Friday, May 17, 2013

Humans Living with Fierce Animals


Introduction

            Predators may not seem more important than adding diversity to planet Earth, but they provide balance within our world’s ecosystems.  Many predators are part of trophic cascades and they may be considered keystone species.  In trophic cascades, if top predators are removed, then control of grazer abundance is released and they over-graze the plants which help recycle CO2 and provide oxygen to the earth.  If a cascade occurs from removing one predator, then that animal may be a keystone species because it has a disproportionately large effect on its environment relative to its abundance (Strong 2013).  Today, these important species are in peril, remaining in only small populations and still in danger of extinction. However, to protect and preserve natural populations without direct contact can prove challenging.   Moreover, many of these large animals are forced to live in closer proximity to humans’ urban cities because we are occupying their habitat.  In this blog, I will discuss human interactions with these animals .  The lion’s share of this blog will focus on individual predator’s current abundance, human interactions if any, and today’s conservation efforts.  First I will discuss some ideas on how to understand human-carnivore encounters and the potential to avoid them through creating a global database.  Next, I will bring up an encounter in Mumbai, India and research based off the attack.  I will follow up on Cougars in Urban environments and the research that is being done on how to prevent many of their mortalities.  In addition I'll mention where research is lacking to connect cougar success to other large predators.  I will then talk about bears and current conservation efforts and lastly end with conservation efforts in action for the South American Jaguar.

Wednesday, May 8, 2013

Human Safety around Large Carnivores



(Loveman, 2011)
          When living with large carnivores, it is likely there will be negative interactions. Attacks by large carnivores on people can increase resistance to conservation efforts. However, large carnivores need these heavy conservation efforts because their numbers are still declining. They are still dwindling because they are threatened by hunting, depletion of wild prey, habitat destruction, degradation, and fragmentation (Loë and Röskaft 2004). In addition, humans that experience negative interactions or have negative attitudes towards large carnivores make it more difficult to conserve them.  For example, when a human or domestic animal is killed by a large carnivore, they demand lethal consequences for that animal.  Is there any hope to conserving large carnivores alongside humans?  There are objectives to consider to balance carnivore and human satisfaction.
            Even with legislation in place such as the Endangered Species Act, large carnivore abundance decreases.  Further management ideas, such as reintroduction of species, appears successful in some areas.  An Important foundation for reintroduction includes ensuring there is a low level of human conflict with large carnivores (Loë and Röskaft 2004).  This proves difficult in multi-use landscapes where humans and carnivores live.  The difficult tasks that conservation administrations face include: forming successful multi-use management plans, decreasing loss of livestock to large carnivores, analyzing predator-prey relationships to see how man and carnivore compete for game, stopping illegal hunting, establishing functional education programs to reduce fear and resistance to large carnivore conservation, and finally successfully appeasing human safety concerns (Loë and Röskaft 2004).
            Human safety is of course compromised when there is an injury or death due to a conflict with a large carnivore.  These instances add to historical negative attitudes towards these animals, along with lethal responses to the predator.  Large carnivores tend to be killed if they attack and fatally injure a human.  In addition, some responses result in hunting-campaigns with the outcome of killing many innocent carnivores.  Some attacks can be prevented by the behavior of the human towards an aggressive carnivore.  In order to minimize attacks and create positive attitudes toward these predators requires close observations of attack situations.  This way, human safety concerns get addressed while the large carnivore gets conservation management.




Large carnivores will always be a threat to humans and will continue to be as human populations grow and carnivores coexist in the same.   Löe and Eivin Röskaft in 2004 gathered data on carnivore attacks on humans from databases all over the world such as British Government of India, Ugandan Game Department, and others.  This data goes back a century and includes accounts from multiple families of carnivores.  However, this data only includes numbers, not the specifics involved with the fatal attack, per the High Commissioner of India in regards to tiger attacks.  For example, socioeconomic factors may influence variability in statistics such as in urban areas where people hike in bear habitat, or rural societies in Asia and Africa, where there are high rates of attacks due to daily domestic activities.    Löe (2004) found that more than 90% of the recorded large carnivore attacks on humans occurred in Asia and Africa between 1950 and 2000.
            How can there be balance between human and carnivore satisfaction.  Scientists have the data and know that big cats, mainly tigers, wolves, and bears are likely responsible for more numerous fatalities.  Next research needs to be done to understand the reasons behind the numbers, not assume the problem lies in the animal.  For example, from table 1, tigers have estimated to have killed over 12 thousand people in a century.  H. Hendrich in his paper , “The status of the tiger…” in 1975,  suggested that environmental differences may be involved in the stark variability in attacks. He hypothesized that the high rate of attacks on humans in Sunderban, Bangladesh, by the Bengal tiger (P. t. tigris) compared to most other areas was due to lack of available fresh water, a hypothesis not yet tested.  S. Herrero in his 1985 paper, Bear Attacks, analyzed brown bear (Ursus arctos) and American black bear (U. americanus) attacks in North America. He discovered they make two general modes of attack. “Defensive attacks” may occur when the bear is stressed and feels threatened, usually when suddenly encountering a person. “Offensive attacks” occur when a bear wants something such as food or space, or in abnormal instances, human prey. Herrero noted humans behaved benignly when encountering an aggressive bear, likely because they did not understand the bear’s behavior.


            Löe and Eivin Röskaft propose a solution to understanding carnivore attacks for future research, allowing the ability to create management plans for large, potentially dangerous carnivores.  Databases that record attacks should be uniform and agree on the specific information needed about attack (Löe and Röskaft 2004).  The differences in attack databases result from disagreement regarding what information is necessary.  For example, in table 2, five databases contain information on human behavior during an encounter while Nevada’s Report Form on Interactions with Mountain Lions and the Californian Wildlife Incident Report Form record narrative, descriptive information.
           The number of carnivore attacks is really unknown, and information on how to avoid attacks is even scarcer.  Two solution suggested by Loë and Röskaft include of course getting rid of the chance of encounters and also teach people to behave in a way so that an encounter does not turn into an attack.  Management plans that include protected areas and removing problem animals are helpful but people should know how to protect themselves by having knowledge of protective behavioral techniques.  This is because large problem animals such as tigers, wolves, and bears are in multi-use populated areas and these encounters are expected to increase as human population increases.  Present knowledge often is unsatisfactory to draw conclusions about the occurrence and cause of attacks (Loë and Röskaft 2004)  Loë and Röskaft suggest that formal information systems that include database(s) covering attacks and encounters should be implemented in large carnivore conservation, to be able to respond to future requests for information. Establishing a central organization to gather and disperse all information on large carnivore attacks might be an effective way of achieving this (Loë and Röskaft 2004).

Wednesday, May 1, 2013

Leopard Attack in Mumbai, India


A leopard gets ready to pounce on a forest guard in this attack in July, 2011. Six people were mauled.
(Dutta 2011)

I am interested in biodiversity. I am saddened and enraged about how early pioneers slaughtered all the large predators, for the safety of human settling and industry development. In addition I am interested in ecology and how removal of species at specific trophic levels, especially high levels, throws off the balance of an ecosystem. In my lifetime I want to study wildlife, not sure how yet, but I recently read a news article about a fatal leopard attack on a 50 year old woman.  I also read the corresponding research paper. The article was “Big cats in our Backyards: Persistence of Large Carnivores in a Human Dominated Landscape of India” by V Athreya et al. The following is a summary of the research that Athreya et al performed.                                                                           
            High profile predatory animals have long played roles in world-wide focused conservational research.  Generally they are considered flagship species (raising a species’ profile for protection) or umbrella species (species protection indirectly protects many others in a community).  Preserving these species historically has been compacted to designating wildlife protected areas (PA), where human land-use is greatly limited.  This focus has been arguably beneficial for densely populated tropical areas such as India.  There are few PAs in India with dense human populations between them.  Evidence has shown that carnivores have adapted to an array of habitats modified by humans rarely involving lethal interactions.  The goal of this study was to assess the tolerance limit of carnivores with wide ranges that interface with large human densities when residing outside of their PAs in India.  Increasingly, we are aware that animals such as wolves and mountain lions live within dense human-populations.  This paper aimed to stimulate our understanding of wild carnivore community structures in urban areas and considering the inclusion of human-dominated landscapes as PAs.
            This study was performed at Akole Tehsil of the Ahnednagar district of Western Maharashtra in India (figure 1).  Akole Tehsil houses 191 villages with a density of 177 people/km2 and the study covered 179km2.  About 80% of the population is rural with farming as the main sustenance while 15% of land is protected.  The nearest sanctuary was located 18km from the study area.  Within the study area 37 camera traps (remote controlled cameras with motion or infrared sensors) were set up approximately 1.5 km in areas inhabited commonly by leopards, usually on human trails.  The cameras were used at night due to large daytime human and cattle traffic.  Individual leopard and hyenas were identified by fur marking patterns.  To estimate their densities, the study used capture-recapture (CR) sampling and Spatially explicit capture-recapture (SECR) (Athreya 2013).  CR measures an initial population sample which is compared to a second independent sample, the second is assumed to be similar to the first.  SECR sampling is more accurate.  It uses a mathematical function taking into account that a large range animal has a decreasing probability of being detected by camera when it’s further away from the center of its range. 
(Athreya 2013)

            Over 1110 camera trap nights, 4124 exposures of 13 species where documented.  In decreasing order, humans were the most common, then domestic cats, leopards, and striped hyenas (table 1). Eighty-one photos of leopards with five individual males and 6 distinct females were obtained.  Using CR and SECR, the study revealed a leopard density of 6.4±0.78/100km2 and a hyena density of 9±3.35/100km2 over a landscape area of 187.5km(Athreya 2013).

(Athreya 2013)

            There was clear evidence from cubs and urine markings in the study are that populations of leopards and hyenas considered this their habitat.  This overturns the thought that leopards in human-dense places are strays.  This aspect of carnivores’ ability to adapt to various habitats should be considered when studying a species and its community perseverance.  Further in ecological prospect, leopards as flagship species can help their conservation.  However, when sharing space in human-modified habitats, the carrying capacity socially limited, based on human tolerance towards carnivorous predators.  The leopards preyed mostly on domestic dogs and abundant livestock, whereas in PAs wild deer was the prey.  Most other countries remove (generally lethally) predators that kill livestock.  India does not kill because of its socio-cultural acceptance of all life forms including potentially dangerous animals.  This requires humans to readily share human-use landscapes outside of PAs.  Social and ecological scientific research should consider living with carnivores as flagship species, an evolving form of conservation management (Athreya 2013).