Monday, 11 May 2015

Monkey Fever Disease in South India: Some recommendations for its management.

Macaca radiata



The Western Ghats is a mountain range that runs parallel to the western coast of the India starting near the border of the states of Gujarat and Maharashtra and running through Maharashtra, Goa, Karnataka, Kerala, and Tamil Nadu states ending at Kanya Kumari, the southern tip of India. The forests in the Western Ghats are unique in that they are some of the best representatives of non-equatorial tropical evergreen forests. With  an estimated 7,400 species of flowering plants, 139 mammal species, 508 bird species, 179 amphibian species and 288 freshwater fish species Western Ghats  is  one of the eight "hottest hotspots" of biological diversity in the world. Researchers suspect that even more unidentified species may exist in these forests. An estimated 325 globally threatened flora, fauna, bird, amphibian, reptile and fish species make their home in the forests of Western Ghats. I first saw the majestic Western Ghats as a nine year old when I accompanied my father Professor Joshua Stephen during his research visits to the forests. In the early nineties along with my father from whom we imbibed the enthusiasm for forest conservation, my siblings and I including my sister Sarah,  a contributor on Ecoratorio, conducted voluntary research on the biodiversity in the Western Ghats. Needless to say, the conservation of flora and the fauna of the Western Ghats is of much interest to me.

Western Ghats near Ponmudi Hills


Wayand , a district in the north-east of Kerala state, is bordered by the Western Ghats on the East and is part of the Nilgiri Biosphere reserve. An estimated 885.92 sq km of Wayanad is under forest cover, but the higher altitude allows the cultivation of cash crops and spices (Wayanad is one of the biggest foreign exchange earners of the state),which has led to  ongoing exploitation of the natural  resources, which scientists have warned could lead to environmental crises. One such crisis has now come from a rather unsuspecting angle - Monkey fever which has reared its head in Wayanad. First, in December 2014 more than 100 monkey deaths were reported in Wayand wildlife sactuary ;  this was followed by cases of Monkey Fever in humans in Wayanad.  Since January 2015  there have been  127 reported  cases including  seven deaths in humans. Most of the affected have been tribals,  the indigenous people  who live in the forest and  mountains of Western Ghats. An outbreak on a smaller scale has also been reported in Malapurram district of Kerala again affecting the tribals in that area.

What is Monkey Fever?
Monkey Fever   otherwise known as Kyasanur forest disease (KFD)   is caused by Kyasanur forest disease virus (KFDV), a member of the Flaviviridae family. Other infamous members of this family include the virus that causes yellow fever and dengue . The disease was first identified in 1957  by Work and Trapido , with the observation of deaths in monkeys  with heavy mortality in two species of monkeys namely  the black faced langur (Semnopithecus entellus) and the red faced bonnet monkey (Macaca radiata)  followed by  high incidence of illnesses characterised by acute fever and a few deaths among the villagers in the forested areas of Shimoga district, Karnataka State. Subsequently  the virus was isolated from monkeys , man, and ticks from the Kyasanur forest in Karnataka, India and hence the name.


The vector, the main hosts, and the reservoir hosts
The vector for Monkey Fever appears to be ticks. The virus-infested ticks seem to infest diverse areas such as forest (tropical evergreen, semi evergreen and moist deciduous forests,) cultivated clearings and grasslands. KFD virus has been isolated from several  species of ticks  found in the Western Ghats , however, Haemaphysalis spinigera  is  thought to be  the  major vector . The main hosts of Monkey fever are rats, shrews, squirrels and porcupines, but bats and monkeys also carry the virus. Larger mammals such as goats and cows can become infected with KFD, but current evidence does not seem to implicate transmission of the disease though pasteurised milk. Among animals, current evidence shows that only monkeys seem to die upon exposure to infected ticks.

Often the first clue for the prevalence of the disease in any area  is monkey deaths, a gruesome warning that human cases could soon follow. Humans get Monkey Fever from a tick bite or by contact with an infected animal either ill or recently dead. Human to human transmission has not been reported so far.

Interestingly, Monkey Fever in humans seems to follow a seasonal pattern and human cases are usually reported from November until June, when young ticks or nymphs become active in forests. This time coincides with the warmer months when humans venture into forests for clearing forests, herding and for gathering firewood.

Symptoms, diagnosis of the disease, and treatment
Like many viral diseases there is an incubation period of 3-8 days with the virus,  after which the symptoms of Monkey Fever Disease  manifest suddenly with fever, severe headache, severe muscle pain, cough , diarrhoea and  dehydration. Sometimes, bleeding from nasal cavity, throat, gums, and gastrointestinal tract may also occur. Patients often experience abnormally low blood  pressure, and low  blood counts.  A small fraction of   patients recovers after 1-2 weeks of symptoms without complications. However, most patients present a biphasic illnesses pattern and begin to experience second wave of symptoms at the beginning of the third week. These symptoms include fever and signs of encephalitis. Confirmatory diagnosis can be made by isolation of virus from blood by cell culture methods. Sensitive techniques such as PCR can also be used in the diagnosis in the early stages of the disease. In the later stages of the disease, enzyme-linked immunosorbent (ELISA) can be sensitive in detecting the disease.

Whilst there is no specific treatment for Monkey Fever so far, rapid and timely supportive therapy is very important for preventing complications, hastening  recovery, and for reducing mortality. Treatment depends on the symptoms of the patient and includes hydration, adequate nutrition, and the usual precautions for patients with other bleeding disorders. Patients with preexisting  diseases such as tuberculosis and liver cirrhosis maybe more prone to dying.  Mortality rate  upon infection ranges between 3-5%.


Who is at risk?
Tribals (Indigenous people) living in forest areas who may come across the ticks or infected and dead monkeys during food gathering in the forest ( the  reported cases  in Kerala have largely been from the tribal hamlets),  people who earn a living from working in  the forest  (cattle grazers, forest officials and health care workers serving the tribal areas),  and hikers in the forest are potentially at risk for infection by contact with infected ticks or infected monkeys. 

Monkey fever : Another example of human -animal conflict ?
It has been long argued that  clearing of forest area for cultivation causes changes in tick fauna and is considered as  very pertinent to outbreaks. Deforestation could also cause the reservoir hosts to relocate into human settlements. Additionally, deforestation causes monkeys to come to human settlements in search of food.  Livestock grazing in cleared forested areas and grasslands also cause the ticks to attach to livestock and herders which in turn are accidentally introduced to human settlements.

Prevalence:  Monkey Fever is spreading
Although Monkey Fever Disease  was thought to be endemic to specific districts in Karnataka state,  as early as the late eighties, an antibody survey indicated the possible existence of this disease in Kerala and Tamilnadu although there were no reported  human deaths or monkey deaths then. Since 2013, Monkey Fever cases has affected Wayanad (Kerala)  and Nilgiris ( Tamilnadu), which makes it plausible that infections in these areas may have been missed earlier due to the  lack of an organized surveillance system. The evidence of KFD virus circulation in three southern states of India presently raises serious concerns for human health.  

Whilst eliminating the disease is nearly impossible due to the ability of the virus to hide in the reservoir hosts in the impenetrable forests, it could be contained effectively. Here are some recommendations:


Recommendations for the management of Monkey Fever Disease

The need for creating awareness of Monkey Fever Disease:  There should be awareness programs on monkey fever through different communication channels. Tribal settlements in Western Ghats often do not have access to modern amenities such as TVs , radios etc.  Illiteracy could also be high, therefore awareness messages using modern modes of communication might  not reach the target groups. Therefore awareness of the disease has to be ensured through health workers visiting the areas and communicating orally highlighting the need to avoid high risk areas, contact with dead animals and encouraging people to seek health care promptly on being ill.

Health care centres/mobile health clinics  in tribal areas neededTribal areas are notorious for having poor access to healthcare. Tribals are also the poorest citizens.  There is often lack of/ poor transportation to nearby towns where hospitals may be located due to lack of vehicular roads. Even upon reaching health care centres ,  tribals often  face discrimination and insensitivity  from health care officials. To circumvent this, tribal areas should be  provide with accessible health care centres with adequately trained health workers /doctors who could spot the disease quickly and give the appropriate treatment. Additionally mobile health clinics could also be employed that can bring health services to remote and isolated parts. Furthermore, these health care centres and mobile units could also collect data for  researchers who will be able to monitor , the prevalence, spread,  and changing patterns( if any) of the disease.

Vaccination campaigns in people in the target area and beyond:   Current vaccination practice uses  formalin-inactivated tissue-culture vaccine which  has been the primary strategy for controlling KFD in Karnataka . This is a seemingly a good one. However  recently published  studies from Karnataka shows that the currently adopted vaccination strategy has its own pitfalls. Valuable lessons can be learned that could be used in the other states to control the disease. Firstly the strategy in Karnataka involved mass vaccination of  persons 7–65 years of age  in the high risk regions . But the study showed that persons outside this range were also infected suggesting vaccination programmes to include persons  outside this age group . The study also showed that vaccine coverage in villages selected for vaccination in 2013 was surprisingly low. Further, the uptake of the vaccine was poor ( the current vaccine is multi-dosed  due to the transiency of  the vaccine-induced immunity ,requiring   two vaccine doses  to be administered  with the first booster dose of vaccine recommended within 6–9 months after primary vaccination after which annual booster doses are recommended for 5 years after the last confirmed case in the area) . Only some of the vaccinated persons took the full dose. The study showed that effectiveness  for persons taking full dose was 82.9%, two doses ( 62.4%)  compared to non-vaccinated individuals. The study also  indicated that targeting vaccination to areas within a 5-km radius of reported KFD activity may not be effective in preventing KFDV transmission as there have been  occurrence of cases in areas >5 km away from vaccinated villages.

In a nutshell, increased vaccine coverage is needed with respect to age as well as area (It has to extend beyond the ages of 7-65 years and has to extend to all persons- pending adequate medical advice for use in pediatric and elderly persons in the target area,  and  has to extend beyond the current limit of 5 km radius
Although cumbersome, full doses of current vaccine might be the best option currently available until better vaccines are available
There is a need for production of newer vaccines that accounts for drifts and diversity of current strain, and that which does not require periodic boosters. It is believed that such a vaccine would  lead to increased effectiveness and increased uptake.

Carcasses of infected dead animals to be disposed appropriately: Forest officials should be trained adequately in following appropriate biosafety procedures while handling infected animals and should dispose carcasses appropriately and expediently. They should also be trained in decontaminating surrounding areas where infected and dead monkeys are found.

Initiating Monkey Fever Surveillance Units: There should be active surveillance for Monkey Fever by instituting Monkey Fever Surveillance Units.  Not only target areas, but also regions outside should be tested in a systematic manner for virus positivity in ticks  far in advance of the peak season. This is indispensable for  preventing disease emergence in new areas.  In addition, disease surveillance systems should be in place to monitor effectiveness of vaccination programmes and for detecting any hidden niches of infection. Incidences of unusual monkey deaths and human fever cases should be monitored by the Monkey Fever Surveillance Units and information rapidly communicated  to forest officials and health authorities so that they can take prompt action.

Use of Preventive clothing and Tick repellents: Persons living in forests and those  visiting forested areas should be provided with preventive clothing and tick repellents . Tick repellents are reported to provide significant protection against tick bites.

Cordoning off the area : During the peak  season, the target  areas and areas in a  wider radius  should be off limits  for outsiders (apart from health workers and forest officials dressed in protective clothing)  and  hikers should  prevented  from going to the infected areas and also high risk areas.

Tourists encounter Bonnet monkeys near Ponmudi Hills

Banning cattle grazing: In the target areas, livestock grazing must be prohibited. In this respect it has to be emphasized that tribals are not the culprits, as they have no agricultural practices but only gather food in the forest.

Stop deforestation and slash-burn agricultural practices: Deforestation and slash -and -burn practices for agriculture forces the vectors from their natural habitats into human populations. Curtailing deforestation and harmful agricultural practices in the forests will prevent the spread of Monkey fever   and other such diseases.

Monkey Fever Disease preparedness and response plans : Scientists  have reiterated  that often the official response to an outbreak is too late. By the time monkey deaths are noticed in an area, the ticks have already flooded the locality. Therefore, the best approach is to prepare ahead and to have all containment measures in place much in advance.

Increased research on Monkey Fever Disease : Increased research is needed on monkey fever especially on the drift and diversity of the virus, and efforts should be made towards producing better vaccines. There is also limited knowledge on the susceptibility and prevalence of monkey fever in other monkey species ( For example  whether  the critically endangered species Lion tailed macaque is susceptible to infection) .  A concerted effort on understanding the natural history of the disease will enhance the efforts to curtail it.



Concluding thoughts
With the Monkey Fever Disease  season seemingly coming to an end, the authorities could easily fall into the trap of complacency and lethargy until new Monkey fever cases hit  the headlines next year. However, the ease by which the disease is spreading should be a warning to the authorities that it is a major perennial problem.  It is not one of those rare diseases anymore. Timely measures need to be in place to ensure that the disease does not spread any further as this could threaten monkey survival as well as cause a major public health crisis, which with passage of  time might be too difficult to contain.

Addendum
Since publishing this post, I have been contacted by the MCVR Virology Lab , Manipal , India that the disease has now been detected in Goa state also. 

References:
Mourya, D., Yadav, P., Sandhya, K., & Reddy, S. (2013). Spread of Kyasanur Forest Disease, Bandipur Tiger Reserve, India, 2012–2013 Emerging Infectious Diseases, 19 (9) DOI: 10.3201/eid1909.121884http://dx.doi.org/10.3201/eid1909.121884">10.3201/eid1909.121884
>
Kiran, S., Pasi, A., Kumar, S., Kasabi, G., Gujjarappa, P., Shrivastava, A., Mehendale, S., Chauhan, L., Laserson, K., & Murhekar, M. (2015). Kyasanur Forest Disease Outbreak and Vaccination Strategy, Shimoga District, India, 2013–2014 Emerging Infectious Diseases, 21 (1), 146-149 DOI: 10.3201/eid2101.141227http://dx.doi.org/10.3201/eid2101.141227">10.3201/eid2101.141227
>




Friday, 8 May 2015

Blue meets Green – What does Conservative party’s win mean for UK's environment?



The results of the general election are in. David Cameron will continue to lead the country for the next 5 years. But how does the UK’s environmental issues fare in the 2015 election manifesto of the Conservative party? Of the several promises listed in it, these grabbed my attention.

Creation of Blue belts for protecting marine environments in the UK and UK ‘s 14 overseas territories: Following on from the work in the previous term, the manifesto promises to complete the network of Marine Conservation Zones to create a UK Blue Belt of protected sites. Last year the coalition government  instituted a  Marine Protected Area around the Pitcairn Islands in the South Pacific –the world’s largest contiguous ocean reserve  with 830,000 square kilometers (3.5 times the landmass of UK).  The manifesto promises to extend this programme around the UK’s 14 Overseas Territories, subject to local approval. 

 Planting 11 million trees: This promise is significant especially because public forests and woodland where supposedly the trees would  be planted are to be kept in trust for the nation.

Building new environmentally sensitive infrastructures: The conservative manifesto promises to build roads and railways with reduced environmental impact. It promises to cut light pollution from new roads, build better noise barriers, include more tunnelling, and help restore habitats lost during construction. A specific case mentioned is that of the construction of High Speed 2 - the planned railways connecting London Euston with the Midlands through to the North. The manifesto promises to ‘replenish locally any biodiversity lost in the construction’. How they are going to achieve this is not mentioned in the manifesto.  Importantly ‘biodiversity’ cannot be easily replenished. Yes trees can be planted, some animals introduced,  however ‘ biodiversity’   refers to the variety of living organisms in different ecosystems starting with microbes and is complex. Thus, ‘replenishing biodiversity’ is not easily achievable, at least not  in totality, though conservation is possible and must be pursued .Therefore the 25 years plan that the Conservatives will develop to restore UK’s biodiversity is commendable.

Pocket Parks in urban areas: The manifesto promises to launch a programme of ‘pocket parks’  - small green spaces that town and city dwellers can enjoy .This is an excellent idea. Here in Ecoratorio, we have repeatedly highlighted the need for more green spaces in the cities.

One omission in the manifesto is the lack of any mention of how they plan to tackle pesticide overuse in the crops, which has been blamed for declining bee numbers. This is a lapse as the manifesto says that they ‘will help our bees to thrive’.


In the days ahead, we will see whether the new government remains committed to its promises.But one fact is clear that  a green Britain will assuredly contribute to a ‘greater Britain’.

Reference: Conservative Party Manifesto 2015  https://www.conservatives.com/manifesto

Monday, 20 April 2015

Urban green spaces: Insights from Valencia

Visiting the city of Valencia in Spain for the first time, we were pleasantly greeted by the subtle aroma of orange blossoms in the air and the sight of beautiful oranges dangling from the orange trees that line the street pavements. Whilst many parts of the city are bordered with trees, there are also other green spaces,  such as beautiful small parks (like the one in the picture  shown below),
complete with Mediterranean flora such as palms, ficus, cycas, and orange trees. 




 The most impressive green space is perhaps the 9 km green belt that runs through the city-  the Jardi delTuria (Garden of the Turia), which is a credit to the city. The Turia is a Spanish river that empties into the Mediterranean near the city of Valencia. In 1957, it flooded and devastated Valencia. Consequently, the course of the river was artifically changed- now running along the city edge before meeting the Mediterranean. The original course of the river continues has been converted into an enormous green space resplendent with beautiful trees with pedestrian paths, cycle paths, and occasionally dotted with football grounds, cafes, athletics tracks, and gardens within the garden. Here city dwellers relax, play, or just get about their business, avoiding the traffic that plies overhead on the many bridges that cross the river bed. Buildings tower over either side of the Turia garden, comprising largely of apartment blocks and businesses. Our walk along the Turia garden in sweltering sunny April was very pleasant which made me realize the importance of green spaces in cities.



Urban heat islands and global warming

Cities have their own micro-climates. Human activities- buildings made of concrete,  asphalt roads , vehicular emissions, heat generated by people, and heat arising from equipment use, all contribute to temperature increases in the urban areas to levels that are significantly higher from the adjoining rural areas where temperatures remains close to air temperatures. Such urban areas are called ‘Urban heat islands’, a concept described over 200 years ago by Luke Howard, the father of meteorology. The term has been coined  as the warmer urban air lies in a ‘sea’ of cooler rural air.  According to the EPA, the annual mean air temperature of a city with 1 million people or more can be 1.8–5.4°F (1–3°C) warmer than its surroundings, going up to temperature difference as much as 22°F (12°C) on a clear, calm night.

Heat islands could not only affect the health of the urban inhabitants by causing heat -related illnesses (a topic discussed in the earlier post), but also contribute to global warming in general, and must not be ignored particularly as predictions indicate that by 2050 about 64% of the developing world and 86% of the developed world will be urbanised - leading to amplification of the issue. Whilst urbanisation cannot be halted, it must be made sustainable.

Mitigation strategies for urban heat island effects

Among the four major strategies United States EnvironmentalProtection Agency (EPA) has suggested for mitigating the effects of urban heat islands, the first one is increasing tree and vegetation cover. The others are the installation of green roofs (roofs with plants grown over a waterproof membrane), installation of cool and reflective roofs (built from materials with high solar reflectance and high heat emittance), and building cool pavements (made of material with high solar reflectivity and good water permeability).

In this post, we will look at the EPA’s primary recommendation. This, in my opinion, is the one with the maximum impact and the least costliest. The major benefits of increasing trees and vegetation covers are the following:
They reduce surface and air temperatures by providing shade and by the process of evapotranspiration. Estimates indicate that evapotranspiration, alone or in combination with shading, can help reduce peak summer temperatures by 2–9°F (1–5°C). By providing shade to buildings, trees decrease the demand for air conditioning and indirectly decrease the need for energy use which, in turn, lowers greenhouse gas emissions and provides better air quality. Trees also function as ‘sinks’ for air pollutants and carbon dioxide. Trees improve the quality of life of city dwellers by enhancing the aesthetic value of their surroundings and promote biodiversity by providing habitats for diverse species.

Interestingly, it  also appears that for some trees living in an urban environment might not be bad after all. In a study in 2012, seedlings of oak were grown for one season at four sites along an urban–rural transect from Central Park in New York City to the Catskill Mountains in upstate New York  with a difference in average maximum temperatures of 2.4 °C and  difference in minimum temperatures of 4.6 °C.  Additionally, seedlings were cultured in growth cabinets simulating the seasonal differential between the city and rural sites. The researchers found that warmer temperatures associated with the urban environment, especially high night-time temperatures, lead to enhanced growth in these seedlings.

The necessity for a Green Channel Programme for our cities

Coming back to our example - Valencia- it appears that the city is going in the right direction with its tree and vegetation cover initiatives. The green spaces and the green belts are not only aesthetically pleasing, but also reduce the heat (personal experience). Increasing the vegetation cover in cities is something where more is less. Thus, Valencia and other cities who have such initiatives cannot rest on their laurels. We really need to have green channels through our cities to cool the urban heat islands.


References

http://www.valenciavalencia.com/sights-guide/turia.htm
http://www.epa.gov/heatisland/about/index.htm

Searle, S., Turnbull, M., Boelman, N., Schuster, W., Yakir, D., & Griffin, K. (2012). Urban environment of New York City promotes growth in northern red oak seedlings Tree Physiology, 32 (4), 389-400 DOI: 10.1093/treephys/tps027http://dx.doi.org/10.1093/treephys/tps027">10.1093/treephys/tps027
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Tuesday, 14 April 2015

Global Temperature Rise and Human Health - How is the World Coping?






Global temperatures have been on the rise since the Industrial Age due to human activity such as the emissions of greenhouse gases from fossil fuel burning, large-scale deforestation, expansion of urban areas where vegetation cover is replaced by artificial heat retaining materials such as asphalt and concrete, some agricultural practices, and waste management activities. Data from the National Climatic Data Centre that  maintains the world's largest climate data archive indicate that the average global temperature across land surfaces was 1.68°C (3.02°F) above the 20th century average of 3.2°C (37.8°F) . To put things in perspective, February 2015 was much warmer than February 2014.

 Epidemiological studies in different parts of the world have unequivocally shown a strong link between high temperature and mortality, which is a public health concern. The magnitude of the problem will only escalate as the global mean temperature continues to increase causing extreme heat events in large geographical areas. Approximately 650 deaths per year occur in United States due to heat events, which account for more fatalities than any other weather hazard. Males outnumber females in deaths cause by extreme heat events.


Vulnerable population for heat-related deaths


 Although the human body can tolerate changes in temperature by the process of thermoregulation, whereby it can protect itself from extremes in ambient temperature, there are limits. Importantly, infants and the elderly particularly those with health conditions such as cardiovascular disease, cerebrovascular disease, neurological diseases, diabetes, renal disease and respiratory disease are particularly vulnerable to mortality due to increase in ambient temperature. However, many studies indicate that there is a lack of risk perception among the population to heat-related deaths.


Global disparity in knowledge pertaining to extreme heat, its consequences, and public health responses  


 In many developed nations, data on temperature rise and its consequences on health are often readily available due to good documentation of historical temperature records and epidemiological research in these areas. Heat vulnerability maps (Heatwave maps) now exist for many areas in developed countries- particularly cities, that help identify regions that are at risk for extreme heat events. In many such places, Heat response plans that help prepare communities for heath rated illnesses exist.
However, developing nations lag behind both in research as well as public health strategies to mitigate extreme heat events. A plethora of factors such as  knowledge gaps, defective record keeping and poor research (death records, which list causes of death are often unreliable particularly in rural areas), archaic technology, lack of funds, corruption, poor public health initiatives, all lead to poor knowledge  or ignorance  pertaining to the health effects of extreme temperature. The health implications of extreme heat  is likely to be  far more pronounced in the developing countries, which are often subject to extreme climate change compared to the developed countries, but is likely staying under the radar.

Here through the pages of Ecoratorio, we have often highlighted the dangers of human activities on the environment and the need for global, personal, and corporate environmental stewardship. Specifically in the context of heat-related illnesses and deaths, a cohesive understanding of the environmental impact on human health, identification of vulnerable populations, expert recommendations on public behaviour and timely communication of these recommendations, generating public awareness through mass media of health-related illnesses and deaths, and enforcement of mitigation steps in the general public is critical. With extreme heath events anticipated to rise in the coming years due to climate change, population increase, and increase in ageing population, it is crucial that  scientific, political and public health action should take place to manage this important issue.



Useful Facts about Heat-related illnesses

  • Although many studies have stressed infants and elderly as being most vulnerable to heat –related illnesses and death, other high-risk groups include young children, older adults (people over 65 years) and people who engage in strenuous activities outdoors.
  • Extreme heat events disproportionately harm vulnerable populations.
  • The majority of heat-related deaths are preventable.
  • During periods of extreme heat, heat-related illnesses can be prevented by using air-conditioning, avoiding strenuous outdoor activities, drinking adequate amounts of fluid, wearing lightweight clothing, and avoiding alcohol consumption. 
  •  Heat Response plans should be in place before extreme heat events occur.
  • Major inequalities exist between developed and the developing nations in the awareness of heat- related illnesses, the contributory factors, and public health initiatives.
References:

  1. http://www.ncdc.noaa.gov/sotc/global/
  2.  http://monash.edu/news/show/heatwave-map-reveals-melbournes-most-vulnerable-postcodes
  3.  Madrigano, J., Ito, K., Johnson, S., Kinney, P., & Matte, T. (2015). A Case-Only Study of Vulnerability to Heat Wave–Related Mortality in New York City (2000–2011) Environmental Health Perspectives DOI: 10.1289/ehp.1408178http://dx.doi.org/10.1289/ehp.1408178">10.1289/ehp.1408178>
  4. Kim, C., Lim, Y., Woodward, A., & Kim, H. (2015). Heat-Attributable Deaths between 1992 and 2009 in Seoul, South Korea PLOS ONE, 10 (2) DOI: 10.1371/journal.pone.0118577http://dx.doi.org/10.1371/journal.pone.0118577">10.1371/journal.pone.0118577>
  5. http://www.epa.gov/climatechange/science/indicators/health-society/heat-deaths.html
  6. Bobb, J., Peng, R., Bell, M., & Dominici, F. (2014). Heat-Related Mortality and Adaptation to Heat in the United States Environmental Health Perspectives DOI: 10.1289/ehp.1307392http://dx.doi.org/10.1289/ehp.1307392">10.1289/ehp.1307392>
  7. http://www.medscape.com/viewarticle/806947

Monday, 8 July 2013

Humans vs Tigers

I have been following an interesting news of a match of Humans vs Tigers. The eventual outcome was a draw: one man and a tiger cub killed on each side.

 The story is that six men from Simpang Kiri village in Aceh Tamiang district went to the Mount Leuser National Park on Sumatra Island for harvesting agarwood (used in incense and perfume). I am assuming that this was probably illegal since national parks does have restricted entry and harvesting this precious material is probably regulated. Nonetheless, they set traps to catch deer (again, I am unsure about whether this amounts to poaching) and caught a Sumatran tiger (Panthera tigris sumatrae) cub instead (which eventually died). This action attracted 5-7 tigers in the vicinity who, quite notably, chased the men. The men climbed up some trees and hung on to dear life for five days, subsisting on rainwater. The tigers, equally persistent, remained at the base. One man was mauled to death when he fell down after a branch snapped. The others contacted nearby villagers via the cell phones. The villagers were helpless, but eventually "tamers" and the rescue team drove the tigers away.

 I could debate at length about whether the men deserved the plight they faced, but more interesting is the behaviour of the tigers. The Sumatran tiger is the smallest (75-140 kg - Prothero et al, 2012) and is critically endangered (Sunarto et al, 2013). It is endemic to, well, Sumatra and the population is around 350. The low numbers are due to deforestation and conversion of lands into acacia and oil palm plantations, fires, and poaching (O'Brien et al, 2003; Sunarto et al, 2012; Johnson, 2013) . This plight was recently highlighted by Sunarto et al, 2013, who calculated that numbers were much lower in the Riau province which was believed to have the highest concentration of tigers (Banerjee, 2012, state that the population had declined by 70%; from 640 in 1982, the numbers fell to 192 in 2007). In a previous paper, the same authors proved that tigers are not particularly fond of plantations and settlements, preferring large contiguous and undisturbed forests and higher altitudes. However, the authors also encourage using the plantations as "corridors, stepping stones, or mosaics of connectivity facilitating animal movement"- which, in my humble opinion, is a recipe for disaster for both tigers and humans.

Indeed, it is sad that a human life and a tiger life were lost. But it could have gone in a few different ways. Five other humans could have been killed. So could have 5-6 critically endangered tigers. We very seldom recognise how our lifestyle preferences (I too have found agarwood to be particularly heady) might be only aggravating human-animal conflict elsewhere...

 Image source: http://www.istockphoto.com/stock-photo-2885355-b-w-sumatran-tiger.php

References Kimberly Elizabeth Johnson (2013). Living Off the Fat of Another Land: Trans Fat Social Policy and Environmental Externalities Environmental Policy is Social Policy – Social Policy is Environmental Policy, 37-50 DOI: 10.1007/978-1-4614-6723-6_4  
Timothy G. O'Brien, Margaret F. Kinnaird, Hariyo T. Wibisono (2003). Crouching tigers, hidden prey: Sumatran tiger and prey populations in a tropical forest landscape Animal Conservation, 6, 131-139 DOI: 10.1017/S1367943003003172
Donald R. Prothero, Valerie J. Syverson, Kristina R. Raymond, Meena Madan, Sarah Molina, Ashley Fragomeni, Sylvana DeSantis, Anastasiya Sutyagina, Gina L. Gage, Size and shape stasis in late Pleistocene mammals and birds from Rancho La Brea during the Last Glacial–Interglacial cycle, Quaternary Science Reviews, Volume 56, 21 November 2012, Pages 1-10, ISSN 0277-3791, http://dx.doi.org/10.1016/j.quascirev.2012.08.015.

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