Showing posts with label Jozani-Chwaka Bay National Park. Show all posts
Showing posts with label Jozani-Chwaka Bay National Park. Show all posts

Saturday, 20 February 2021

JOZANI-CHWAKA BAY NATIONAL PARK AND COVID-19

by Jonathan Walz

Evidence of beach erosion due to climate change at Paje (photo: J. Walz)























In Zanzibar, 2020 was a unique and impactful year. Covid-19 raised challenges for the state and its communities and environments. Compounded climate change and the national elections in October added stresses. The spring high tide event in mid-October (4.68m tidal change amplified by sea level rise) demonstrated that incremental increases to sea level during the last two decades have real world effects, including breached beach crests, saline wells, and inundated agricultural fields. Dramatically reduced tourism on Unguja and tourist revenue, alongside the aforementioned stresses, influenced biodiversity and the management of protected areas.

National parks around the world face multiple challenges during the global pandemic. For instance, significantly reduced staffing due to a decline in income from tourism influences parks’ capacities and plans to effectively enforce protections, facilitate scientific research, and ensure upkeep. In addition, and as a core threat to global biodiversity, administrators and observers of protected areas cite a parallel uptick in illicit activities that continue to degrade environments, species, and the human-environment interface: land grabs, deforestation for firewood and charcoal-making, animal poaching, an intensification of the illicit trade in wildlife and wildlife products, and the illegal mining of rare minerals and construction materials.

Burned bee honeycomb at Jozani (photo: J. Walz
“Biodiversity” is high species richness and evenness, which is equated with ecosystem health, productivity, stability, and resistance to disturbances, including disease. In general, biodiversity hotspots in Zanzibar – terrestrial and marine – are understudied (scholarly investigations in the archipelago being skewed to social and historical topics). Thus, biodiversity in the archipelago faces threats even before its is thoroughly understood. The sickness, death, and social disruption of the pandemic continue to act on the economically impoverished society and on the uncertainties spurred by climate change. Impacts from climate change are apparent: temperature increase (1.2 degrees Celsius since 1997), reduced rainfall with uncertain distribution, consistent sea level rise (0.28 cm/per year since 2009), and coastline and reef degradation. During the pandemic, pressures on the urban economy and food security in Zanzibar City have increased human and environmental vulnerability and changed behavior.

Up to January 2021, although human mortality and Covid-19 infections seemingly have been lower across eastern Africa than in areas of the Americas, Europe, and South Asia, nevertheless there have been negative outcomes in the region, for instance increased food insecurity and growing strains on health systems and natural resources. However, generalized statements about the pandemic’s impacts to nature conservation in Africa and the Global South more broadly deserve scrutiny and critique. What negative impacts to protected areas are being underemphasized in reports and what conservation positives have arisen during the pandemic?

Red colobus monkeys at Jozani (photo: J. Walz)
The Zanzibar archipelago, a semi-autonomous region of Tanzania, has a single national park which serves as a useful case for analysis: Jozani-Chwaka Bay National Park and Biosphere Reserve. Jozani (for short) is an accessible park which in the last two years (2018 and 2019) has received more than 60,000 visitors per year. In April 2020 (during the first global peak in Covid-19), there were 14 total visitors to the park: less than 0.5% the number of visitors in April 2019. Diminished tourism revenue resulted in a temporary 50% reduction in park staff which influenced monitoring and enforcement, park upkeep, and public engagement. Urban job loss and modest food insecurity on Unguja redistributed some residents from nearby Zanzibar City to the countryside near the national park. Schools were closed which left children at home throughout the day to help gather natural resources for these larger households at the park’s edges. In addition, poachers used the ocean – not just land – to access remote areas, a practice previously documented primarily on Unguja’s sister island to the north: Pemba. Ad hoc observations and interviews with rangers documented that illicit activity increased, the evidence of which included tree stumps, cuttings from medicinal plants, shotgun shells, burned bee honeycombs, and traces of sand mining along the bay front.

However, positives for conservation and biodiversity have been lost in caricatures of the impacts of Covid-19. Absent tourists, monkey troops (especially Red colobus monkeys) at the national park reverted to less habituated behaviour. Farmers at the edges of the protected area reported fewer cases of damage to crops from park wildlife. Domesticated and feral animals were more visible, making them easier to humanely capture and relocate outside of park boundaries. In Chwaka Bay, intertidal species like octopus, a popular food served at tourist hotels, rebounded. On June 29, schools reopened; school groups became the primary park visitors and the focus of environmental education programs rather than secondary to the attention of overseas tourists. With few foreign-led NGOs in operation during the pandemic, a few of Zanzibar’s citizens stepped-in as agents of conservation at the park but also in Zanzibar City. They tended to public green spaces, outdoor areas less prone to transmit Covid-19.

Octopus and fisherman at Chwaka Bay (photo: J. Walz)
Biodiversity loss and socio-ecological instability increase vulnerability to on-going and future disasters. To overcome the disabling effects of Covid-19 and the compounding threats of climate change and other influential factors better promotion of evidence-based interdisciplinary study of coupled natural and human systems should be a priority. The multiple invested stakeholders should enforce protections to areas and species through standing or new policies, enhance resources for in-country experts to conduct and communicate research, bolster the health and wealth-being of people and environments through community “green” strategies, and collaborate with mindfulness to improve human livelihoods. The protection and restoration of biodiversity will improve adaptability to threats.

The public should be wary of simple narratives about Covid-19 and its impacts in Zanzibar and elsewhere. Covid-19 has not put threats to biodiversity “on hold”. However, at the same time, Covid-19’s outcomes have not been wholly negative.  As noted, during the pause in tourism, citizens of Zanzibar have initiated and developed conservation practices outside the orbit of ex-patriots, many of whom returned to their home countries due to the pandemic. At national parks in Africa and Indian Ocean island states, Covid-19 produces mixed conservation outcomes. Evidence builds more balanced and meaningful narratives that recognize the vulnerability and adaptability of people, ecosystems, and parks in an era of change.

Sunday, 5 February 2012

A SYKES' MONKEY EATING A SNAKE SKIN

by Helle Goldman

In January 2003, while we were in Zanzibar to camera-trap carnivores in Jozani-Chwaka Bay National Park, my husband Jon Winther-Hansen observed a Zanzibar Sykes’ monkey (Cercopithecus mitis albogularis, a.k.a. Blue monkey or White-throated guenon) eating a sloughed-off snake skin. Partly hidden by the lush foliage of the Indian almond tree (Terminalia catappa) in which it was sitting, the monkey completely consumed its prize in about five minutes. This took place near the Jozani Visitor Centre.

Inhabiting forested parts of east, central and southern Africa, Sykes’ monkeys are food generalists, eating leaves, fruits, seeds, flowers and invertebrates and occasionally preying on vertebrates (Rudran 1978; Butyinski 1982); conspecific infants have also been observed being killed and eaten (Fairgreave 1995). The Zanzibar Sykes' monkey is the subspecies found on Unguja island and on the mainland opposite the Zanzibar archipelago.

We don't know what kind of skin the monkey's meal once belonged to. More than 20 species of snake have been recorded on Unguja (Pakenham 1983: 5; Spawls et al. 2002: passim), but stills from our video clip, some of which are reproduced here, do not permit certain identification of the translucent skin.

While the literature contains a few reports of nonhuman primates dispatching and even consuming snakes (see references in Headland & Greene 2011), we are not aware of reports of Sykes’ monkeys or other primates eating the sloughs snakes leave behind when they shed. We would welcome further information on this point.

References

Butynski, T. M. 1982. Blue monkey (Cercopithecus mitis stuhlmanni) predation on galagos. Primates 23, 563-566.

Fairgrieve, C. 1995. Infanticide and infant eating in the Blue monkey (Cercopithecus mitis stuhlmanni) in the Budongo Forest Reserve, Uganda. Folia Primatologica 64, 69-72.

Headland, T. N. & H. W. Greene 2011. Hunter-gatherers and other primates as prey, predators, and competitors of snakes. Proceedings of the National Academy of Sciences 108, E1470-E1474.

Pakenham, R. H. W. 1983. The reptiles and amphibians of Zanzibar and Pemba islands (with a note on the freshwater fishes). Journal of the East Africa Natural History Society and National Museum 177: 1-40.

Rudran, R. 1978. Socioecology of the Blue monkeys (Cercopithecus mitis stuhlmanni) of the Kibale Forest, Uganda. Smithsonian Contributions to Zoology 249.

Spawls S., K. Howell, R. Drewes & J. Ashe 2002. A Field Guide to the Reptiles of East Africa: Kenya, Tanzania, Uganda, Rwanda and Burundi. London & San Diego: Academic Press.