scholarly journals Ecology of Feral Pigeons: Population Monitoring, Resource Selection, and Management Practices

Author(s):  
Erin E. Stukenholtz ◽  
Tirhas A. Hailu ◽  
Sean Childers ◽  
Charles Leatherwood ◽  
Lonnie Evans ◽  
...  
2008 ◽  
Vol 51 (3) ◽  
pp. 623-633 ◽  
Author(s):  
Carolina Somaio Neves ◽  
Rosana Moreira da Rocha

The aim of this work was to identify the introduced and cryptogenic species in encrusting and associated communities of hard substrates in Paranaguá Bay, Brazil, and to attempt to determine which of these species could negatively affect the local community to suggest management strategies for these species. At least four introduced species were found - a large number in comparison with other port surveys. These were the hydrozoan Garveia franciscana Torrey, 1902, the polychaete Polydora cornuta Bosc, 1902, the barnacles Amphibalanus reticulatus (Utinoni, 1967) and Striatobalanus amaryllis Darwin, 1854, all with potentially harmful impacts. Of the 33 cryptogenic species, four were also listed in the literature as causing negative effects. We propose the following management practices: periodic cleaning of all underwater structures, population monitoring of invasive species and potential substrates, an information database of potential sources of introduction.


2021 ◽  
Author(s):  
◽  
Symone Krimowa

<p>Urban areas and human populations are growing. Cities provide highly modified habitat for species that can adapt their feeding and other behaviours. The growth of urban landscapes and human populations may result in an increase in human-wildlife conflict. Businesses which prepare and sell food (food establishments) may be more likely to encounter conflict with urban wildlife, which may lead to negative attitudes towards urban wildlife. Negative attitudes towards wildlife could create polarised communities and possibly affect the success of environmental initiatives. This study sought to understand (1) how feral pigeons use urban environments and the resources key to their distribution and congregation; (2) whether feral pigeons are food limited in Wellington City; and (3) how the interactions of owners and managers of food establishments with feral pigeons influence their attitudes to feral pigeons. I used 8 transects through the central City which covered a representative sample of urban habitats, including the central business district, green space, and waterfront to estimate resource selection. Bird capture and banding were used to determine feral pigeon condition at a range of sites across the City and included a mix of high, medium and low anthropogenic fed sites. A written survey of owners and managers of food establishments in Wellington was conducted to evaluate attitudes to feral pigeons (n = 62). Feral pigeon resource selection is mainly influenced by people and where they choose to eat (∆AIC ≤ W = 0.999), such as sites with outdoor seating where people may directly feed feral pigeons. However, once a site has been selected, areas with tertiary vegetation and disposed food (W = 0.324 and W = 0.297) are the most likely to attract larger flocks of feral pigeons (although a number of other variables also influence flock size, such as availability of freshwater). Feral pigeons do not appear to be food limited in Wellington as condition was not significantly different between sites (n=48, body condition, (body mass/tarsus length) Kruskal-Wallis = 2.06, p = 0.36; keel condition, Kruskal-Wallis = 0.7283, p = 0.6948; feather condition Kruskal-Wallis = 2.7943, p = 0.2473). Attitudes of food establishment owners and managers towards feral pigeons are most influenced by how often they see feral pigeons (∆AICc ≤ W = 0:465). Therefore, direct experience rather than knowledge, engagement, action or socio-demographics has the most influence on attitudes of owners and managers of food establishments. These results suggest that feral pigeon populations are largely dependent on the availability of anthropogenic foods. Reducing the food provided by people may limit feral pigeon populations. Reductions in pigeon populations are also likely to change attitudes of business owners and reduce conflict because they will be less likely to encounter pigeons. Limiting feeding and access to food waste is probably the most effective way of managing pigeon populations.</p>


2017 ◽  
Vol 8 (1) ◽  
pp. 181-192 ◽  
Author(s):  
Kevin L. Fouts ◽  
Clinton T. Moore ◽  
Kristine D. Johnson ◽  
John C Maerz

Abstract Restoring the natural or historical state of ecosystems is a common objective among resource managers, but determining whether desired system responses to management actions are occurring is often protracted and challenging. For wildlife, the integration of mechanistic habitat modeling with population monitoring may provide expedited measures of management effectiveness and improve understanding of how management actions succeed or fail to recover populations. Southern Appalachia is a region of high biodiversity that has undergone dramatic change as a result of human activities such as historic logging, exotic invasions, and alteration of disturbance regimes—including reduction in application of fire. Contemporary efforts to restore fire-maintained ecosystems within southern Appalachian forests require tools to assess the effects of fire management practices on individual animal fitness and relate them to corresponding influences on species abundance. Using automated sensing equipment, we investigated the effects of burned forests on reptile habitat suitability within the western portion of Great Smoky Mountains National Park, Tennessee. Specifically, we used microclimate measurements to model northern fence lizard Sceloporus undulatus hyacinthinus diurnal activity budgets in unburned and variable burn age (3–27-y) forest stands. We estimated northern fence lizard occurrence and abundance along transects through burned and unburned forests. Burned forest stands had microclimates that resulted in longer modeled daily activity periods under most conditions during summer. S. undulatus abundance was 4.75 times greater on burned stands compared to paired unburned stands, although the relationship between burn age and abundance was not well determined. Results suggest the more open habitat structure of burned areas within these xeric pine–oak forests may benefit S. undulatus.


2021 ◽  
Author(s):  
◽  
Symone Krimowa

<p>Urban areas and human populations are growing. Cities provide highly modified habitat for species that can adapt their feeding and other behaviours. The growth of urban landscapes and human populations may result in an increase in human-wildlife conflict. Businesses which prepare and sell food (food establishments) may be more likely to encounter conflict with urban wildlife, which may lead to negative attitudes towards urban wildlife. Negative attitudes towards wildlife could create polarised communities and possibly affect the success of environmental initiatives. This study sought to understand (1) how feral pigeons use urban environments and the resources key to their distribution and congregation; (2) whether feral pigeons are food limited in Wellington City; and (3) how the interactions of owners and managers of food establishments with feral pigeons influence their attitudes to feral pigeons. I used 8 transects through the central City which covered a representative sample of urban habitats, including the central business district, green space, and waterfront to estimate resource selection. Bird capture and banding were used to determine feral pigeon condition at a range of sites across the City and included a mix of high, medium and low anthropogenic fed sites. A written survey of owners and managers of food establishments in Wellington was conducted to evaluate attitudes to feral pigeons (n = 62). Feral pigeon resource selection is mainly influenced by people and where they choose to eat (∆AIC ≤ W = 0.999), such as sites with outdoor seating where people may directly feed feral pigeons. However, once a site has been selected, areas with tertiary vegetation and disposed food (W = 0.324 and W = 0.297) are the most likely to attract larger flocks of feral pigeons (although a number of other variables also influence flock size, such as availability of freshwater). Feral pigeons do not appear to be food limited in Wellington as condition was not significantly different between sites (n=48, body condition, (body mass/tarsus length) Kruskal-Wallis = 2.06, p = 0.36; keel condition, Kruskal-Wallis = 0.7283, p = 0.6948; feather condition Kruskal-Wallis = 2.7943, p = 0.2473). Attitudes of food establishment owners and managers towards feral pigeons are most influenced by how often they see feral pigeons (∆AICc ≤ W = 0:465). Therefore, direct experience rather than knowledge, engagement, action or socio-demographics has the most influence on attitudes of owners and managers of food establishments. These results suggest that feral pigeon populations are largely dependent on the availability of anthropogenic foods. Reducing the food provided by people may limit feral pigeon populations. Reductions in pigeon populations are also likely to change attitudes of business owners and reduce conflict because they will be less likely to encounter pigeons. Limiting feeding and access to food waste is probably the most effective way of managing pigeon populations.</p>


2009 ◽  
Vol 85 (2) ◽  
pp. 202-217 ◽  
Author(s):  
Charles M Francis ◽  
Peter J Blancher ◽  
R. Dean Phoenix

Bird population monitoring should be designed to enhance conservation of birds through informing policy decisions and management actions. Many different bird surveys are undertaken in Ontario ranging from province-wide multi-species programs such as the Ontario Breeding Bird Atlas to single-species localized surveys for Species at Risk. Although most surveys provide some useful contributions towards understanding the status of bird populations, there remain significant gaps in both species and geographic coverages, especially in the northern half of the province, and few surveys are sufficient for evaluating the specific effects of current management practices on birds. Enhancing bird monitoring in the province should first involve clearly defining, quantitatively, the information required for management, conservation and decision-making, in the context of an adaptive management cycle, and then identifying the most cost-effective monitoring programs to obtain that information. This can most effectively be implemented through a cooperative effort involving all parties with an interest in bird monitoring data including federal and provincial government agencies, environmental non-government organizations, and industry. Key words: bird population monitoring, evaluation, adaptive management, decision-making


2010 ◽  
Author(s):  
Ming-Te Wang ◽  
Thomas J. Dishion ◽  
Elizabeth A. Stormshak ◽  
John Willett

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