Translator Disclaimer
20 April 2016 Collision avoidance by migrating raptors encountering a new electric power transmission line
Author Affiliations +
Abstract

Avian collisions with overhead power lines are of conservation concern, particularly in migration corridors. We studied potential collisions where an existing power line supported by towers 20–25 m tall was replaced by the Susquehanna-Roseland line (S-R line), a new line with towers 55–60 m tall. The S-R line crosses Kittatinny Ridge, a corridor for raptors migrating south through New Jersey and Pennsylvania, USA. We hypothesized that the S-R line, which on Kittatinny Ridge includes markers designed to increase its visibility to birds, would cause migrating raptors to react in 1 of 3 ways: (1) to not alter flight elevation, but to pass safely through the S-R wire zone; (2) to not alter flight elevation, and to not pass safely through the wire zone, leading to collisions; or (3) to alter flight elevation and to pass safely above or below the S-R wire zone. To evaluate these hypotheses, we recorded the flight elevations of migrating raptors in 2013 before construction of the S-R line and in 2014 postconstruction. Preconstruction, we recorded 3,698 raptor crossings. Most raptors (72%) crossed above the anticipated S-R wire zone. Some (24%) passed through the anticipated S-R wire zone, and a few (4%) passed below the anticipated S-R wire zone. Postconstruction, we recorded 4,482 crossings. Most raptors (92%) crossed above the S-R wire zone. A few passed through (5%) or below (3%) the S-R wire zone. Postconstruction, raptors responded to the new line by flying higher than they had when traversing the previous line. We did not observe any collisions. Altered flight elevations and the absence of observed collisions supported hypothesis 3. If similar patterns occur at other lines that cross diurnal migration corridors along ridges, then future monitoring may be better focused on potentially riskier settings, such as areas where migrating birds do not have deflected winds to assist with gaining elevation.

INTRODUCTION

Avian collisions with power transmission lines (≥60 kilovolts [kV]; APLIC 2012) are a global conservation concern (Quinn et al. 2011, Barrientos et al. 2012, Rioux et al. 2013). Large, heavy-bodied species such as swans, pelicans, herons, and cranes are generally thought to be more susceptible to power line collisions than smaller, more maneuverable species (Jenkins et al. 2010, APLIC 2012; but see Pearse et al. 2016), although this may be partly a function of detection bias limiting incidental observations of smaller species (Drewitt and Langston 2008, Rogers et al. 2014). Collisions involving raptors have occurred (Mojica et al. 2009, APLIC 2012), but appear to be relatively uncommon compared with collisions involving other species groups. When encountering transmission lines, birds appear to see large-diameter energized wires (conductors) and avoid them by adjusting flight altitudes upward, subsequently colliding with smaller-diameter, less-visible overhead shield wires that are used for lightning protection (Jenkins et al. 2010, APLIC 2012). For example, across 3 studies, 72% of 373 observed collisions were with overhead shield wires (Faanes 1987, Pandey et al. 2008, Murphy et al. 2009). Power lines that bisect daily avian movement corridors, such as those between roosting and foraging sites, have historically been most associated with avian collisions (Bevanger and Brøseth 2004, Stehn and Wassenich 2008, APLIC 2012), with the risk of collision exacerbated in low light, fog, and inclement weather (Savereno et al. 1996, APLIC 2012, Hüppop and Hilgerloh 2012). The effects of power lines that bisect seasonal movement corridors used during migration have not been thoroughly investigated (Rogers et al. 2014).

Here, we describe the movements of raptors flying perpendicularly across a section of new power line crossing Kittatinny Ridge in New Jersey, USA, an important navigational feature traversed annually by tens of thousands of raptors travelling south during fall migration (Van Fleet 2001, Bildstein 2006, 2008). The new Susquehanna-Roseland line (S-R line) was built within the right-of-way of an existing power line that was supported by towers 20–25 m tall, which were removed and replaced by the 55–60 m tall towers that support the S-R line. From the center of Pennsylvania's eastern border, Kittatinny Ridge extends 300 km southwest through 12 Pennsylvania counties (National Audubon Society 2013) in the central Appalachian Mountains, and northeast into New Jersey. The ridge rises 425–475 m above sea level, 250–300 m above farm-filled valleys on each side, and is covered in second-growth deciduous forest ∼20 m tall. The geography of the area creates updrafts when westerly winds hit Kittatinny Ridge. Raptors glide southwest on these deflected winds, avoiding powered flight and thus conserving energy during migration (Van Fleet 2001, Bildstein 2006, 2008). Kittatinny Ridge is an Important Bird Area (National Audubon Society 2013) and is home to Hawk Mountain, a research center focused on raptor conservation science and education worldwide (Hawk Mountain 2013). The movement of migrating raptors along this high-traffic corridor has been monitored since 1934 (Bildstein 2008), lending Kittatinny Ridge important social as well as conservation values.

The newly constructed power line, which is 2.5 times taller than the previous line and has a wire zone entirely above the forest canopy, poses a collision risk for the thousands of raptors that migrate along Kittatinny Ridge annually. We hypothesized that raptors would react to the S-R line in 1 of 3 ways: (1) that raptors would not alter their flight elevations above ground level, but would pass safely through the S-R wire zone; (2) that raptors would not alter their flight elevations and would not pass safely through the S-R wire zone, leading to collisions; or (3) that raptors would alter their flight elevations to pass safely above or below the S-R wire zone. To evaluate our competing hypotheses, we collected data on the flight elevations of migrating raptors prior to construction of the S-R line as raptors traversed an existing line, and after construction as raptors traversed the S-R line. This design allowed us to evaluate whether raptors changed their flight elevations with increased obstacle height.

METHODS

The S-R line was built within the right-of-way of an existing line that was supported by towers that were 20–25 m tall. The existing line was removed and replaced by the S-R line during February through April of 2014, between the 2 fall migration seasons that we monitored. The S-R line included a new 230 kV line and a new 500 kV line that were installed together on towers 55–60 m tall. The line was composed of 4 parallel planes of wires (Figure 1A), with the top plane of wires composed of 2 optical ground wires (OPGWs), each 1.9 cm in diameter. The OPGWs provided lightning protection to the energized wires below, and supported bundles of fiber-optic communication lines. The presence of fiber-optic bundles increased the diameter of the wires, potentially increasing their visibility to birds. On the S-R line, the OPGWs were marked every 10 m with Swan Flight Diverters (Preformed Line Products, Cleveland, Ohio, USA) on the 3 spans (totaling 1.4 km ) crossing Kittatinny Ridge, to help to increase the visibility of the line to flying birds (Figure 1B). The Swan Flight Diverters were staggered on each OPGW, so that, although they were at 10 m intervals on each OPGW, they appeared to be at 5 m spacing when viewed perpendicularly to the line. The lower 3 planes of wires were composed of bundled conductors consisting of 3 wires, each 3.9 cm in diameter, connected via spacers that separated the conductors by 60.0 cm in a triangular configuration (Figure 1C). The 4 sets of wires occurred at heights from 25 m (lowest) to 60 m (highest) above the contours of Kittatinny Ridge, creating an S-R wire zone from 25 to 60 m above ground level. In contrast to the previously existing line, the wires of which were partially shielded by the surrounding tree canopy, the entire S-R wire zone is above the canopy and in the potential flight path of migrating raptors.

FIGURE 1.

(A) Schematic of structures supporting the Susquehanna-Roseland 230/500 kilovolt (kV) transmission line (S-R line) crossing Kittatinny Ridge, New Jersey, USA. Numbers indicate locations of wire planes. (B) The upper crossarm, wire plane #1, was composed of optical ground wires marked with Swan Flight Diverters (SFDs). The SFDs were 0.2 m tall at the widest point. (C) The lower 3 crossarms, wire planes #2, #3, and #4, supported single (230 kV) and bundled (500 kV) conductors, with bundled conductors separated by a 60 cm spacer.

i0010-5422-118-2-402-f01.tif

We reviewed historical fall migration count data from nearby Raccoon Ridge (HMANA 2013) to identify a survey period (September 1 through November 25) that was likely to document 95% of raptors migrating along Kittatinny Ridge. In 2013, the initiation of counts was delayed by permitting arrangements related to construction of the S-R line. This resulted in preconstruction surveys being conducted from September 24 through November 25 in 2013, and postconstruction surveys being completed from September 1 through November 25 in 2014. Variation in survey periods can lead to bias in migration counts, but only if the variation is not accounted for in analyses (Crewe et al. 2016). We considered the consequences of survey duration by evaluating differences in counts for Broad-winged Hawks (Buteo platypterus), which could have been missed in our 2013 counts because they migrate early in the fall season (HMANA 2013). We followed the Hawk Migration Association of North America's (HMANA) protocols for counting migrating raptors (HMANA 2014), surveying from 08:00 to 16:00, Monday through Friday.

We counted raptors passing between 500 m west of Kittatinny Ridge and 650 m east of the ridge in northwestern New Jersey, USA (Figure 2). These distances allowed us to count all raptors flying along the contours of Kittatinny Ridge from the top of the ridge to the valley floors on either side. We used observers trained and experienced in HMANA methodology. During each count, we used 2 observers simultaneously, with 1 observer counting raptors passing along the northwestern side of Kittatinny Ridge, and 1 observer counting raptors passing along the southeastern side. One observer was the same person during all counts, ensuring consistency across the entire study, while the second observer changed among counts. Observers were stationed at the top of Kittatinny Ridge, within an area cleared of vegetation as required for safe installation and operation of the S-R line. To avoid double-counting individual raptors, observers communicated via radio as individual birds crossed the ridge. Observers identified raptors to the lowest taxonomic level possible, and used a laser range finder (RX-1000i TBR W/DNA; Leupold & Stevens, Beaverton, Oregon, USA) equipped with a clinometer to identify the distance and angle to each bird as it crossed the power line. This enabled precise vertical and horizontal locations to be identified for each raptor as it traversed the S-R wire zone. Thus, we quantified each raptor's position relative to the S-R wires in both years, even though the line was not yet in place during the 2013 surveys.

FIGURE 2.

Locations of observers, study spans, and study site within the region for recording flight locations of migrating raptors crossing the Susquehanna-Roseland 230/500 kilovolt (kV) transmission line (S-R line) on Kittatinny Ridge, New Jersey, USA (Base map: World Street Map; ESRI, Redlands, California, USA).

i0010-5422-118-2-402-f02.tif

We used chi-square (χ2) tests to evaluate any differences in the proportions of raptors passing above the S-R wire zone, within the S-R wire zone, and below the S-R wire zone in 2013 vs. 2014. We conducted χ2 tests that included all raptors observed, and separate tests that evaluated subsets of raptors by species or taxonomic group. Multiple comparisons of subsets of data increase the probability of type I error. To address this concern, we used a Bonferroni correction (Sokal and Rohlf 1995), dividing our initial significance level (α = 0.05) by the number of tests that we conducted (5), to yield a corrected significance level of α = 0.01. We used the seasonal pattern of detection of individual species to consider the consequences of the shorter sampling period in 2013 (63 days) compared with 2014 (86 days).

We used a Geographic Information System (GIS; ArcGIS Desktop 10.2, ESRI, Redlands, California, USA) and Power Line Systems – Computer Aided Design and Drafting (PLS-CADD; Power Line Systems, Madison, Wisconsin, USA) to visually display the accumulated spatial locations of raptors crossing the S-R line. To do this, we used a 9 m (1-arc-second) digital elevation model to calculate the absolute elevation above sea level for each raptor. We then used the Linear Referencing Toolbox in ArcGIS and ET GeoWizards (ET Spatial Techniques, Pretoria, South Africa) to model location data in 3-dimensional (3-D) space. We integrated the 3-D raptor observation data into PLS-CADD, facilitating simultaneous evaluation of raptor flight elevation data and an engineering model of the S-R transmission line, depicting the wires and supporting towers. The use of PLS-CADD enabled us to precisely identify the location of the S-R wire zone in 3-D space, and thus to precisely quantify a migrating raptor's potential collision risk where flight elevations transected the S-R wire zone, despite the curve of the wires. Because wires sag between towers, the use of PLS-CADD allowed us to identify with certainty when a raptor flying below the height of the top of the towers was nevertheless flying above a sagging wire.

RESULTS

We did not observe any raptors collide with any wires. During 9 weeks of observation in 2013, and 12 weeks of observation in 2014, we recorded 3,698 preconstruction (2013) and 4,482 postconstruction (2014) raptor crossings of the S-R line survey area (Table 1, Figure 3). Our study showed a 21% increase in the number of raptors counted from 2013 to 2014, driven largely by a 9,514% increase in the number of Broad-winged Hawks counted. Specifically, only 7 Broad-winged Hawks were recorded in 2013, and nearly all of the 673 Broad-winged Hawks counted in 2014 were counted prior to the initiation date of the 2013 preconstruction surveys.

TABLE 1.

Flight elevation relative to the S-R wire zone of the Susquehanna-Roseland 230/500 kilovolt (kV) transmission line (S-R line) for raptors crossing the S-R line along Kittatinny Ridge, New Jersey, USA. The 2013 columns indicate preconstruction data, and the 2014 columns indicate postconstruction data.

i0010-5422-118-2-402-t01.tif

a

PD indicates the percent difference in the number of raptors counted between 2013 and 2014.

FIGURE 3.

Flight locations of migrating raptors (gray dots) crossing the Susquehanna-Roseland 230/500 kilovolt (kV) transmission line (S-R line) on Kittatinny Ridge, New Jersey, USA, in (A) 2013, with towers 20–25 m tall, and (B) 2014, with towers 55–60 m tall. The tree canopy (not illustrated) was 20–25 m tall in both years.

i0010-5422-118-2-402-f03.tif

In 2013, most (72%) raptors crossed above the S-R wire zone. Some (24%) crossed within the S-R wire zone, and a few (4%) crossed below. In 2014, most (92%) raptors again crossed above the S-R wire zone, but a few crossed within (5%) or below (3%) the S-R wire zone. Raptors were more likely to pass above the S-R wire zone following construction of the S-R line (χ2 = 613.6, df = 2, P < 0.001). Two species, Turkey Vulture (Cathartes aura) and Sharp-shinned Hawk (Accipiter striatus), included enough crossings within and below the S-R wire zone to conduct species-specific analyses (i.e. n ≥ 5 for all count categories). Both species passed more frequently through the preconstruction anticipated S-R wire zone than through the postconstruction actual S-R wire zone, with significantly higher proportions passing above the S-R wire zone postconstruction (Turkey Vulture: χ2 = 458.0, df = 2, P < 0.001; Sharp-shinned Hawk: χ2 = 45.6, df = 2, P < 0.001). These 2 species accounted for most of the data for vultures (90%) and accipiters (86%), respectively, so we did not conduct family-level analyses for these 2 groups. Individual species within 2 taxonomic groups, buteos and falcons, did not include enough crossings within and below the S-R wire zone to consider any species-specific differences, so we evaluated these groups at a higher level, and found similar patterns. Individuals in both groups were more likely to pass above the S-R wire zone following construction (buteos: χ2 = 50.6, df = 2, P < 0.001; falcons: χ2 = 19.6, df = 2, P < 0.001). The other groups examined, ospreys, eagles, and harriers, did not include enough crossings within and below the S-R wire zone to be evaluated statistically, but qualitatively followed the patterns of the more abundant species.

DISCUSSION

We hypothesized that raptors encountering the newly constructed S-R line where the line crossed Kittatinny Ridge would either (1) fly safely through the S-R wire zone, (2) collide with wires in the S-R wire zone, or (3) avoid the S-R wire zone by flying above or below all wires. In comparing preconstruction (2013) flight elevations with postconstruction (2014) flight elevations, we found that most of the raptors that we observed avoided the postconstruction S-R wire zone by passing above it, supporting hypothesis 3. Specifically, hypothesis 3 was supported by a 28% increase in the proportion of birds flying above the S-R wire zone postconstruction compared with preconstruction values. Although 21% more raptors were observed in 2014 than in 2013, removing Broad-winged Hawks from the analysis reduced this difference to 3%. Therefore, we believe that the difference in flight heights between years represents a behavioral response by raptors to avoid colliding with the S-R line. Shifting flight elevation to pass above the S-R wire zone suggests that raptors were able to identify the full extent of the S-R wire zone and to simply alter their flight altitudes upward to pass higher over the S-R wire zone postconstruction. This is true even though the preexisting line protruded only partially above the surrounding forest, while the postconstruction wire zone occurred entirely above the top of the surrounding forest canopy.

In cases where avian collisions with power lines have been documented, most have involved collisions with overhead static wires (Faanes 1987, Pandey et al. 2008, Murphy et al. 2009). The S-R line included OPGWs instead of traditional overhead static wires, and included Swan Flight Diverters on the OPGWs. Both the OPGWs and the Swan Flight Diverters increased the diameter of the top wires relative to traditional, unmarked overhead static wires. This larger diameter may have made the top wires more visible, enabling migrating raptors to detect and avoid them. The conductors on the S-R line were composed of 3 wires bundled together, increasing their collective diameter, and likely also increasing visibility and avoidance. These engineering features likely enabled diurnal migrating raptors to detect and fly above the S-R line. The implications of our study for future placement of transmission lines are substantial. Specifically, our results suggest that well-marked lines, even within high traffic corridors, may pose little collision risk to diurnally migrating raptors, although the cumulative energetic costs associated with making a series of adjustments in flight elevation as a raptor encounters transmission lines throughout its migratory route have not been explored. However, because we did not also evaluate a power line of similar height to the S-R line in similar circumstances, but without line marking, OPGWs, and bundled conductors, we do not know the extent to which any of these specific features contributed to the apparent visibility of the S-R line.

Avian collisions with power lines are associated primarily with transmission systems (≥60 kV; APLIC 2012), which typically exceed the height of distribution lines by 2–4 times. Despite the height difference, the influence of power line height on collision risk has not been well explored. A primary obstacle to evaluating the effects of line height is that studies in which sufficient numbers of carcasses are found for analyses typically involve lines of similar height across the study area (e.g., Mojica et al. 2009, Sporer et al. 2013, Rogers et al. 2014), and large studies of different types of lines typically include little data on actual collision mortality (e.g., Quinn et al. 2011), reducing the inference from rare events to population-level effects (Loss 2016). A second obstacle is that most collisions with transmission lines involve overhead shield wires (Faanes 1987, Pandey et al. 2008, Murphy et al. 2009), which are rarely present on distribution systems, confounding the effects of height with the effects of other aspects of line design. One study that explicitly evaluated the effects of line marking on transmission and distributions lines found no difference when line type was included in multivariate analyses (Barrientos et al. 2012), and thus no implications of line height. Studies of collisions at wind energy facilities and cell towers have shown much stronger effects of structure height on collision risk, with taller structures associated with greater risk (de Lucas et al. 2008, Gehring et al. 2011). The tallest cell towers can be >300 m high (Gehring et al. 2011), and the rotor-swept areas of the tallest terrestrial wind turbines can be as high as 200 m (New et al. 2015), 7.5 and 5.0 times the height of typical transmission lines, respectively. This difference in structure design and associated biological consequences highlights the reality that problems and solutions for one aspect of tall structures or electric energy generation and transmission do not necessarily transfer well to other aspects of the electricity industry, particularly given the influence of lighting type or siting on behavior and ultimately collision risk (Gehring et al. 2009, Smith and Dwyer 2016, Watson et al. 2016).

Energy infrastructure can raise conservation concerns when tall structures occur within migration corridors (de Lucas et al. 2004, Johnston et al. 2014, Rogers et al. 2014). Typical preconstruction surveys use radar or flight position estimates together with estimates of the future location of energy infrastructure to evaluate preconstruction vs. postconstruction differences in risk in relation to flight elevation. Typical postconstruction surveys seek carcasses to infer collision risk. Our study included the novel use of a laser range finder equipped with a clinometer combined with the novel use of PLS-CADD to precisely identify the locations of raptors in 3-D space relative to the S-R wire zone. Because preconstruction surveys of this type are relatively rare, our study provides the first example of merging these technologies. Other studies could benefit from integrating PLS-CADD into GIS methodology and analyses to more precisely identify the locations of raptors and potential obstacles in 3-D space. Adopting these techniques may increase the ability of conservation scientists and resource managers to identify the specific characteristics of energy infrastructure that affect avian collision risk, facilitating the focusing of mitigation efforts to greatest effect. For example, if diurnal raptors are consistently found to avoid well-marked transmission lines in migration corridors, then the substantial effort and expense required to conduct postconstruction monitoring may be better invested in researching and mitigating more pressing risks to migrating birds (Loss et al. 2014a, Loss 2016).

Annual numbers of avian collisions with power lines suggested by meta-analyses are substantial; for example, between 8 and 57 million annually in the U.S. (Loss et al. 2014b), and between 2.5 and 25.6 million annually in Canada (Rioux et al. 2013). Studies that have independently supported the findings of these meta-analyses typically have involved research into daily movements in breeding areas or wintering areas (e.g., Mojica et al. 2009, Barrientos et al. 2012, Sporer et al. 2013), or at migratory stopover sites (e.g., Stehn and Wassenich 2008, Murphy et al. 2009). Few published studies have explicitly considered collision with power lines specifically during migratory flight (but see Rogers et al. 2014), so we investigated a site where avian collisions with a new power transmission line were of potential concern with regard to migrating raptors. During migration, studies have also examined avian collisions with buildings (Loss et al. 2014b), cell towers (Gehring et al. 2009, 2011), and wind turbines (Pearce-Higgins et al. 2012, Johnston et al. 2014, Pearse et al. 2016). Specifically with respect to wind turbines, but with broad conceptual implications for avian collisions in general, Piorkowski et al. (2012) advocated 4 research priorities for wind energy and migratory wildlife: standardize protocols and definitions; develop new methods and models for assessing and forecasting risk; document lethal and sublethal effects; and improve access for researchers. We tried to address these goals with this project. Specifically, we used new methods to quantify avian responses to an anthropogenic structure within a migration corridor, we investigated lethal effects, and we relied on cooperation with industry to conduct our study. To maximize the applicability of information across studies, we encourage future researchers to also explicitly consider the 4 research priorities of Piorkowski et al. (2012) when designing studies of collisions involving other sites, focal species, and possible anthropogenic obstacles.

ACKNOWLEDGMENTS

We thank J. Scheivert, S. McConnell, and Z. Bordner for conducting the fieldwork described in this study. We are grateful to A. Bebault (National Park Service), J. Smith, and 2 anonymous reviewers for comments on an early report which guided and improved this work. H. Bates and R. Tedesco assisted in drafting and PLS-CADD modeling.

Funding statement: This study was funded by PPL Electric Utilities Corporation, Allenstown, Pennsylvania, USA, and EDM International, Fort Collins, Colorado, USA. No funders had any input into the content of the manuscript, nor required approval prior to submission or publication.

Ethics statement: This study was purely observational. Because we did not attempt to approach our study animals nor to modify their behavior in any way, we did not have an IACUC protocol.

Author contributions: J.L., C.E.R., R.E.H., J.L.C., and M.A.L. conceived the idea, design, and experiment (supervised research, formulated question or hypothesis); J.L., C.E.R., R.E.H., J.L.C., and M.A.L. performed the experiments (collected data, conducted the research); R.E.H., J.L.C., M.A.L., and J.F.D. wrote the paper; J.L., C.E.R., R.E.H., J.L.C., and D.D.A. developed or designed the methods; R.E.H., J.L.C., D.D.A., and J.F.D. analyzed the data; and J.L., C.E.R., R.E.H., J.L.C., and J.F.D. contributed substantial materials, resources, or funding.

LITERATURE CITED

1.

APLIC (Avian Power Line Interaction Committee) (2012). Reducing Avian Collisions with Power Lines: The State of the Art in 2012. Edison Electric Institute, Washington, DC, USA. Google Scholar

2.

Barrientos, R., C. Ponce, C. Palacín, C. A. Martín, B. Martín, and J. C. Alonso (2012). Wire marking results in a small but significant reduction in avian mortality at power lines: A BACI designed study. PLOS One 7:e32569.  10.1371/journal.pone.0032569 Google Scholar

3.

Bevanger, K., and H. Brøseth (2004). Impact of power lines on bird mortality in a subalpine area. Biodiversity and Conservation 27:67–77. Google Scholar

4.

Bildstein, K. L. (2006). Migrating Raptors of the World: Their Ecology and Conservation. Cornell University Press, Ithaca, NY, USA. Google Scholar

5.

Bildstein, K. L. (2008). A brief history of raptor conservation in North America. In State of North America's Birds of Prey (K. L. Bildstein, J. P. Smith, E. Ruelas Inzunza, and R. R. Veit, Editors). Series in Ornithology No. 3, American Ornithologists' Union, Washington, DC, USA, and Nuttall Ornithology Club, Cambridge, MA, USA.pp. 5–36. Google Scholar

6.

Crewe, T. L., D. Lepage, and P. D. Taylor (2016). Effect of sampling effort on bias and precision of trends in migration counts. The Condor: Ornithological Applications 118:117–138. Google Scholar

7.

de Lucas, M., G. F. E. Janss, and M. Ferrer (2004). The effects of a wind farm on birds in a migration point: The Strait of Gibraltar. Biodiversity and Conservation 13:395–407. Google Scholar

8.

de Lucas, M., G. F. E. Janss, and M. Ferrer (2008). Collision fatality of raptors in wind farms does not depend on raptor abundance. Journal of Applied Ecology 45:1695–1703. Google Scholar

9.

Drewitt, A. L., and R. H. W. Langston (2008). Collision effects of wind-power generators and other obstacles on birds. Annals of the New York Academy of Sciences 1134:233–266. Google Scholar

10.

Faanes, C. A. (1987). Bird behavior and mortality in relation to power lines in prairie habitats. Fish and Wildlife Technical Report 7, United States Department of the Interior, Publications Unit, Fish and Wildlife Service, Washington, DC, USA. Google Scholar

11.

Gehring, J., P. Kerlinger, and A. M. Manville (2009). Communication towers, lights, and birds: Successful methods of reducing the frequency of avian collisions. Ecological Applications 19:505–514. Google Scholar

12.

Gehring, J., P. Kerlinger, and A. M. Manville (2011). The role of tower height and guy wires on avian collisions with communication towers. Journal of Wildlife Management 75:848–855. Google Scholar

13.

Hawk Mountain(2013). Hawk Mountain 2013 Annual Report. Hawk Mountain Sanctuary Association, Kepton, PA, USA. Google Scholar

14.

HMANA (Hawk Migration Association of North America)(2013). Raccoon Ridge 2011–2013 Hawkwatch Site Profile.  http://hawkcount.org/sitesel.php Google Scholar

15.

HMANA (Hawk Migration Association of North America)(2014). HMANA Data Form Instructions.  http://www.hmana.org/data-submission/ Google Scholar

16.

Hüppop, O., and G. Hilgerloh (2012). Flight call rates of migrating thrushes: Effects of wind conditions, humidity and time of day at an illuminated offshore platform. Journal of Avian Biology 43:85–90. Google Scholar

17.

Jenkins, A. R., J. J. Smallie, and M. Diamond (2010). Avian collisions with power lines: A global review of causes and mitigation with a South African perspective. Bird Conservation International 20:263–278. Google Scholar

18.

Johnston, N. N., J. E. Bradley, and K. A. Otter (2014). Increased flight altitudes among migrating Golden Eagles suggest turbine avoidance at a Rocky Mountain wind installation. PLOS One 9:e93030.  10.1371/journal.pone.0093030 Google Scholar

19.

Loss, S. R. (2016). Avian interactions with energy infrastructure in the context of other anthropogenic mortality sources. The Condor: Ornithological Applications 118:424–432. Google Scholar

20.

Loss, S. R., T. Will, S. S. Loss, and P. P. Marra (2014a). Bird–building collisions in the United States: Estimates of annual mortality and species vulnerability. The Condor: Ornithological Applications 16:8–23. Google Scholar

21.

Loss, S. R., T. Will, and P. P. Marra (2014b). Refining estimates of bird collision and electrocution mortality at power lines in the United States. PLOS One 9:e101565.  10.1371/journal.pone.0101565 Google Scholar

22.

Mojica, E. K., B. D. Watts, J. T. Paul, S. T. Voss, and J. Pottie (2009). Factors contributing to Bald Eagle electrocutions and line collisions on Aberdeen Proving Ground, Maryland. Journal of Raptor Research 43:57–61. Google Scholar

23.

Murphy, R. K., S. M. McPherron, G. D. Wright, and K. L. Serbousek (2009). Effectiveness of avian collision averters in preventing migratory bird mortality from powerline strikes in the central Platte River, Nebraska. Final Report to the U.S. Fish and Wildlife Service, Grand Island, Nebraska, USA. Google Scholar

24.

National Audubon Society(2013). Audubon Important Bird Areas: Kittatinny Ridge Site Profile. National Audubon Society, Manhattan, NY, USA.  http://netapp.audubon.org/IBA/Site/1157 Google Scholar

25.

New, L., E. Bjerre, B. Millsap, M. C. Otto, and M. C. Runge (2015). A collision risk model to predict avian fatalities at wind facilities: An example using Golden Eagles, Aquila chrysaetos. PLOS One 10:e0130978.  10.1371/journal.pone.0130978 Google Scholar

26.

Pandey, A., R. E. Harness, and M. K. Schriner (2008). Bird strike indicator field deployment at the Audubon National Wildlife Refuge in North Dakota: Phase two. California Energy Commission, Public Interest Energy Research Energy-Related Environmental Research Program, CEC-500-2008-020, Sacramento, CA, USA. Google Scholar

27.

Pearce-Higgins, J. W., L. Stephen, A. Douse, and R. H. W. Langston (2012). Greater impacts of wind farms on bird populations during construction than subsequent operation: Results of a multi-site and multi-species analysis. Journal of Applied Ecology 49:386–394. Google Scholar

28.

Pearse, A. T., D. A. Brandt, and G. L. Krapu (2016). Wintering Sandhill Crane exposure to wind energy development in the central and southern Great Plains, USA. The Condor: Ornithological Applications 118:391–401. Google Scholar

29.

Piorkowski, M. D., A. J. Farnsworth, M. F. Fry, R. W. Rohrbaugh, J. W. Fitzpatrick, and K. V. Rosenberg (2012). Research priorities for wind energy and migratory wildlife. Journal of Wildlife Management 66:451–456. Google Scholar

30.

Quinn, M., S. Alexander, N. Heck, and G. Chernoff (2011). Identification of bird collision hotspots along transmission power lines in Alberta: An expert-based geographic information system (GIS) approach. Journal of Environmental Informatics 18:12–21. Google Scholar

31.

Rioux, S., J-P. L. Savard, and A. A. Gerick (2013). Avian mortalities due to transmission line collisions: A review of current estimates and field methods with an emphasis on applications to the Canadian electric network. Avian Conservation and Ecology 8:7.  http://dx.doi.org/10.5751/ACE-00614-080207 Google Scholar

32.

Rogers, A. M., M. R. Gibson, T. Pockette, J. L. Alexander, and J. F. Dwyer (2014). Scavenging of migrant carcasses in the Sonoran Desert. Southwestern Naturalist 59:542–547. Google Scholar

33.

Savereno, A. J., L. A. Savereno, R. Boettcher, and S. M. Haig (1996). Avian behavior and mortality at power lines in coastal South Carolina. Wildlife Society Bulletin 24:636–648. Google Scholar

34.

Smith, J. A., and J. F. Dwyer (2016). Avian interactions with renewable energy infrastructure: An update. The Condor: Ornithological Applications 118:411–423. Google Scholar

35.

Sokal, R. R., and F. J. Rohlf (1995). Biometry, third edition. W. H. Freman, New York, NY, USA. Google Scholar

36.

Sporer, M. K., J. F. Dwyer, B. D. Gerber, R. E. Harness, and A. K. Pandey (2013). Marking power lines to reduce avian collisions near the Audubon National Wildlife Refuge, North Dakota. Wildlife Society Bulletin 37:796–804. Google Scholar

37.

Stehn, T. V., and T. Wassenich (2008). Whooping Crane collisions with power lines: An issue paper. Proceedings of the North American Crane Workshop 10:25–36. Google Scholar

38.

Van Fleet, P. K. (2001). Geography of diurnal raptors migrating through the valley-and-ridge province of central Pennsylvania 1991–1994. In Hawkwatching in the Americas ( K. L. Bildstein and D. Klem, Jr., Editors). Hawk Migration Association of North America, North Wales, PA, USA. pp. 23–49. Google Scholar

39.

Watson, M. J., D. R. Wilson, and D. J. Mennill (2016). Anthropogenic light is associated with increased vocal activity by nocturnally migrating birds. The Condor: Ornithological Applications 118:338–344. Google Scholar
Jeff Luzenski, Claudia E. Rocca, Richard E. Harness, John L. Cummings, Daryl D. Austin, Melissa A. Landon, and James F. Dwyer "Collision avoidance by migrating raptors encountering a new electric power transmission line," The Condor 118(2), 402-410, (20 April 2016). https://doi.org/10.1650/CONDOR-15-55.1
Received: 5 April 2015; Accepted: 1 January 2016; Published: 20 April 2016
JOURNAL ARTICLE
9 PAGES


SHARE
ARTICLE IMPACT
Back to Top