse populations [9, 10]. However, part of the challenge associated with managing habitat of generalist species is that habitat use plasticity by these species may require region-specific research to inform conservation and management [8].
A typical unit used when managing sharp-tailed grouse and their habitat is known as the “breeding complex”, which is focused on their mating grounds (hereafter, leks) and typically a 2-km radius around the leks [8, 11]. Leks are communal display arenas where males compete for females; males show high site fidelity to the same lek area over the years [12]. Sharp-tailed grouse home ranges change throughout the year, but males spend the majority of the year in close proximity to the lek site [8, 9, 13]. Once a female has mated she will typically travel 1–2 kms away from the lek to nest [14, 15]. Due to the central role of leks in the breeding complex and the high detectability of male displays, leks are excellent units for the study of sharp-tailed grouse habitat use and subsequently, management [11]. Understanding what features sharp-tailed grouse select at and around lek sites can help delineate important habitat. However, due to the variability of habitats and landscapes used by the seven sharp-tailed grouse subspecies [8], the consistency of features selected for lekking may differ within each subspecies range.
Here we examined habitat features influencing lek occurrence for the plains sharp-tailed grouse (T.p. jamesi) in southern Saskatchewan, Canada. The plains sharp-tailed grouse inhabits primarily shrubby grasslands across the Great Plains of North America, and their leks are usually found in areas with short grasses, often associated with shrubs, on natural rises [10, 16, 17]. Female grouse require the presence of tall vegetation or woody shrubs for nesting and brood-rearing, though these features are typically found within larger open grassland complexes [18]. Nesting habitat contrasts with lek sites, whereby leks may be abandoned if too much woody vegetation is accumulated [19]. Fine-scale models that include features such as vegetation height exist for predicting suitable plains sharp-tailed grouse habitat, but these models focus primarily on nesting and brood-rearing habitat [20]. Areas with tall residual grasses are considered optimal for sharp-tailed grouse nesting and brood rearing, whereas approximately 5–10% shrub cover is considered optimal for wintering habitat [20]. However, the outcomes of these fine-scale modeling efforts are often difficult or impossible to extrapolate over a large area to predict sharp-tailed grouse habitat and manage it appropriately.
Our study used a combination of field surveys and remotely sensed landcover and topographic data to examine multiple habitat factors that are predicted to influence sharp-tailed grouse lek occurrence. We acquired lek information using contemporary (2018–2019) and historical field surveys (1990–2004), government pre-development surveys (1995–2016), and citizen science data (2017–2019) in the prairie ecoregion of Saskatchewan. As a generalist species, sharp-tailed grouse are less likely to be reliant on particular vegetation species, so we focused on using coarser land cover-based habitat assessments. These landscape variables are easy to monitor and acquire at large scales, making this type of analysis easier to apply for decision making over large landscapes. We modelled of the suitability of habitat for leks across the grasslands of southern Saskatchewan, Canada using a Habitat Suitability Index (HSI). Based on the HSI, we determined the relative rankings and importance of different habitat features for predicting the suitability of a site for leks. Lek sites are only one part of the breeding complex, so we predicted that leks would be influenced more by their surrounding habitat features than those directly at the lek location.
Methods
Study area
Our study area encompassed the prairie ecozone in southern Saskatchewan, Canada (latitude range 49 to 52° and longitude range -101 to -110°) and included an area of approximately 240,967 km2. Southern Saskatchewan receives an average of 395 mm of precipitation per year, with most falling in the month of June, and the average maximum temperature in the summer is approximately 25.5°C [21]. The study area consists of two major land-uses, annual crop production and grazing by domestic cattle, with an extensive road network and other smaller land-uses including oil and gas extraction, urban and rural habitations, and mining. Our study area is in the northeastern range of the plains subspecies of sharp-tailed grouse [8].
Historical surveys
The Saskatchewan Ministry of Environment (ENV) conducted sharp-tailed grouse lek surveys across the prairie and parkland ecoregions of Saskatchewan from 1958 to 2004. These surveys were used to develop the framework for our survey protocols and locations. These historic surveys were conducted within typically township-sized (approximately 41.4 km2) predefined survey blocks that included a mix of grazed grassland and annual cropland (two of the dominant land uses in Saskatchewan). Driving surveys were conducted in April and May from one hour before sunrise until two hours after sunrise on days without rain and wind speeds below 25 km/h. Stops were conducted every 1.6 km (1 mile) for a minimum of two minutes to listen and visually survey for leks. Once a lek was discovered, surveyors recorded the location as either a quarter-section (a 800m x 800m unit of land division) or a GPS location once this technology became widely available. Counts of both male and female grouse in attendance were conducted, and if possible a flush count, in which birds were made to fly away from the lek, was also done. Each block was surveyed twice within a season when possible. Not all blocks were surveyed consistently throughout the program, and new blocks were added as the program matured.