Attempts to deter elephants from entering crop fields and human settlements in Africa have used various barriers (e.g. electric fences, chilli fences, beehive fences or plant barriers), situated on or very near the boundaries of fields or villages, with rather variable success. We explored a very simple new barrier concept based upon re-arranging the layout of foreign stimuli already known to arouse suspicion and fear among elephants. Deterrence involved deploying unnaturally scented objects on and across their pathways of habitual movement leading to crop field clusters. Elephants are suspicious of unpleasant olfactory stimuli, like string or cloth saturated with pungent-smelling chilli oil, old engine oil, or creosote and dislike ‘chilli smoke’. Foreign visual items like plastic bottles, reflective metal strips and cow bells possibly reinforced suspicion of these unpleasant scents and influenced the deterrent effect. These flimsy items deployed over very short distances merely acted as a bluff to ‘problem elephants’ that people were actively trying to impede their progress, and the vast majority chose to turn back or deviate substantially. Thus we coined the term a ‘soft virtual boundary’. We demonstrate that placing virtual boundaries away from village and agricultural lands, forces elephants to encounter them upon leaving their daytime refuges, while still in natural habitat. The suspicion and fear generated here considerably reduces elephants’ determination to proceed onwards to risk crop raiding. When multiple, small virtual boundaries are strategically moved around at intervals, a ‘virtual fence dynamic’ delivers an enduring deterrent effect. In ten study areas in two countries over seven years this technique led to considerable and consistent reductions in crop damage levels of up to 95% in places. Because these methods (i) completely rely on local knowledge, (ii) were exceptionally low cost and (iii) demonstrated rapid results, the ‘buy-in’ from affected communities of small-scale subsistence farmers was immediate and very enthusiastic. So this strategy has the potential to remove the most intractable stumbling block to the sustainability of human-elephant conflict mitigation efforts in smallholder agriculture – reliance upon conservation donor funding for very costly and problematic mitigation measures like fencing, compensation schemes and elephant translocations.
Large predators are thought of as ecological keystone species, posterchildren of conservation campaigns, and sought-after targets of tourists and photographers. At the same time, predators kill livestock and huntable animals, and occasionally people, triggering fears and antipathy among those living alongside them. Until the 1960’s government-sponsored eradication and persecution campaigns in the United States prioritized interests of livestock producers and recreational hunters, leading to eradication of wolves and bears over much of their range. Without large predators, subsidized by changes in agricultural practices and milder winters, ungulate populations erupted, triggering negative ecological impacts, economic damage, and human health crises (such as tick-borne diseases). Shifting societal preferences have ushered in more predator-friendly, but controversial wildlife policies, from passively allowing range expansion to purposeful reintroductions (such as release of wolves in Yellowstone National Park). Attempts to restore wolves or mountain lions in the U.S. and protecting coyotes appear to enjoy strong public support, but many state wildlife agencies charged with managing wildlife, and recreational hunters continue to oppose such efforts, because they perceive predators as competitors for huntable animals. There may be compelling reasons for restoring predators or allowing them to recolonize their former ranges. But if range expansion or intentional releases of large predators do not result in ecosystem recovery, reduced deer populations, or Lyme disease reductions, conservationists who have put their reputation on the line and assured decision makers and the public of the important functional role of large predators may lose public standing and trust. Exaggerated predictions by ranchers and recreational hunters of greatly reduced ungulate populations and rampant livestock killing by large carnivores may lead to poaching and illegal killing threatening recovery of predator populations. How the return of large carnivores may affect vegetation and successional change, ungulate population size, other biota, livestock and human attitudes in different landscapes has not been appropriately assessed. Societal support and acceptance of living alongside predators as they expand their range and increase in abundance requires development and monitoring of social, ecological and economic indicators to assess how return of large predators affects human and animal and plant livelihoods.
What would successful deer management look like in Scotland? To some, flourishing populations of native wild deer represent success. But to others, negative impacts such as damage to woodlands and peatlands, agricultural and forestry losses, deer-vehicle collisions, and facilitating Lyme disease spread represent failure. Conflicting interests and incentives among people involved in deer management mean a common definition of success, and therefore clear management targets, remain elusive. While some environmental groups urgently call for an increase in the number of deer culled (shot) each year, other stakeholders aim to maximize deer numbers. Overcoming this governance failure will require clearly articulated, scientifically valid, and socially acceptable socio-ecological objectives to be co-produced by a broad range of stakeholders. Systematic monitoring of deer impacts will also be needed to evaluate the ability of specific management interventions to achieve defined objectives. Reintroducing Eurasian lynx (Lynx lynx) has been suggested as a means to reduce deer numbers and their negative ecological and socioeconomic impacts. However, evidence of lynx impacts on deer numbers, deer impacts, and social conflicts over deer suggest lynx reintroduction alone would not effectively reduce negative impacts of deer in Scotland, though it could be part of a broader solution. In the short-term, achieving sustainable numbers of deer in Scotland will require a substantial increase in the number of deer culled and effective changes to the way deer management is incentivized, regulated, implemented, and monitored.
The illegal wildlife trade (IWT) is a global issue that threatens the conservation of many species of fauna and flora and affects the livelihoods of people who are dependent upon wildlife. By far the most common approach to tackling IWT is to enhance law enforcement, including arming rangers and tougher penalties for perpetrators. Yet, critics of this approach argue that efforts to reduce IWT in source countries are likely to fail without the involvement of local people. However, little is known about the effectiveness of community-based approaches to tackling IWT or how this is being measured. We used information from the www.peoplenotpoaching.org learning platform to analyze over 100 case studies of community-based anti-IWT interventions to understand what proportion have been effective and how this has been measured. We present a typology of frequently reported outcomes, their indicators and means of verification. We show that effectiveness in community-based anti-IWT interventions is measured by a number of indicators and using a variety of verification means. Our findings suggest that conservation practitioners more frequently implement activities to measure conservation outcomes in comparison to livelihood outcomes, which has implications for how we consider if a community-based anti-IWT project has been effective. We recommend that future community-based anti-IWT projects build in more robust monitoring, evaluation and learning activities to measure how livelihood benefits impact local communities given their support is crucial to achieving long-term conservation success.
Public wildlife management in the United States is transforming as agencies seek relevancy to broader constituencies. State agencies in the United States, while tasked with conserving wildlife for all beneficiaries of the wildlife trust, have tended to manage for a limited range of benefits in part due to a narrow funding model heavily dependent on hunting, fishing, and trapping license buyers. To best meet the needs, interests, and concerns of a broader suite of beneficiaries, agencies will need to reconsider how priorities for management are set. This presents an opportunity for conservation program design and evaluation to be elevated in importance. We argue that success in wildlife conservation in the U.S. requires assessment of both decision-making processes and management results in relation to four questions: conservation of what, under what authority, for what purposes, and for whom?