Abstract:Animals select and use habitats based on environmental features relevant to their ecology and behavior. For animals that use acoustic communication, the sound environment itself may be a critical feature, yet acoustic characteristics are not commonly measured when describing habitats and as a result, how habitats vary acoustically over space and time is poorly known. Such considerations are timely, given worldwide increases in anthropogenic noise combined with rapidly accumulating evidence that noise hampers t… Show more
“…While we observed that traffic noise was a dominate component at many of our recording locations, other foreground and background sources were also present. As demonstrated by Job et al (2016), urban acoustic environments can be highly variable at small scales (i.e. street scales), although global trends have also been found on large scales (i.e.…”
Context Biophony is the acoustic manifestation of biodiversity, and humans interact with biophony in many ways. However, quantifying biophony across urban landscapes has proven difficult in the presence of anthrophony, or sounds generated by humans. Improved assessment methods are required to progress our understanding of the processes influencing biophony across a variety of spatial-temporal scales. Objectives We aimed to identify how the landscape influences biophony, as well as the total acoustic environment, along an urban to rural gradient. We designed the study to quantify how soundscapelandscape relationships change across a variety of spatial-temporal scales. Methods We recorded the afternoon acoustic environment during the spring of 2016 at 30 locations in the city of Innsbruck, Austria using a spatially balanced random sampling design. We quantified the total acoustic environment with the sound exposure level (SEL) metric, and developed a new metric, percent biophony (PB), to quantify biophony while avoiding noise bias. We quantified relationships with land cover (LC) classes, as well as a landscape index, distance to nature (D 2 N), across 10 scales. Results D 2 N within 1280 m best predicted PB, while both the LC class trees and D 2 N within 40 m best predicted SEL. PB increased more throughout the spring at locations with more natural surrounding LC, while PB did not change significantly at locations with more urban surrounding LC. Conclusions LC and composite indices can serve as reasonable predictors for the acoustic environment; however, the relationships are scale dependent. Mapping soundscapes can help to illustrate possible driving mechanisms and provide a valuable tool for urban management and planning.
“…While we observed that traffic noise was a dominate component at many of our recording locations, other foreground and background sources were also present. As demonstrated by Job et al (2016), urban acoustic environments can be highly variable at small scales (i.e. street scales), although global trends have also been found on large scales (i.e.…”
Context Biophony is the acoustic manifestation of biodiversity, and humans interact with biophony in many ways. However, quantifying biophony across urban landscapes has proven difficult in the presence of anthrophony, or sounds generated by humans. Improved assessment methods are required to progress our understanding of the processes influencing biophony across a variety of spatial-temporal scales. Objectives We aimed to identify how the landscape influences biophony, as well as the total acoustic environment, along an urban to rural gradient. We designed the study to quantify how soundscapelandscape relationships change across a variety of spatial-temporal scales. Methods We recorded the afternoon acoustic environment during the spring of 2016 at 30 locations in the city of Innsbruck, Austria using a spatially balanced random sampling design. We quantified the total acoustic environment with the sound exposure level (SEL) metric, and developed a new metric, percent biophony (PB), to quantify biophony while avoiding noise bias. We quantified relationships with land cover (LC) classes, as well as a landscape index, distance to nature (D 2 N), across 10 scales. Results D 2 N within 1280 m best predicted PB, while both the LC class trees and D 2 N within 40 m best predicted SEL. PB increased more throughout the spring at locations with more natural surrounding LC, while PB did not change significantly at locations with more urban surrounding LC. Conclusions LC and composite indices can serve as reasonable predictors for the acoustic environment; however, the relationships are scale dependent. Mapping soundscapes can help to illustrate possible driving mechanisms and provide a valuable tool for urban management and planning.
“…Future work on this application with SPreAD-GIS might benefit from altering the tool to place less importance on the wind factor (and adjust other factors as necessary). Future work might consider ground-truthing sound estimates during monthly siren tests using in situ microphone arrays similar to Job et al (2016). This would confirm or refute the importance of wind (and other factors), which in this example was highly significant, on the sound propagation estimates.…”
Section: Discussionmentioning
confidence: 82%
“…While this type of approach is efficient, it is not without its limits. Ultimately, the analysis is constrained by the fact that buffers are based on ideal, theoretical estimates of the distance from the siren that the siren noise will reach; these types of estimates do not factor in the intricacies of sound propagation (Webster, 2014) and the role of environmental factors such as topography, weather conditions (e.g., temperature, wind, humidity), and land cover (Job et al, 2016). Such factors influence citizens' ability to hear the sirens; e.g., Hodler (1982) observed that sirens were inaudible to Kalamazoo residents located upwind.…”
Section: Gis-based Extent and Coverage Modelingmentioning
confidence: 99%
“…In this way, sound propagation modeling to date has focused on ecological applications (i.e. soundscape ecology; Barber et al, 2010Barber et al, , 2011Job et al, 2016). Research applications in soundscape ecology led to the development of the GIS-based 'System for the Prediction of Acoustic Detectability' toolset or SPreAD-GIS (Reed et al, 2010(Reed et al, , 2012(Reed et al, , 2016.…”
Section: Gis-based Extent and Coverage Modelingmentioning
“…Furthermore, environmental features can affect the propagation and intensity of light and noise exposure. For instance, a study that mapped sound propagation from playbacks in three terrestrial habitats found forests had broader sound pressure level gradients than prairie or urban habitats due to more sound reflection and reverberation (Job et al, 2016). Seasonally changing environmental conditions could also alter an organism's response to sensory stimuli.…”
The extent of artificial night light and anthropogenic noise (i.e., “light” and “noise”) impacts is global and has the capacity to threaten species across diverse ecosystems. Existing research involving impacts of light or noise has primarily focused on noise or light alone and single species; however, these stimuli often co‐occur and little is known about how co‐exposure influences wildlife and if and why species may vary in their responses. Here, we had three aims: (1) to investigate species‐specific responses to light, noise, and the interaction between the two using a spatially explicit approach to model changes in abundance of 140 prevalent bird species across North America, (2) to investigate responses to the interaction between light exposure and night length, and (3) to identify functional traits and habitat affiliations that explain variation in species‐specific responses to these sensory stimuli with phylogenetically informed models. We found species that responded to noise exposure generally decreased in abundance, and the additional presence of light interacted synergistically with noise to exacerbate its negative effects. Moreover, the interaction revealed negative emergent responses for several species that only reacted when light and noise co‐occurred. Additionally, an interaction between light and night length revealed 47 species increased in abundance with light exposure during longer nights. In addition to modifying behavior with optimal temperature and potential foraging opportunities, birds might be attracted to light, yet suffer inadvertent physiological consequences. The trait that most strongly related to avian response to light and noise was habitat affiliation. Specifically, species that occupy closed habitat were less tolerant of both sensory stressors compared to those that occupy open habitat. Further quantifying the contexts and intrinsic traits that explain how species respond to noise and light will be fundamental to understanding the ecological consequences of a world that is ever louder and brighter.
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