1. Citizen science is gaining increasing prominence as a tool for science and engagement. However, despite being a potentially valuable tool for sustainable development, citizen science has little visibility in many developing countries.2. We undertook a collaborative prioritisation process with experts in conservation and the environment to assess the potential of environmental citizen science in East Africa, including its opportunities, benefits and barriers. This provided principles that are applicable across developing countries, particularly for large-scale citizen science.3. We found that there was great potential for citizen science to add to our scientific knowledge of natural resources and biodiversity trends. Many of the important benefits of citizen science were for people, as well as the environment directly.Major barriers to citizen science were mostly social and institutional, although projects should also consider access to suitable technology and language barriers. 4. Policy implications. Citizen science can provide data to support decision-making and reporting against international targets. Participation can also provide societal benefits, informing and empowering people, thus supporting the United Nations'This is an open access article under the terms of the Creative Commons Attribution License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.
Human –wildlife conflicts (HWC) affect the social-economic aspects of millions of people across the world and is one of the most important challenges facing wildlife conservation. Long-term data collection provides an opportunity to critically understand HWC trends and enable wildlife stakeholders to create evidence-based solutions for co-existence of people and wildlife. We used Kenya Wildlife Service (KWS) data for the 2010-2018 period to analyse trends in typology, seasonality and economic costs of HWC in Kajiado and Laikipia Counties in Kenya. A total of 953 HWC reported cases in the two counties were analysed. Wildlife threats to human life, crop damage and livestock predation were the common form of HWC, contributing 65.7% (n=626), 21.7% (n=207), and 7.7% (n=73) respectively. Apart from livestock predation (t=2.431; P=0.028) all other types of HWC did not show any significant differences in the two counties over the nine-year period. Elephants were responsible for the highest conflict cases (79%, n=753) followed by baboons (6.9%, n=66). Elephants contributed to the highest human fatality and injuries (43%, n=10); while snakes and buffalo were second, each contributing to 17% (n=4) of the total cases. Majority of the HWC occurred in the dry season months of July (n=114), January (n=99) and October (n=96). The overall trend indicated increasing HWC cases over the 9 years in both counties. The analysis of economic cost of HWC showed that a total of 64.09 hectares of crops were damaged in 2010-2018, with 70% of the cases reported in Kajiado County. In terms of predation, Kajiado lost livestock worth KES 1,785, 000 (U$ 16,780.53) while Laikipia lost KES 407,000 (U$ 3826.15). This study provides empirical evidence that can be used to develop strategies for mitigating HWC based on types, seasons and conflict species.
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