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The Influence of Noise Pollu1on on Bird Diversity Teyla Simon, Veronica Wright, Tasnima Elahi Project TRUE, Wildlife Conserva>on Society Methods
Introduc1on
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and terrestrial species (1). They are important habitats in urban landscapes that provide nesting opportunities for wetland breeding birds, while also providing food resources for both native and invasive birds (2). One method of assessing wetland quality is by studying the changes in bird communities, given that birds are a powerful indicator species. (2) The literature indicates that anthropogenic noise may have damaging effects on the individual fitness of birds by acting as a physiological stressor (3). Avian populations that persist in noisy habitats, experience masking important vocalizations necessary for mating, which leads to negative behavioral changes and a decrease in fitness (3). Anthropogenic noise can serve as a powerful sensory pollutant that has the ability to nonrandomly distribute bird communities by interfering with different bird species’ ability to receive, respond and dispatch acoustic cues and signals necessary for mating and prey/predator detection (4).
1. Ten min fixed point counts conducted at four randomly chosen points at wetland loca>ons.
• Average noise level, or overall noise pollution, in a wetland site seems to
3. Par>cipants used the Decibel 10th app during their 10-‐ min fixed point counts to record noise levels.
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Image 6. Logo of the Decibel 10th app used to measure noise levels
Further Analysis
• After further analyzing the bird data and noise pollution data collected we observed that he noise pollution in an area is more strongly correlated with the abundance of native and invasive bird species, rather than the richness of native and invasive bird species present.
Image 4. Teyla and Veronica looking at a Black-Crowned Night Heron during their bird count at Inwood Hill Park. 350
• The purpose of this study was to observe if there is a correlation
2. All birds heard or seen within a 50-‐m radius were recorded using a dependent-‐observer approach. In this approach, survey teams consisted of two par>cipants in which one par>cipant acted as the primary observer no>ng bird species and abundance, and the other par>cipant acted as the secondary observer recording data and no>ng any birds missed by the primary observer.
between noise pollution and the bird species richness in wetland sites.
• We hypothesized that if there are lower levels of noise pollution in
Image 1. Frequency reading from site 2 in The Rambles.
Image 3. Additional frequency reading from Site 2 in The Rambles.
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Abundance of native birds
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Abundance of invasive birds R² = 0.76396
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Figure 4. This graph demonstrates that as the average noise pollution increases in wetland sites the abundance of both native and invasive birds decreases.
R² = 0.50732
Influence of Average Noise Levels on Bird Richness
Influence of Maximum Noise Levels on Bird Richness
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R² = 0.9258
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Average Noise Level
Figure 1. Trend in which the average noise levels increase as the average bird richness decreases.
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Average Bird Richness
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R² = 0.07125
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Figure 5 This graph demonstrates that as the average noise pollution increases in wetland sites the average richness in invasive bird species decreases.
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Influence of Noise Pollution on the Number of Native and Invasive Bird Species
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R² = 0.14848
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Number of Natives
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Number of Invasives
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R² = 0.81939
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Figure 2. This graph demonstrates that the maximum noise levels in wetland sites do not relate to the bird.
Independent Teen Studies Question: Are birds going to be more noise-tolerant at our sites in Manhattan versus Queens? Hypothesis: Birds will be more tolerant of noise pollution in Manhattan than Queens. Method: We conducted fixed-point counts while measuring noise pollution using a mobile app called Decibel 10th. Results/ Conclusions: There is no trend to support the hypothesis that the difference in noise pollution effects bird richness in Queens versus Manhattan.
Bird Richness vs. Average Noise Pollution 10 8 6 4 2 0 40
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Average Noise Pollution
Figure 9. The average bird diversity index between Manhattan and Queens demonstrates a higher bird species diversity in Queens.
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Figure 3. Demonstrates no clear trend that noise pollution effects bird richness in Queens vs. Manhattan
Future Research ● Determine if there is a trend between bird species diversity and frequency noise levels. ● Determine if other human activities, such as transportation, might influence bird species diversity and abundance. ● Determine how the environmental surroundings, such as the type of plants at wetlands, might influence bird species diversity and abundance.
References
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Bird Richness
Image 2. Frequency noise level detection app, SpectrumView
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Results Average Bird Richness
Question Are invasive or native bird species more prevalent in areas of high tones/frequencies? Hypothesis More invasive birds will be observed in areas where high frequencies are recorded. Method Point counts while measuring frequency using a mobile app called SpectrumView. Results/Conclusions The trend observed, through all sites, is that bird diversity, as measured by Simpson’s Diversity Index, decreases when frequencies in the surrounding environment increase. The inverse was also observed.
Influence of Noise Pollution on the Abundance of Native and Invasive Bird Species
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wetlands, then we will observe a higher bird species richness.
Independent Teen Studies
Average Abundance of Birds
Image 5. Noise recording
Research Goal
negatively influence the bird richness. Supports our hypothesis that at lower levels of noise pollution we will observe higher bird diversity. Bird richness in wetland sites is not influenced by the maximum level of noise. Our data indicates that it is more important to look at the overall noise pollution in wetland sites rather than the maximum noise levels when trying to determine the influence on bird richness.
Avergae Number of Birds
• Wetlands are one of the most biodiverse systems, supporting both aquatic
Conclusions
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(1) Faccioli, Michela, Antoni Riera Font, and Catalina M. Torres Figuerola. "Valuing the recreational benefits of wetland adaptation to climate change: a trade-off between species’ abundance and diversity." Environmental management 55.3 (2015): 550-563. Retrieved from http://link.springer.com/article/10.1007/s00267-014-0407-7 (2) McKinney, Richard A., Raposa, Kenneth B., Cournoyer, Rose M. “Wetlands as habitat in urbanizing landscapes: Patterns of bird abundance and occupany.” Landscape and Urban Planning 100 (2011): 144-152. (3) Mora, Jordan W., John N. Mager III, and Douglas J. Spieles. "Habitat and landscape suitability as indicators of bird abundance in created and restored wetlands." ISRN Ecology 2011 (2011). Retrieved from: file:///Users/g-lll308/Downloads/297684.pdf (4) Caitlin R. Kight, Margaret S. Saha, and John P. Swaddle 2012. Anthropogenic noise is associated with reductions in the productivity of breeding Eastern Bluebirds (Sialia sialis) Ecological Applications 22:1989–1996. Retrieved from: http://www.esajournals.org/doi/full/10.1890/12-0133.1 (5) Francis, C. D. (2015), Vocal traits and diet explain avian sensitivities to anthropogenic noise. Global Change Biology, 21: 1809–1820. doi: 10.1111/gcb.12862. Retrieved from: http://onlinelibrary.wiley.com/doi/10.1111/gcb.12862/full