Pigeons and People: Resource Ecology and Human Dimensions of Urban Wildlife

<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>

Pigeons and People: Resource Ecology and Human Dimensions of Urban Wildlife

<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>

Seroprevalence of Newcastle Disease Virus in Slaughtered Pigeons from Selected Markets in Zaria, Kaduna State Nigeria

Newcastle disease (ND) outbreak even in the face of vaccination is a common problem in Nigeria. Three Newcastle disease (ND) panzootic were recorded in the past and one of such was caused by feral pigeon fecal contamination of poultry feed materials. The study was designed to investigate the presence of ND antibodies in pigeons slaughtered in three markets in Zaria Nigeria. A total of 1500 Pigeons sera samples were tested across the selected markets, namely: Sabon-gari, Samaru and Tudun-wada markets. Five hundred blood samples were collected from each market. An overall seroprevalence of 22.33% (335/1500) was recorded in this study. Hemagglutination inhibition test revealed that pigeons from Sabon-gari market had the highest seroprevalence of 29% (145/500). Female pigeons had higher seroprevalence of 27.66% (130/470) compared to male pigeons 19.90% (205/1030). Younger pigeons of < 10 weeks old are more prone to ND infection with a seroprevalence of 34.21% (52/152) compared to pigeons > 10 weeks old 20.99% (238/1348). Also, only in Samaru market was there a significant association between ages (P = 0.00) and sexes (P = 0.00) of pigeons and seroprevalence of ND. Therefore, free routine ND vaccination campaign should be launched in the study areas with more emphases targeting the market species in order to mitigate the epidemic cycle of the virus. Moreover, market poultry farmers should be enlightened on the economic significance of the disease and the need to maintain strict biosecurity measures on their market farms.

Being Dark is Better: A Feral Pigeon Plumage Polymorphism as a Response to Urban Environments in Slovakia

The purpose of this study was to determine the distribution and plumage phenotypes of the feral pigeon, Columba livia forma urbana (Gmelin, 1789), in Slovakia. Censuses carried out in the built-up areas of 16 towns and cities from November to February (2012–2018) counted and evaluated 3,123 individual birds. The most frequent were melanic colored birds (checker, T-pattern and spread phenotypes), which predominated in the population (51.6%, n = 1,613), followed by paler ones (42.1%, n = 1,316) and other types (6.2%, n = 194). A statistically significant difference was confirmed among the melanic and paler plumage phenotypes (χ2 = 81.49, df = 15, p < 0.0001). Correlation confirmed the different importance of city area and human density on the maintenance of dark and/or pale pigeons living in cities.

Feeding ecology of blue rock pigeon (Columba livia) in the three districts of Punjab, Pakistan

Present paper provides information on the feeding regimens of the two genders of the blue-rock pigeon (Columba livia Linn.) in the sampled habitats of the three districts viz. Rawalpindi, Faisalabad and Bahawalpur of the Punjab province, Pakistan. This feral pigeon, considered ubiquitous species, inhabits both the grasslands and clumped environments to establish their roosts and nests. The study explored about comparable feeding proportions from three major habitats of the pigeons which were captured with medium sized mist-nets. For Rawalpindi in the winter season, the Zea mays was one of the predominant food item (30.6%) for males, and other ranked major food contents were (26.7%, 22.4% and 20.2%), and fairly similar feeding proportions were also recorded for the females (50.4%, 33.3%, 36.4% and 23.9%) for Carthamus oxyacantha, Hordeum vulgare, Triticum aestivum and Zea mays respectively. Evidently, no significant deviations in the existing food crops for the three sites for the feral pigeon were detected, which strongly suggested that the, modes of feeding habits among the sustainable roosts and nests which were closely located to food crops, exerted negligible impacts during intermittent pigeon foraging movements in the diurnal conditions.

The synanthropic status of wild rock doves (Columba livia) and their contribution to feral pigeon populations

Wild rock doves still breed in suitable habitats along southern and insular Italy, even if their colonies are threatened by the genetic intrusion of feral pigeons. One of their prominent behaviours is the daily foraging flights from colonial to feeding grounds which involves coming into contact with man-made buildings. These are exploited firstly as roosting places near crop resources and later for nesting. This incipient synanthropy is not extended to direct food dependence on humans, by which they tend to remain independent. In the same way that ferals genetically intruded the wild colonies, in urban habitats, rock doves mix with ferals because of the large interbreeding possibilities. In the natural range of the wild species, this has occurred since the appearance of the feral form of pigeons and still continues with the residual populations of rock doves, representing their endless contribution to the feral populations, at least until the dissolution of the gene pool of the primordial form of wild rock dove.