Saturday, March 21, 2020

Impact of Perry essays

Impact of Perry essays On July 8, 1853, Commodore Matthew Perry of the United States Navy, commanding a squadron of two steamers and two sailing vessels, sailed into Tokyo harbor, carrying the message to the Japanese authorities : Agree to trade in peace, or suffer the consequences in war.(Andrew Gordon, Modern History of Japan, p49). His mission signified American interest in Japan trade. After taking over California from Mexico in the 1848, Americans wanted to become a commercial power in the Pacific. Also, with the whaling supplies exhausted in the Atlantic, Americans and British whalers had ventured into the Pacific waters and facing the competition of the British, the American wanted Japanese to sell coal to their naval fleet and allow resupply stops for the whalers in Japanese ports and to open Japan as a new market for their manufactured goods. Japan at this time was ruled by the shogun from the Tokugawa family and during this period, Japanese contacts with outsiders were severely limited, primarily due to the fear of the shogun and the other samurai that outside contacts presented a potential threat to their power. In response to this incident, the shogun ordered defence to be strengthened along the coastline and rumours of impending war sparked off panic in Japan. Also, the shogun did something unprecedented and unusual, he actually requested the various daimyos submit their advice on how to best deal with the Americans in hope of rallying a consensus for his choice to make some concessions and avoid war(Gordan, Modern History of Japan, p49). In early 1854, he returned with a fleet of 9 ships and the Japanese tried to intimidate the Americans but to no avail, and faced with the firmness of Perry and aware of their military strength relative to the Americans, the shogun signed the Treaty of Kanagawa which opened 2 ports(Shimoda and Hakodate) to the Americans. This event was followed by similar treaties with other Western p...

Thursday, March 5, 2020

Politics of George Clooney, Actor and Liberal Activist

Politics of George Clooney, Actor and Liberal Activist American actor George Clooney is a liberal, a strong supporter of liberal causes and charities, and an outspoken critic of conservative politics and warmongering. Clooney supported John Kerry for President in 2004; Barack Obama in 2008 and 2012, and Hilary Clinton in 2016. Among other causes, he actively supports gay rights. Im a liberal. Im confused when that became a bad word. Its interesting. I think what happened over a period of time, probably in the late 80s when it became sort of a political tool.... [T]he liberal movement morally, you know, has stood on the right side of an awful lot of issues. We thought that blacks should be allowed to sit at the front of the bus and women should be able to vote, McCarthy was wrong, Vietnam was a mistake.  George Clooney to CNNs Larry King on February 16, 2006. Actor, Director, Producer George Clooney is best-known as having been a television and film actor since early 1980s, and as a director and film producer since 2002s Confessions of a Dangerous Mind. Most Americans first noticed him as the handsome Dr. Doug Ross on the popular television program ER from 1994 to 1999. Clooney regularly appeared in five other television shows prior to ER. Clooneys acting credits range from the goofy Return of the Killer Tomatoes (1988) to the seriocomic O Brother Where Art Thou, the Coen brothers 2000 take on Homers The Odyssey. His writing, producing, and directing credits include political-commentary films such as Syriana (2005) and The American (2010), as well as historically-themed films such as The Monuments Men (2014) and Good Night, and Good Luck (2006). The Clooney Family George Clooney was born in 1961 near Lexington, Kentucky to Nick Clooney, a regional newscaster and well-liked TV personality, and Nina Warren Clooney, local city council member, and former Kentucky beauty queen. Hes also the nephew of the singer Rosemary Clooney and cousin of actor Miguel Ferrer. One 2003 article dubs the Clooney clan the Kennedys of Kentucky for their formidable liberal influence in the conservative northern part of that state. By all reports, the Clooneys are a close-knit, Irish-Catholic family, and George is fiercely loyal to his father. When Nick Clooney ran for Congress in 2004, George raised over $600,000 from fellow celebrity-activists for his fathers unsuccessful campaign and made personal appearances on behalf of his father. Charity Causes In the charity world, Clooney is known for his work with numerous disaster relief efforts, including America: A Tribute to Heroes in 2001 for victims of 9/11; Tsunami Aid: A Concert of Hope, to benefit victims of the late-2004 Indian Ocean tsunami; and the Hope for Haiti Now for the victims of the 2010 earthquake. Clooney donated $1 million in September 2005 to the United Way Hurricane Katrina Response Fund to help out the victims of the hurricane. Clooney is a member of the United Way Board of Trustees. Said Clooney when he made the donation, Today our neighbors need food, shelter, and health care, but the very near future is when the difficult part of rebuilding lives and homes and cities starts. Were all in this one together. In March 2006, Clooney donated his Oscar gift-bag (Value: about $100,000) to the United Way, to be auctioned off to benefit that humanitarian organizations programs. Preventing Mass Atrocities Clooney has also contributed money and time to the recognition, prevention, and cessation of genocides and mass atrocities. He was instrumental in the creation of Journey to Darfur, a program on the ongoing conflict in Darfur; the recognition of the Armenian Genocide; the Satellite Sentinel Project reporting on the civil war between Sudan and South Sudan; and the Aurora Prize, which awards people who risk their lives to present genocides and atrocities. In 2006, Clooneys longtime liberal activism and unabashed political views also rose to headline-attracting public prominence. After a 5-day visit to Darfur, Clooney spoke out against genocide in that country and urged greater US and NATO involvement. In September 2006, Clooney testified before the UN Security Council, urging that UN peacekeepers enter Darfur. Clooney and the Conservative Media Clooney has been the focus of attacks from conservative media outlets. In September 2001, Clooney was a primary organizer on a telethon to raise money for victims of 9/11. The program, America: A Tribute to Heroes raised US $129 million which was donated to The United Way. Conservative political commentator Bill OReilly took Clooney and his associates to task for not appearing on The OReilly Factor program to respond to scattered news reports that the money was not, in fact, going to the victims. Infuriated, Clooney responded in an angry letter to OReilly on November 6, 2001, in which he scolded, The fund is not only the most successful single fundraiser ever, it is doing exactly what it is designed to do. Responsibly. The money is going out to the right people... In 2014, the British tabloid The Daily Mail reported that the family of his then-fiancee, Amal Alamuddin, opposed their marriage on religious grounds, saying that some of her relatives had joked about killing the bride if she disobeyed her parents. Clooney wrote an open letter in the USA Today calling the paper a laughable tabloid that crossed into the arena of inciting violence. A Few Political Films Over his career, Clooney has appeared in and had some creative control over the production of several films with political content. Here are a few of the best known. Three Kings (1999)- At the Gulf Wars end, four US soldiers come across a potential jackpot: a rolled up treasure map to Saddam Husseins stashes of confiscated gold hidden bewteen the buttocks of a captured soldier. While pursuing selfish gain, the men collide with Iraqi civilians and experience a different side of the war.Confessions of a Dangerous Mind  (2002)- Based on the life of Chuck Barris, who claimed dual careers as loony game-show host and CIA operative for the US government. Also directed by Clooney.Good Night, and Good Luck (2005)- Taking place during the early days of broadcast journalism in 1950s America, this film chronicles the real-life conflict between newsman Edward R. Murrow and Senator Joseph McCarthy and his House Un-American Activities Committee. In a political climate of fear and reprisal, the CBS news crew persists. McCarthy is brought before the Senate and made powerless as his lies and bullying tactics are finally uncovered. Clooney was nominated for a Bes t Director Oscar for this film. Syriana (2005)- In this political thriller that unfolds against the intrigue of the global oil industry, Clooney plays the role of career CIA operative who disturbing truths about the work to which he has devoted his life. He won the 2006 Best Supporting Oscar and a Golden Globe for this role.The Ides of March (2011)- Clooney directed and co-wrote the screenplay for this take on modern-day dirty politics,Money Monster (2016)- A financial TV hose and his producer are taken hostage by an irate investor who is convinced there is a conspiracy driving fluctuations in global high tech markets. Summing Up Liberalism When asked in 2005 by the German magazine Brigitte, why conservatives continually vilify liberals, Clooney succinctly summed up liberalism.... Its quite amazing that liberal nowadays has become a swear word as in the history of our country it always meant to be on the side of justice. It started with the witchhunt in Salem, the conservatives point of view was: Burn them at the stake, and the liberals point of view was: There are no witches. And thats how it continued with the civil rights movement and womens suffrage. The liberals were always right in the end. Sources: Carr. 2005. A ringside seat for Murrow versus McCarthy. The New York Times, 18 September 2005.Cieply M. 2010. Within days, a global benefit takes shape. The New York Times 21 January 2010. Gibson, C. 2017. George Clooney takes aim at powerhourse D.C. lobbying firm over its ties to the Sudanese government. The Washington Post 7 July 2017.Somaiya R and Haughney C. 2014. Heard the News on George Clooney? This Much Is True: He’s Livid. The New York Times, 11 July 2014.Internet Movie Database (IMDb). 2017 George Clooney. Downloaded 24 November 2017

Monday, February 17, 2020

How to lie in Statistics Essay Example | Topics and Well Written Essays - 1000 words

How to lie in Statistics - Essay Example I feel statistical information presents the facts as they are. The characteristics of the samples are made to show the characteristics of the entire population under study. The sample’s statistical results are generally assumed not to represent the characteristics of those who are not part of the population. For example, the $25,111 salary represents the average salary of people chosen for the statistical tests (such as people in Yale alone). However the $24,111 salary does not represent the people not chosen for the survey, such as the people working in Alaska (14). Likewise, the $25,111 average salary is true only for the time period when the statistical tests were undertaken. However, the $25,111 average salary may not be true when the same statistical tests were taken 30 years prior to the current Yale statistical tests. Likewise, a similar test conducted 20 years after the current statistical tests will generally show a different statistical finding (18). Interpreting the difference in the findings, the statistical findings should not be taken as occurring in ALL situations; to do so would be a lie. It is a lie because interpreting the statistical results is all-encompassing would be too twisted, exaggerating, oversimplified, or distorted. Sales people would use the average results of statistical test to convince the prospective buyers to purchase their wares; the sales persons are willing to lie to generate sales. Consequently, many buyers are persuaded by the statistical test results to buy the sales person’s products and services. The buyer wants to join the â€Å"band wagon† by buying what the average person wants to buy (103). I feel the author (9) correctly emphasized the statistical data can show the validity of the first sentence â€Å"There’s a mighty lot of crime around here†. However, such interpretations are subject to correction. For example, statistical data showing the number of crimes committed in one neig hborhood can be more persuasive to the leaders when compared to absence of statistical information on the same topic. In fact, the average person can easily draw up several theories based on common sense or statistical trends. However, the trends are high probabilities (not100 percent assurance) of future outcomes. Further, I correctly understand that statistical information correctly presents quantitative as well as qualitative figures as basis for decision making. The manager can base one’s expansion policy on the statistical figure stating there is a huge profit. However, the manager must beware of false statistical figures. The statistical computation of the gross profit figure may be based on erroneous data. Likewise, the manager must ensure that the mathematical computation of the statistical results is accurate (112). To ensure that statistical outcomes are reliable, the manager must determine if the there is no distortion or manipulation of the raw statistical data ga thered. Someone may have intentionally changed or manipulated the real statistical data to suit selfish or biased needs. The spoiled statistical data will generate unrealistic statistical findings. The unrealistic statistical findings will trigger unprofitable management decisions (133). I think statistics generally shows facts that are based on real outcomes. The records of the Connecticut Tumor Registry show that cancer survival has increased due to the

Monday, February 3, 2020

John Stuart Mills Utilitarianism Essay Example | Topics and Well Written Essays - 500 words

John Stuart Mills Utilitarianism - Essay Example Mills view on this statement is on the quality of happiness that matters and not the quantity of pleasure. He is also of the view that one pleasure may be more valuable than another. If there is an instant where all that have exposure of both pleasures give a decided preference despite any act of moral obligation to choose it, mills sees it as the more desirable pleasure. It is evident that if one pleasure is far above the other that it is preferred even when it is not satisfying there is another pleasure in the environment is capable to fill the discontent. Mills also view that no human being can be contented to be transformed into any of the lower creature for the benefit of full interest of a beast’s pleasure. It is apparent that a man cannot wish to sink into a lower level of life. This may be associated with the love of liberty and independence (Mill, 2002). I agree with Mill in his statement that it is better to be a human being dissatisfied than a pig satisfied. The observation that even a noble character can bring less happiness to an individual as for the society it is beneficial. It is apparent that the outstanding happiness principle assures the total amount of happiness as the noble character even when it is not desirable to an individual. I agree also with Mills that no person in his conscience mind would be selfish even when he is persuaded that the fool is satisfied with his interest than he is with his. Another reason I agree with Mills is that a being of higher dignity is entitled to more to be happy. A human being is capable of more specific suffering and certainly has access to more opportunities than creature of an inferior type (Mill, 2002). In the instance one try to know what satisfies a pig, one can find out is that it is food. It is evident due to its greedy nature a pig tends to eat a lot. As for human beings satisfaction is not only brought by food as surrounding oneself with

Sunday, January 26, 2020

Alpine Plant Biodiversity in the Central Himalayas

Alpine Plant Biodiversity in the Central Himalayas Alpine Plant Biodiversity in the Central Himalayan Region: Perspective of Global Climate Change Summary Increase in surface temperature at global scale has already affected a diverse set of physical and biological systems in many parts of the world and if it increases at this rapid rate then the condition would be worst one could have ever thought off. Garhwal Himalaya, major part of the great Himalayan mountainous system is also much sensitive and vulnerable to the local, regional and global changing climate. Due to strong altitudinal gradient, varied climatic conditions and diverse set of floral and faunal composition, the impact of climate change seems to be much higher. This paper highlights some important features of the changing pattern of vegetational composition, distribution and impact of climate change on the phenological aspect of major alpine plant species present in the Garhwal Himalayan region. It also shows cumulative changes, which operate at local level but are globally pervasive. These cumulative changes include change in the land cover/ land use and other anthropogen ic activities, which are related to the climate change. Overall biodiversity in the Himalayan region has been depleted as the consequences of complex and multitude pressure of climate change. The depleted biodiversity has indirectly affected the socio-economic development of the local communities on which their sustenance depends and is inherently critical to the consideration and management of natural resource. Introduction Plant diversity and Status The varied altitudinal, climatic and topographical conditions in the Himalaya results in different types of microhabitats. Geographic isolation, glaciations, evolution and migration of the species in the past all together have contributed to the high level of biodiversity in this mountain system. As per genetic, species and ecosystem level resources, Himalaya is one of the hotspots of biodiversity in the world, which represents about one-tenth of the worlds known species of high altitude plant and animal species. Some parts in the Himalayan region are center for origin of many crops and fruit species and are important source of gene for their wild relatives. The floral diversity of this region shows assemblage of many endemic and exotic species of plants from the adjoining regions. A large number of western Himalayan flora in the Garhwal Kumaon region seems to have been invaded from Tibet, western China and adjoining north-east Asia (Rau, 1975). In the present scenario biodiversity seems to have been depleted in these regions due to land degradation, habitat fragmentation, increasing population pressure, over exploitation of bio-resources and finally due to the changing pattern of the climate. Nearly 10% of flowering plants are listed under various categories of threatened species. Red Data Book of Indian plants listed about 620 threatened species, of which, 28 are presumed extinct, 124 endangered, 81 vulnerable, 160 rare and 34 insufficiently known (Nayar and Sastry, 1987, 1988), however, Red list of threatened plants indicates 19 species as extinct. Among others, 1236 species are listed as threatened, of which, 41 taxa are possibly extinct, 152 endangered, 102 vulnerable, 251 rare and 690 of indeterminate status (IUCN, 1997). From the Himalayan region the important plant species included in threatened categories are mostly the valuable medicinal and aromatic plants, which, support the economic condition and health care sys tem of the local communities. It is well known that, in the context of the present scenario of climate change especially due to global warming many of the high-elevated ecosystems are severely sensitive and vulnerable. Their fragility may accelerate the changes occurring in their composition and structure to the slight variations in climatic factors. These regions include glacier, alpine pasture/ meadows and timber line ecosystem, which are the important source of the seasonal runoff, freshwater, valuable medicinal and aromatic plants, grazing land, source of timber and wild edibles for the mankind. Future scenario of climate change: According to the Third Assessment Report of Intergovernmental Panel on Climate Change (IPCC) 2001, average global temperature close to the earths surface has increased by 0.6 Â °C Â ± 0.2Â ° C since 19th century mainly due to the emission of CO2. If human beings do not act to reduce the present level of CO2 there will be additional increment in temperature of 1.4Â ° C to 5.8Â ° C in the next 40 100 year. Current information available on the pattern of future climate change through General Circulation Models (GCMs) suggested that the annual mean warming would increase about 3Â °C in the decade of 2050s and about 5Â °C in decade of the 2080s over the land region of Asia. Precipitation would increase annually about 7% and 11% in decades of 2050s and 2080s respectively. There would be a decline in the summer precipitation that seems likely to be over the central part of arid and semi-arid Asia. GCM also showed high uncertainty in future projection of winter and summer precipitati on over south Asia, because much of tropical Asian climate is noticeably associated with the annual monsoon cycle. In Central Himalayan region, through the assessment of people perception it is interpreted that, climate change resulted in the increase in warming, decline in rainfall during March- May, high rainfall during Aug- Sept instead of normal peak in July- Aug, decline in the snowfall intensity and winter precipitation in Jan-Feb instead of Dec-Jan (Saxena et al., 2004). This scenario can hardly trigger to think about the changing pattern of climate or its negative and positive impacts at local, regional and global level. Although assessment of future climate change scenario through some of scientific models needs a better infrastructure and high technological inputs, specific impact of climate change on different ecosystems can be discerned by comprehensive studies on long term monitoring of the different aspects of ecosystem which is lacking in the Indian context especially in the Garhwal Himalayan region due to poor infrastructure and management practices. So, as per as need concern in these remote areas the assessment of impact on the natural resources in future climate changes can be done through the site-specific sensitivity analysis and it can be related to the traditional knowledges of the peoples living in this particular region of the Himalaya. Sensitivity analysis would help to assess what will be happen if various climatic variables changed, and analysis also evaluates the positive or negative impacts of changing climate on the natural resources. This assessment would help us to make the l ocal communities realize the importance of conservation and management practice so that the endangered and threatened species could be saved from becoming extinct. Assessment of vulnerability and adaptive capacity of the various ecosystems and to develop indigenous knowledge based coping mechanism are important to determine the impact of climate change. This also links the ecological processes to the social processes and appreciates the relationship between the biodiversity and ecosystem functioning. Climate change: Impact on different vegetation zone Natural ecosystems at high elevations are much more sensitive to the climatic variations (Ramakrishnan et al., 2003) or global warming then the managed systems. Their sensitivity is prominently attributed to their limited productivity during snow-free growing season (Price et al., 2000), low dispersal capability, geographically localized, genetically impoverished, highly specialized and slow reproducing ability of the high altitude plants (McNeely, 1990; WWF, 2003). As a consequence of global warming the present distribution of species in high altitude ecosystems projected to shift higher as results of upward altitudinal movement of the vegetation belts. Although the rate of vegetation change is expected to be slow and colonization success would depend on the ability of adaptation and interaction of the plant species with the climate and other associated species, weeds, exotic and invasive species. Their success also depends on their ecological niche width and their role in the ecosy stem functioning. Increase in the temperature would result competition between such species and new arrivals. As the result, species which have wide ecological tolerance have an advantage to adapt and those which are at the edge of range, genetically impoverished, poor dispersal ability and reproducer are under the threshold of extinction. A likely impact of climate change is also observed over the phenological aspect of vegetation in the alpine, sub alpine and timberline zone. Changes in the pattern of snowfall and snowmelt in these mountain regions and increase in mean annual surface temperature has pronounce impact on the date and time of the flowering and other phenophases of certain valuable, keystone species of plants. Earlier snowmelt simulate early flowering in some early growing plants and possibly increase in surface temperature may extend the growing period and productivity of certain grass species in the cooler climatic region. There is a gradual decrease in the growing period from timberline to the snow line, Rawat and Pangtey, (1987) reported about 20 weeks growing period near timberline and barely 4-6 weeks above 5000 m asl. Thus, increase in the average temperature due to global warming the growing period of the vegetation would be seems to extend at high altitudes. Evidences of climate change through p eople perception in Garhwal Himalaya reveals that increase in the warming results decline in the yield of apple fruits and shortening the maturity period of winter crops, whereas, the production of cash crops like potato, peas and kidney beans under warm condition increases. Change in rainfall pattern, snowfall intensity will increase large-scale mortality and damage to the crops, which are close to the maturity on the other hand, Barley and wheat crop production is severely affected due to winter precipitation in months of Jan- Feb (Saxena et al., 2004). Vulnerability of different vegetation belts in the Garhwal Himalaya. Dominant tree species in the low and mid altitude zone have a wider range of distribution. Shorea robusta the climax species of lower elevation is distributed over moist to dry deciduous bio-climates in central India where temperature is much higher while rainfall is quite low. Quercus spp. the climax species at mid elevation is also distributed over a wide range (1100- 1800m) The mid altitude which is dominated by broad leaves and coniferous forest (Rao, 1994) mainly species of Quercus spp. and Pinus spp. on response to the warming may be replaced by the species like Shorea robusta and Terminalia spp. Warming also increases the chance of greater fire risk in dry or moist deciduous forests, these impacts on the forest can directly influence the local livelihood based on fuel and fodder (Ramakrishnan et al. 2003). Rhododendron arboreum is a very prominent forest species because of its red flowers covering almost the whole canopy. At higher elevations this species used to attain peak flowering stage in February / March but now due to warming flowering time in this species seems to shift in the months of January/February. The phenological calendar at lower altitude has thus shifted to the higher altitudes. Exact times of leaf fall, flushing, flowering and fruiting may vary depending upon the elevation indicating sensitivity of phenophases to temperature and moisture stress regime. Flowering and fruiting start earlier about a month with increase in elevation by 600 m (increase in temperature by 2.4 degree C) in Rhododendron arboreum, Prunus cerasoides, Myrica esculenta, Pyrus Pashia and Reinwardtia indica in Central Himalaya. Leafless period in deciduous species like Aesculus indica and Alnus nepalensis is longer at higher altitude as compared to lower altitude. At higher elevation (1500-3300m) i n Central Himalaya, evergreen and winter deciduous species occur equally across the elevation/temperature gradient. All across the elevation / temperature gradient, majority of tree species show vernal flowering. Species showing vernal flowering (before 15 June) increased in frequency and those with aestival flowering (between 15 June 15 September) decreased with increase in annual temperature drown based on the elevation gradient. Thus, change in the temperature would affect flowering and fruiting time of different species or also induce change in species composition. Vegetation of the timberline in different parts of world not only differs in terms of species composition but also exhibit different types of species (Crawford, 1989). In some regions the timberline represents exclusively evergreen conifers while in some it represents totally deciduous broad-leaved trees (Purohit, 2003). In the central Himalaya the Betula utilis, Abies pindrow and Rhododendron campanulatum, are the native species of timberline (Rawal and Pangtey, 1993), and have a complex, spatial habitat and reservoir of large number of medicinal and aromatic plants and wild edibles. During recent past, timberline, the most prominent ecological boundary in the Himalaya where the sub-alpine forests terminates, has been identified as sensitive zone to environmental change and could be effectively modeled / monitored for future climate change processes. The species from tree-line have a narrow range of distribution, as temperature optima for most of these species is higher than the temperature in their natural habitats, warming will be expected to promote their growth but they may be threatened if they fail to compete with the changing climatic conditions (Saxena et al., 2004). Due to the over exploitation and changing global climatic condition many of the medicinal and aromatic plants in and around the timberline shrunk in size and distribution from their natural habitats and some of them are listed rare, threatened and endangered. Besides, the herbs some tree species of the timberline across the western Himalaya viz. Taxus baccata, Betula utilis etc. are also facing sever threats of depletion (Purohit, 2003). Most of the species valued by local communities have a poor soil seed bank, there could be large-scale local extinction of these species if seed production on a landscape scale decline (Saxena et al., 2004). Swan (1967) identified two parts of the alpine region i.e. above timberline (Lower alpine zone; 300 -4000 masl) and higher alpine zone (4000 masl snowline). Grasses and sedges are dominating members of alpine vegetation at lower altitude but they are characteristically replaced by non- grassy dwarf plant species at higher altitude near snowline. The area immediate above timberline and zone of stunted trees shrubs marks the alpine scrub. The vegetation of the lower alpine zone consists of dwarf shrubs, cushionoid herbs, grasses and sedges, Salix, Rosa, Lonicera, Ribes, Cotoneaster and Berberis etc. form the major shrub species at lower alpine zone (Kala et. al., 1998). The herbaceous flora of this zone represent spectacular array of multicolored flowers and include many short period growing cycle plant species. The major herbs of this zone are Potentilla, Geranium, Fritillaria, Lilium, Corydalis, Cyananthus, Anemone, Ranunculus, and Impatiens etc. The vegetation of the higher alpine zone is rather sparse, dotted with moraines, boulders and rocky slopes forming suitable habitat for the patches of shrubs e.g. Rhododendron lepidotum, Juniperus spp. Betula utilis and many species of colourful flowering plants, grasses and sedge etc. In the alpine with the onset of summer, the physical condition of the every patches of ground undergoes constant change, this is the root cause for the instability and succession of plants. Another feature of alpine plant distribution is that in the same habitat one could see the growth of several related or unrelated species and only one species dominate in the entire habitat almost to the exclusion of the other species. This difference may be due to the Physico- chemical properties of the soil. Initiation of growing season depends on the intensity of snowfall in the proceeding season and start of the melting of snow during spring (April May). In alpine region flowering is started during the month of May in some species, but in most of the species flowering occurs during June to late July and it goes up to early August (Nautiyal et al., 2001). Jennifer A. Dunne et al. (2003) reported that in experimental condition, increasing 2Â °C average soil temperature during the growing season for every two weeks of earlier snowmelt flowering time is advanced by 11 day in the sub-alpine region. Senescence at community level was gradually starts from July to September depending on the growth cycle of the plant species in Central Himalaya (Nautiyal et al., 2001). However in a study conducted by Zhang and Welker (1996) in Tibetan Tundra alpine the community senescence, which actually starts in September was postponed until October under warmer condition and stimulates the growth of grasses. It indicates that the warmer condition as result of increase CO2 enrichment extend the growing period and increase in the grass productivity and dis tribution may suppress the growth of forbs, shrubs (Zhang and Welker, 1996), similarly the valuable medicinal plants also affected (Ramakrishnan et al., 2003). It is possible that timber productivity in the high altitudes/ longitudes could increase as result of climate change, but it could take decades to occur and the newly form forests habitats are likely to retain lower level of native biodiversity due to loss of species that are unable to cope and some species will become more abundant and widely distributed (Alward et. al., 1999) Biotic invasion is another important cause of change in the geographical distribution of the plant species, which is derived or accelerated by the global change. Elevated CO2 might enhance the long-term success and dominance of exotic grasses and their shift in species composition mainly driven by global change has potential to accelerate fire cycle and may reduce biodiversity (Smith et al, 2000). The water use efficiency due to increase atmospheric CO2 can allow increase in potential distribution of Acacia nilotica spp. indica in Australia and increase temperature favour its reproductive life cycle (Kriticos et al, 2003). As the glaciers are receding at a fast rate the newly formed moraine belt is an excellent area to study the invasion of plants from the adjacent mountains and pastures.In recent several land uses and land covers of the high altitude is eroded due to the glacier melting, avalanches and land slides, which favour to extend the distribution of Polygonum polystachyum, a fast growing herb, is mostly found on freshly eroded slopes, past camping sites, river banks and avalanche tracks (Kala et. al., 1998). The other successful invaders found in these habitats are species of Lonicera and Berberis followed by Rosa and Ephedra. Increase temperature may results higher pathogen survival rate and most of the plant species will be severely threatened due to insect, pest and fungal disease. To the changing climate, plants can respond following possible ways firstly no change in their species composition but change in productivity and biogeochemical cycle. Secondly, evolutionary adaptation to the new climatic condition either through plasticity (i.e. shift in phenology) or through genetic response. Followed by emigration to the new areas, as warming observed in the alpine has been associated with upward movement of some plant taxa by 1-4 meter per decade on mountain tops and loss of some taxa that formally were restricted to higher altitude (Grabherr et.al., 1994). Ultimately, they may undergo extinction (Bawa and Dayanandan 1998, Ramakrishnan et al.2003). Most of the plant species changes over time through the process of succession, with pioneer species preparing the way for others, identifying the species present, the physical forms plant takes and the area they occupied are the way for observing change. All the changes involve dynamic and that are difficult or impossi ble to predict, natural ecosystems in this regard serve as a kind of natural laboratory, where natural mechanisms of change such as change in climatic condition and change in the feature of physical and biological systems observe practically. Appropriate management strategies need to developed in such a way that it may have to find a new balance between traditional conservation and maintenance of biodiversity and other ecosystem functioning. Effect on the vegetation: Upward movement of the vegetation belt. It result change in the pattern of structure and distribution of many valuable plant species, Reduction in the area of severely sensitive ecosystem like high altitude pastures, snow cover peaks and important glaciers. Changes in the phenology of some plant species, which include change in time of flowering and seed formation. Changes in the habitat, which is favourable for new alien weedy and invasive species. Increases fire risk in the sub-temperate and temperate dry deciduous and pine forests. Increases productivity of some grass species from the high altitude regions. Adverse impact on the timber production of forest. Effect on the agro-system: Changes the pattern and time of cropping. Shortening the maturity period of some winter crops, which are traditionally important constituent of mountain agriculture. Increase in the pathogen survival rate and crops are more susceptible to pest, insect and fungal diseases. Decline in the yield productivity of some traditional crops; whereas increasing temperature may also be favour the productivity crops like wheat. Decline in the yield of some horticultural fruits which needs chilling effect for their fruit development as seen in case of Apple fruit production. Uncertain high precipitation leads to destruction of crop productivity during flowering, seed formation and maturation time. Effect on Physical system: Accelerate intensity of glacier melting. Reduces area under snow cover and changes the time of snowmelt and snowfall at high-elevated ecosystems. Adverse impact on the seasonal runoff, freshwater availability. Increases the incident of landslides in mountains, drought condition and sever flood condition at lowland regions. Soil properties and process like organic matter decomposition, leaching and soil-water relation were influenced by increase temperature. Socio-economic conditions of the humankind severely affected: Reduction in the area of pasture adversely affect the local pastoral economy, as most of the local livestock of the transhumant and adjoining lowland peoples depends on the high altitude pastures in Garhwal in the summer season. Impact on the timber, medicinal plants and agriculture in the high altitude region in some extent gives negative results to the related industries. Economy through the hydropower generation is affected. Change in the social culture of the peoples living at high altitude regions, i.e. the time of the migration of the transhumant in Garhwal in recent affected due to the adverse climatic conditions. Which also affect their source of economy like agriculture, wool based occupation etc. Changes were also seen in the health conditions of the people living in high altitude, peoples of these regions now more worried about the heat stresses, vector borne diseases, respiratory, eye disorder etc. Status of many endangered wildlife fauna in the Himalayan region affected, and changes in the behavioural and seasonal migration of the animal species can be possible. Table: Distribution of some major plant species at different altitudinal belt of Garhwal Himalaya. Altitude (m asl) Plant species 500- 1400 Shrubs: Zizyphus xylopyrus, Woodfordia fructicosa, Trees: Rhododendron arboreum, Shorea robusta, Dalbergia sisso, Acacia catechu, Adina cardifolia, Terminalia, Cassia fistula, Mallotus philippensis, Bombax ceiba.Agele, 1500-2400 Herbs: Clematis montana, Anemone rivularis, A. obturiloba, Ranunculus hirtellus, Thalictrum chelidonii,Barbarea vulgaris, Silene indica, Malvia verticillata, Geraanium nepalense, Fragaria indica, Potentilla fulgens Epilobium pulustre,Bupleurum falcatum, Aster peduncularis, A. thomsonii, , Gentiana aprica etc. Shrubs: Prunus cornuta, Rosa macrophylla, Zizyphus xylopyrus, Woodfordia fructicosa Trees: Rhododendron arboreum, Shorea robusta, Dalbergia sisso, Acacia catechu, Pinus roxburghii,P. wallichiana, Quercus leucotricophora, Q. semecarpifolia, Adina cardifolia, 2500- 3400 Herbs: Anemone rivularis, A. obturiloba, Ranunculus hirtellus, Thalictrum chelidonii, T. minus, T. elegans, Aquilegiaa pubiflora, Caltha palustris Clematis montana, Clematis barbellata, Delphinium vestitum, Podophyllum hexandrum, Corydalis cornuta, Arabis nova, Viola canescens, Silene edgeworthii, S. Indica, Stellaria monosperma, Geranium collinum, G. himalayense, Trigonella emodi, Geum roylei, Potentilla fruticosa, P. fulgens, P. gelida, P. leuconota, P. polyphylla etc. Grasse Sedge: Carex cruciata, Agrostis pilosula,Poa supina, P. alpina, Danthonia. Shrubs: Cotoneaster macrophylla, Cotoneaster acuminatus, Lonicera, Salix, Rubus foliolosus, Spiraea bella, Berberis glaucocarpa, Myricaria bracteata, Skimmia laaureola, Astragallus candolleanus, Rosa macrophylla. Ribes himalense, Trees: Betula utilis, Taxus baccata, Rhododendron campanulatum, Alnus nitida, A. nepalensis, Abies pindrow, Cedrus deodara, Pinus wallichiana, Acer ceasium, Junipers 3500-4400 Herbs: Cypridium elegans*, C. himalaicum, Epipogium aphyllum, Dactylorrhiza hatagirea, Listera tenuis, Neottianthe secundiflora, Aconitum balfouri, A. falconeri, A. heterophyllum, A. violaceum, Ranunculus pulchellus, Thalictrum alpinum, Podophyllum hexandrum, Acer caesium*, Meconopsis aculeate, Corydalis sikkimensis, Megacarpaea polyandra, Astragallus himalayanus, Nardostachys graandiflora*, Picrorhiza kurrooa*, Pleurospermum angelicoides, Saussurea costus*, S. obvallata, Angelica glauca, Ribes griffithii, Lonicera asperifolia, Waldhemia tomentosa, Primula glomerata, Arnebia benthamii, Geranium pratense, Impatiens thomsonii, I. racemosa, Dioscorea deltoidea*, Allium humile, A. stracheyi*, A. wallichi, Clintonia udensis, Thamnocalamus falconeri, Orobanche alba, Sedum ewersii, S. heterodontum,Pimpnella diversifolia, Morina longifolia Grasse Sedge: Elymus thomsonii, Agrostis munroana, Calamagrostis emodensis, Danthonia cachemyriana, Festuca polycolea, Poa pagophila, Stipa roylei, Carex infuscate, C. nivalis, Kobresia royleana, K. duthei etc. Shrubs: Cotoneaster duthiana, Cotoneaster acuminatus Hippophae tibetana, Rosa sericea, Sorbus macrophylla, S. ursine, Rhododendron anthopogon, Trees: Sorbus aucuparia, Cedrus deodara, Betulla utilis, 4500- above Herbs: Oxygraphis glacialis, Ranunculus pulchellus,Corydalis bowerii, Alyssum canescens,Draba altaica, Silene gonosperma, Potentilla sericea, Sedum bouverii, Saussurea obvallata, S. simpsoniana, Christolea himalayensis Literature cited Rau, M. A. (1975). High altitude flowering plants of west Himalaya. BSI, Howrah, India, pp.214. Singh, D. K. and Hajra, P. K., in Changing Perspectives of Biodiversity Status in the Himalaya (eds Gujral, G. S. and Sharma, V.), British Council Division, British High Commission, Publ. Wildlife Youth Services, New Delhi, 1996, pp. 23-38. Dunne, J.A., Harte, J. and Taylor, K. (2003). Sub alpine Meadow Flowering Phenology Responses To Climate Change: Integrating Experimental And Gradient Methods, Ecological Monographs 73 (1), pp. 69-86. IPCC (2001). Climate Change-2001: Impacts, Adaptation and Vulnerability, contribution of Working Group II to the Third Assessment Report of the Intergovernmental Panel on Climate Change. Kriticos, D.J., Sutherst, R.W., Brown, J.K., Adkings, S.W. and Maywald, G.F. (2003) Climate Change and The Potential Distribution of an Invasive Alien Plant: Acacia nilotica ssp.indica in Australia, Journal of Applied Ecology, 40; 111-124. Nautiyal, B.P., Prakash, V and Nautiyal, M.C. (2000). Structure And Diversity Pattern Along An Altitudinal Gradient In An Alpine Meadow Of Madhyamaheshwer, Garhwal Himalaya, India. Indian Journal of Environmental Science 4(I). 39- 48. Nautiyal, M.C., Nautiyal, B.P. and Prakash, V. (2001). Phenology And Growth Form Distribution In An Alpine Pasture At Tungnath, Garhwal Himalaya. Mountain Research and Development, Vol. 21, No. 2, 177-183. Price, M.V. and Waser, N.M. (2000). Responses of sub alpine meadow vegetation to four year of experimental warming. Ecological Applicati Alpine Plant Biodiversity in the Central Himalayas Alpine Plant Biodiversity in the Central Himalayas Alpine Plant Biodiversity in the Central Himalayan Region: Perspective of Global Climate Change Summary Increase in surface temperature at global scale has already affected a diverse set of physical and biological systems in many parts of the world and if it increases at this rapid rate then the condition would be worst one could have ever thought off. Garhwal Himalaya, major part of the great Himalayan mountainous system is also much sensitive and vulnerable to the local, regional and global changing climate. Due to strong altitudinal gradient, varied climatic conditions and diverse set of floral and faunal composition, the impact of climate change seems to be much higher. This paper highlights some important features of the changing pattern of vegetational composition, distribution and impact of climate change on the phenological aspect of major alpine plant species present in the Garhwal Himalayan region. It also shows cumulative changes, which operate at local level but are globally pervasive. These cumulative changes include change in the land cover/ land use and other anthropogen ic activities, which are related to the climate change. Overall biodiversity in the Himalayan region has been depleted as the consequences of complex and multitude pressure of climate change. The depleted biodiversity has indirectly affected the socio-economic development of the local communities on which their sustenance depends and is inherently critical to the consideration and management of natural resource. Introduction Plant diversity and Status The varied altitudinal, climatic and topographical conditions in the Himalaya results in different types of microhabitats. Geographic isolation, glaciations, evolution and migration of the species in the past all together have contributed to the high level of biodiversity in this mountain system. As per genetic, species and ecosystem level resources, Himalaya is one of the hotspots of biodiversity in the world, which represents about one-tenth of the worlds known species of high altitude plant and animal species. Some parts in the Himalayan region are center for origin of many crops and fruit species and are important source of gene for their wild relatives. The floral diversity of this region shows assemblage of many endemic and exotic species of plants from the adjoining regions. A large number of western Himalayan flora in the Garhwal Kumaon region seems to have been invaded from Tibet, western China and adjoining north-east Asia (Rau, 1975). In the present scenario biodiversity seems to have been depleted in these regions due to land degradation, habitat fragmentation, increasing population pressure, over exploitation of bio-resources and finally due to the changing pattern of the climate. Nearly 10% of flowering plants are listed under various categories of threatened species. Red Data Book of Indian plants listed about 620 threatened species, of which, 28 are presumed extinct, 124 endangered, 81 vulnerable, 160 rare and 34 insufficiently known (Nayar and Sastry, 1987, 1988), however, Red list of threatened plants indicates 19 species as extinct. Among others, 1236 species are listed as threatened, of which, 41 taxa are possibly extinct, 152 endangered, 102 vulnerable, 251 rare and 690 of indeterminate status (IUCN, 1997). From the Himalayan region the important plant species included in threatened categories are mostly the valuable medicinal and aromatic plants, which, support the economic condition and health care sys tem of the local communities. It is well known that, in the context of the present scenario of climate change especially due to global warming many of the high-elevated ecosystems are severely sensitive and vulnerable. Their fragility may accelerate the changes occurring in their composition and structure to the slight variations in climatic factors. These regions include glacier, alpine pasture/ meadows and timber line ecosystem, which are the important source of the seasonal runoff, freshwater, valuable medicinal and aromatic plants, grazing land, source of timber and wild edibles for the mankind. Future scenario of climate change: According to the Third Assessment Report of Intergovernmental Panel on Climate Change (IPCC) 2001, average global temperature close to the earths surface has increased by 0.6 Â °C Â ± 0.2Â ° C since 19th century mainly due to the emission of CO2. If human beings do not act to reduce the present level of CO2 there will be additional increment in temperature of 1.4Â ° C to 5.8Â ° C in the next 40 100 year. Current information available on the pattern of future climate change through General Circulation Models (GCMs) suggested that the annual mean warming would increase about 3Â °C in the decade of 2050s and about 5Â °C in decade of the 2080s over the land region of Asia. Precipitation would increase annually about 7% and 11% in decades of 2050s and 2080s respectively. There would be a decline in the summer precipitation that seems likely to be over the central part of arid and semi-arid Asia. GCM also showed high uncertainty in future projection of winter and summer precipitati on over south Asia, because much of tropical Asian climate is noticeably associated with the annual monsoon cycle. In Central Himalayan region, through the assessment of people perception it is interpreted that, climate change resulted in the increase in warming, decline in rainfall during March- May, high rainfall during Aug- Sept instead of normal peak in July- Aug, decline in the snowfall intensity and winter precipitation in Jan-Feb instead of Dec-Jan (Saxena et al., 2004). This scenario can hardly trigger to think about the changing pattern of climate or its negative and positive impacts at local, regional and global level. Although assessment of future climate change scenario through some of scientific models needs a better infrastructure and high technological inputs, specific impact of climate change on different ecosystems can be discerned by comprehensive studies on long term monitoring of the different aspects of ecosystem which is lacking in the Indian context especially in the Garhwal Himalayan region due to poor infrastructure and management practices. So, as per as need concern in these remote areas the assessment of impact on the natural resources in future climate changes can be done through the site-specific sensitivity analysis and it can be related to the traditional knowledges of the peoples living in this particular region of the Himalaya. Sensitivity analysis would help to assess what will be happen if various climatic variables changed, and analysis also evaluates the positive or negative impacts of changing climate on the natural resources. This assessment would help us to make the l ocal communities realize the importance of conservation and management practice so that the endangered and threatened species could be saved from becoming extinct. Assessment of vulnerability and adaptive capacity of the various ecosystems and to develop indigenous knowledge based coping mechanism are important to determine the impact of climate change. This also links the ecological processes to the social processes and appreciates the relationship between the biodiversity and ecosystem functioning. Climate change: Impact on different vegetation zone Natural ecosystems at high elevations are much more sensitive to the climatic variations (Ramakrishnan et al., 2003) or global warming then the managed systems. Their sensitivity is prominently attributed to their limited productivity during snow-free growing season (Price et al., 2000), low dispersal capability, geographically localized, genetically impoverished, highly specialized and slow reproducing ability of the high altitude plants (McNeely, 1990; WWF, 2003). As a consequence of global warming the present distribution of species in high altitude ecosystems projected to shift higher as results of upward altitudinal movement of the vegetation belts. Although the rate of vegetation change is expected to be slow and colonization success would depend on the ability of adaptation and interaction of the plant species with the climate and other associated species, weeds, exotic and invasive species. Their success also depends on their ecological niche width and their role in the ecosy stem functioning. Increase in the temperature would result competition between such species and new arrivals. As the result, species which have wide ecological tolerance have an advantage to adapt and those which are at the edge of range, genetically impoverished, poor dispersal ability and reproducer are under the threshold of extinction. A likely impact of climate change is also observed over the phenological aspect of vegetation in the alpine, sub alpine and timberline zone. Changes in the pattern of snowfall and snowmelt in these mountain regions and increase in mean annual surface temperature has pronounce impact on the date and time of the flowering and other phenophases of certain valuable, keystone species of plants. Earlier snowmelt simulate early flowering in some early growing plants and possibly increase in surface temperature may extend the growing period and productivity of certain grass species in the cooler climatic region. There is a gradual decrease in the growing period from timberline to the snow line, Rawat and Pangtey, (1987) reported about 20 weeks growing period near timberline and barely 4-6 weeks above 5000 m asl. Thus, increase in the average temperature due to global warming the growing period of the vegetation would be seems to extend at high altitudes. Evidences of climate change through p eople perception in Garhwal Himalaya reveals that increase in the warming results decline in the yield of apple fruits and shortening the maturity period of winter crops, whereas, the production of cash crops like potato, peas and kidney beans under warm condition increases. Change in rainfall pattern, snowfall intensity will increase large-scale mortality and damage to the crops, which are close to the maturity on the other hand, Barley and wheat crop production is severely affected due to winter precipitation in months of Jan- Feb (Saxena et al., 2004). Vulnerability of different vegetation belts in the Garhwal Himalaya. Dominant tree species in the low and mid altitude zone have a wider range of distribution. Shorea robusta the climax species of lower elevation is distributed over moist to dry deciduous bio-climates in central India where temperature is much higher while rainfall is quite low. Quercus spp. the climax species at mid elevation is also distributed over a wide range (1100- 1800m) The mid altitude which is dominated by broad leaves and coniferous forest (Rao, 1994) mainly species of Quercus spp. and Pinus spp. on response to the warming may be replaced by the species like Shorea robusta and Terminalia spp. Warming also increases the chance of greater fire risk in dry or moist deciduous forests, these impacts on the forest can directly influence the local livelihood based on fuel and fodder (Ramakrishnan et al. 2003). Rhododendron arboreum is a very prominent forest species because of its red flowers covering almost the whole canopy. At higher elevations this species used to attain peak flowering stage in February / March but now due to warming flowering time in this species seems to shift in the months of January/February. The phenological calendar at lower altitude has thus shifted to the higher altitudes. Exact times of leaf fall, flushing, flowering and fruiting may vary depending upon the elevation indicating sensitivity of phenophases to temperature and moisture stress regime. Flowering and fruiting start earlier about a month with increase in elevation by 600 m (increase in temperature by 2.4 degree C) in Rhododendron arboreum, Prunus cerasoides, Myrica esculenta, Pyrus Pashia and Reinwardtia indica in Central Himalaya. Leafless period in deciduous species like Aesculus indica and Alnus nepalensis is longer at higher altitude as compared to lower altitude. At higher elevation (1500-3300m) i n Central Himalaya, evergreen and winter deciduous species occur equally across the elevation/temperature gradient. All across the elevation / temperature gradient, majority of tree species show vernal flowering. Species showing vernal flowering (before 15 June) increased in frequency and those with aestival flowering (between 15 June 15 September) decreased with increase in annual temperature drown based on the elevation gradient. Thus, change in the temperature would affect flowering and fruiting time of different species or also induce change in species composition. Vegetation of the timberline in different parts of world not only differs in terms of species composition but also exhibit different types of species (Crawford, 1989). In some regions the timberline represents exclusively evergreen conifers while in some it represents totally deciduous broad-leaved trees (Purohit, 2003). In the central Himalaya the Betula utilis, Abies pindrow and Rhododendron campanulatum, are the native species of timberline (Rawal and Pangtey, 1993), and have a complex, spatial habitat and reservoir of large number of medicinal and aromatic plants and wild edibles. During recent past, timberline, the most prominent ecological boundary in the Himalaya where the sub-alpine forests terminates, has been identified as sensitive zone to environmental change and could be effectively modeled / monitored for future climate change processes. The species from tree-line have a narrow range of distribution, as temperature optima for most of these species is higher than the temperature in their natural habitats, warming will be expected to promote their growth but they may be threatened if they fail to compete with the changing climatic conditions (Saxena et al., 2004). Due to the over exploitation and changing global climatic condition many of the medicinal and aromatic plants in and around the timberline shrunk in size and distribution from their natural habitats and some of them are listed rare, threatened and endangered. Besides, the herbs some tree species of the timberline across the western Himalaya viz. Taxus baccata, Betula utilis etc. are also facing sever threats of depletion (Purohit, 2003). Most of the species valued by local communities have a poor soil seed bank, there could be large-scale local extinction of these species if seed production on a landscape scale decline (Saxena et al., 2004). Swan (1967) identified two parts of the alpine region i.e. above timberline (Lower alpine zone; 300 -4000 masl) and higher alpine zone (4000 masl snowline). Grasses and sedges are dominating members of alpine vegetation at lower altitude but they are characteristically replaced by non- grassy dwarf plant species at higher altitude near snowline. The area immediate above timberline and zone of stunted trees shrubs marks the alpine scrub. The vegetation of the lower alpine zone consists of dwarf shrubs, cushionoid herbs, grasses and sedges, Salix, Rosa, Lonicera, Ribes, Cotoneaster and Berberis etc. form the major shrub species at lower alpine zone (Kala et. al., 1998). The herbaceous flora of this zone represent spectacular array of multicolored flowers and include many short period growing cycle plant species. The major herbs of this zone are Potentilla, Geranium, Fritillaria, Lilium, Corydalis, Cyananthus, Anemone, Ranunculus, and Impatiens etc. The vegetation of the higher alpine zone is rather sparse, dotted with moraines, boulders and rocky slopes forming suitable habitat for the patches of shrubs e.g. Rhododendron lepidotum, Juniperus spp. Betula utilis and many species of colourful flowering plants, grasses and sedge etc. In the alpine with the onset of summer, the physical condition of the every patches of ground undergoes constant change, this is the root cause for the instability and succession of plants. Another feature of alpine plant distribution is that in the same habitat one could see the growth of several related or unrelated species and only one species dominate in the entire habitat almost to the exclusion of the other species. This difference may be due to the Physico- chemical properties of the soil. Initiation of growing season depends on the intensity of snowfall in the proceeding season and start of the melting of snow during spring (April May). In alpine region flowering is started during the month of May in some species, but in most of the species flowering occurs during June to late July and it goes up to early August (Nautiyal et al., 2001). Jennifer A. Dunne et al. (2003) reported that in experimental condition, increasing 2Â °C average soil temperature during the growing season for every two weeks of earlier snowmelt flowering time is advanced by 11 day in the sub-alpine region. Senescence at community level was gradually starts from July to September depending on the growth cycle of the plant species in Central Himalaya (Nautiyal et al., 2001). However in a study conducted by Zhang and Welker (1996) in Tibetan Tundra alpine the community senescence, which actually starts in September was postponed until October under warmer condition and stimulates the growth of grasses. It indicates that the warmer condition as result of increase CO2 enrichment extend the growing period and increase in the grass productivity and dis tribution may suppress the growth of forbs, shrubs (Zhang and Welker, 1996), similarly the valuable medicinal plants also affected (Ramakrishnan et al., 2003). It is possible that timber productivity in the high altitudes/ longitudes could increase as result of climate change, but it could take decades to occur and the newly form forests habitats are likely to retain lower level of native biodiversity due to loss of species that are unable to cope and some species will become more abundant and widely distributed (Alward et. al., 1999) Biotic invasion is another important cause of change in the geographical distribution of the plant species, which is derived or accelerated by the global change. Elevated CO2 might enhance the long-term success and dominance of exotic grasses and their shift in species composition mainly driven by global change has potential to accelerate fire cycle and may reduce biodiversity (Smith et al, 2000). The water use efficiency due to increase atmospheric CO2 can allow increase in potential distribution of Acacia nilotica spp. indica in Australia and increase temperature favour its reproductive life cycle (Kriticos et al, 2003). As the glaciers are receding at a fast rate the newly formed moraine belt is an excellent area to study the invasion of plants from the adjacent mountains and pastures.In recent several land uses and land covers of the high altitude is eroded due to the glacier melting, avalanches and land slides, which favour to extend the distribution of Polygonum polystachyum, a fast growing herb, is mostly found on freshly eroded slopes, past camping sites, river banks and avalanche tracks (Kala et. al., 1998). The other successful invaders found in these habitats are species of Lonicera and Berberis followed by Rosa and Ephedra. Increase temperature may results higher pathogen survival rate and most of the plant species will be severely threatened due to insect, pest and fungal disease. To the changing climate, plants can respond following possible ways firstly no change in their species composition but change in productivity and biogeochemical cycle. Secondly, evolutionary adaptation to the new climatic condition either through plasticity (i.e. shift in phenology) or through genetic response. Followed by emigration to the new areas, as warming observed in the alpine has been associated with upward movement of some plant taxa by 1-4 meter per decade on mountain tops and loss of some taxa that formally were restricted to higher altitude (Grabherr et.al., 1994). Ultimately, they may undergo extinction (Bawa and Dayanandan 1998, Ramakrishnan et al.2003). Most of the plant species changes over time through the process of succession, with pioneer species preparing the way for others, identifying the species present, the physical forms plant takes and the area they occupied are the way for observing change. All the changes involve dynamic and that are difficult or impossi ble to predict, natural ecosystems in this regard serve as a kind of natural laboratory, where natural mechanisms of change such as change in climatic condition and change in the feature of physical and biological systems observe practically. Appropriate management strategies need to developed in such a way that it may have to find a new balance between traditional conservation and maintenance of biodiversity and other ecosystem functioning. Effect on the vegetation: Upward movement of the vegetation belt. It result change in the pattern of structure and distribution of many valuable plant species, Reduction in the area of severely sensitive ecosystem like high altitude pastures, snow cover peaks and important glaciers. Changes in the phenology of some plant species, which include change in time of flowering and seed formation. Changes in the habitat, which is favourable for new alien weedy and invasive species. Increases fire risk in the sub-temperate and temperate dry deciduous and pine forests. Increases productivity of some grass species from the high altitude regions. Adverse impact on the timber production of forest. Effect on the agro-system: Changes the pattern and time of cropping. Shortening the maturity period of some winter crops, which are traditionally important constituent of mountain agriculture. Increase in the pathogen survival rate and crops are more susceptible to pest, insect and fungal diseases. Decline in the yield productivity of some traditional crops; whereas increasing temperature may also be favour the productivity crops like wheat. Decline in the yield of some horticultural fruits which needs chilling effect for their fruit development as seen in case of Apple fruit production. Uncertain high precipitation leads to destruction of crop productivity during flowering, seed formation and maturation time. Effect on Physical system: Accelerate intensity of glacier melting. Reduces area under snow cover and changes the time of snowmelt and snowfall at high-elevated ecosystems. Adverse impact on the seasonal runoff, freshwater availability. Increases the incident of landslides in mountains, drought condition and sever flood condition at lowland regions. Soil properties and process like organic matter decomposition, leaching and soil-water relation were influenced by increase temperature. Socio-economic conditions of the humankind severely affected: Reduction in the area of pasture adversely affect the local pastoral economy, as most of the local livestock of the transhumant and adjoining lowland peoples depends on the high altitude pastures in Garhwal in the summer season. Impact on the timber, medicinal plants and agriculture in the high altitude region in some extent gives negative results to the related industries. Economy through the hydropower generation is affected. Change in the social culture of the peoples living at high altitude regions, i.e. the time of the migration of the transhumant in Garhwal in recent affected due to the adverse climatic conditions. Which also affect their source of economy like agriculture, wool based occupation etc. Changes were also seen in the health conditions of the people living in high altitude, peoples of these regions now more worried about the heat stresses, vector borne diseases, respiratory, eye disorder etc. Status of many endangered wildlife fauna in the Himalayan region affected, and changes in the behavioural and seasonal migration of the animal species can be possible. Table: Distribution of some major plant species at different altitudinal belt of Garhwal Himalaya. Altitude (m asl) Plant species 500- 1400 Shrubs: Zizyphus xylopyrus, Woodfordia fructicosa, Trees: Rhododendron arboreum, Shorea robusta, Dalbergia sisso, Acacia catechu, Adina cardifolia, Terminalia, Cassia fistula, Mallotus philippensis, Bombax ceiba.Agele, 1500-2400 Herbs: Clematis montana, Anemone rivularis, A. obturiloba, Ranunculus hirtellus, Thalictrum chelidonii,Barbarea vulgaris, Silene indica, Malvia verticillata, Geraanium nepalense, Fragaria indica, Potentilla fulgens Epilobium pulustre,Bupleurum falcatum, Aster peduncularis, A. thomsonii, , Gentiana aprica etc. Shrubs: Prunus cornuta, Rosa macrophylla, Zizyphus xylopyrus, Woodfordia fructicosa Trees: Rhododendron arboreum, Shorea robusta, Dalbergia sisso, Acacia catechu, Pinus roxburghii,P. wallichiana, Quercus leucotricophora, Q. semecarpifolia, Adina cardifolia, 2500- 3400 Herbs: Anemone rivularis, A. obturiloba, Ranunculus hirtellus, Thalictrum chelidonii, T. minus, T. elegans, Aquilegiaa pubiflora, Caltha palustris Clematis montana, Clematis barbellata, Delphinium vestitum, Podophyllum hexandrum, Corydalis cornuta, Arabis nova, Viola canescens, Silene edgeworthii, S. Indica, Stellaria monosperma, Geranium collinum, G. himalayense, Trigonella emodi, Geum roylei, Potentilla fruticosa, P. fulgens, P. gelida, P. leuconota, P. polyphylla etc. Grasse Sedge: Carex cruciata, Agrostis pilosula,Poa supina, P. alpina, Danthonia. Shrubs: Cotoneaster macrophylla, Cotoneaster acuminatus, Lonicera, Salix, Rubus foliolosus, Spiraea bella, Berberis glaucocarpa, Myricaria bracteata, Skimmia laaureola, Astragallus candolleanus, Rosa macrophylla. Ribes himalense, Trees: Betula utilis, Taxus baccata, Rhododendron campanulatum, Alnus nitida, A. nepalensis, Abies pindrow, Cedrus deodara, Pinus wallichiana, Acer ceasium, Junipers 3500-4400 Herbs: Cypridium elegans*, C. himalaicum, Epipogium aphyllum, Dactylorrhiza hatagirea, Listera tenuis, Neottianthe secundiflora, Aconitum balfouri, A. falconeri, A. heterophyllum, A. violaceum, Ranunculus pulchellus, Thalictrum alpinum, Podophyllum hexandrum, Acer caesium*, Meconopsis aculeate, Corydalis sikkimensis, Megacarpaea polyandra, Astragallus himalayanus, Nardostachys graandiflora*, Picrorhiza kurrooa*, Pleurospermum angelicoides, Saussurea costus*, S. obvallata, Angelica glauca, Ribes griffithii, Lonicera asperifolia, Waldhemia tomentosa, Primula glomerata, Arnebia benthamii, Geranium pratense, Impatiens thomsonii, I. racemosa, Dioscorea deltoidea*, Allium humile, A. stracheyi*, A. wallichi, Clintonia udensis, Thamnocalamus falconeri, Orobanche alba, Sedum ewersii, S. heterodontum,Pimpnella diversifolia, Morina longifolia Grasse Sedge: Elymus thomsonii, Agrostis munroana, Calamagrostis emodensis, Danthonia cachemyriana, Festuca polycolea, Poa pagophila, Stipa roylei, Carex infuscate, C. nivalis, Kobresia royleana, K. duthei etc. Shrubs: Cotoneaster duthiana, Cotoneaster acuminatus Hippophae tibetana, Rosa sericea, Sorbus macrophylla, S. ursine, Rhododendron anthopogon, Trees: Sorbus aucuparia, Cedrus deodara, Betulla utilis, 4500- above Herbs: Oxygraphis glacialis, Ranunculus pulchellus,Corydalis bowerii, Alyssum canescens,Draba altaica, Silene gonosperma, Potentilla sericea, Sedum bouverii, Saussurea obvallata, S. simpsoniana, Christolea himalayensis Literature cited Rau, M. A. (1975). High altitude flowering plants of west Himalaya. BSI, Howrah, India, pp.214. Singh, D. K. and Hajra, P. K., in Changing Perspectives of Biodiversity Status in the Himalaya (eds Gujral, G. S. and Sharma, V.), British Council Division, British High Commission, Publ. Wildlife Youth Services, New Delhi, 1996, pp. 23-38. Dunne, J.A., Harte, J. and Taylor, K. (2003). Sub alpine Meadow Flowering Phenology Responses To Climate Change: Integrating Experimental And Gradient Methods, Ecological Monographs 73 (1), pp. 69-86. IPCC (2001). Climate Change-2001: Impacts, Adaptation and Vulnerability, contribution of Working Group II to the Third Assessment Report of the Intergovernmental Panel on Climate Change. Kriticos, D.J., Sutherst, R.W., Brown, J.K., Adkings, S.W. and Maywald, G.F. (2003) Climate Change and The Potential Distribution of an Invasive Alien Plant: Acacia nilotica ssp.indica in Australia, Journal of Applied Ecology, 40; 111-124. Nautiyal, B.P., Prakash, V and Nautiyal, M.C. (2000). Structure And Diversity Pattern Along An Altitudinal Gradient In An Alpine Meadow Of Madhyamaheshwer, Garhwal Himalaya, India. Indian Journal of Environmental Science 4(I). 39- 48. Nautiyal, M.C., Nautiyal, B.P. and Prakash, V. (2001). Phenology And Growth Form Distribution In An Alpine Pasture At Tungnath, Garhwal Himalaya. Mountain Research and Development, Vol. 21, No. 2, 177-183. Price, M.V. and Waser, N.M. (2000). Responses of sub alpine meadow vegetation to four year of experimental warming. Ecological Applicati

Saturday, January 18, 2020

Primate Observation Essay

Primates are some of the most interesting animals to watch and learn about whether it be in person at a zoo or seeing a film or documentary on wild ones in a natural environment. Part of this reason is due to the incredible amount of similarities found in between primates and humans. After observing two different primate species at a local zoo, I found out that by observing their behavior, we gain a small insight into human behaviors and their roots. Today I will discuss the different types of behavior I observed as well as the effects of being in captivity and how this helps us understand hunan behavior. On sunny April 19th this year, I visited the San Francisco Zoo and the first species I observed were the gorillas, also known as Gorilla Beringei. Upon approaching the gorilla habitat, at about 1:30 p.m., I noticed the enclosure was roughly about fifty yards in diameter. Throughout the enclosure, there were different levels of ground elevation varying from small hills, to large rock structures placed about twenty feet away from the gorilla cages inside the habitat. There were also many plant or bush like shrubs around as well as trees varying from shape and size throughout the enclosure. The overall shape of the enclosure was similar to an octagon which supported different observational vantage points from a few different sides. The gorillas are the largest primates still existing today. The gorillas in the enclosure varied in size and appearances. All the females were much smaller then the male silverback, however within the female group, their sizes also varied. Some females within the group were less massive and more lengthy then for example the female in charge of the newborn gorilla. The â€Å"mother† of the baby gorilla, Kabibe, was much larger then the other females and she seemed to have more authority within the social group. The male silverback, Oscar Jones, was impressively larger then any other gorillas in the enclosure and had a much larger head and arms in comparison. He had long thick black hair with a patch of silver on his back symbolizing maturity. In total, I observed about six to eight gorillas out of the cages and interacting within the enclosure. The second species I  observed around 3:40 pm were the siamangs, or symphalangus syndactylus. Their enclosure was much different then the previously observed gorillas enclosure. This one was about fifty feet high, 30 feet long, and 20 feet wide and in the shape of the letter â€Å"L†. It’s made of reinforced glass from the bottom to about 10 feet high, then becomes a chain linked metal cage the rest of the way up. The structure contained many different objects from which the siamangs were able to use to climb up or down. Some of these objects included, climbing logs, swings, many thick pieces of rope, cylindrical shaped rubber tubes, planks of wood, and many other suspended objects. Towards the bottom of the enclosure, there were also a lot of plant life and bushes or flower like things where the siamangs could sit or interact with one another when not climbing around. Within the enclosure, there were two siamangs. Although not labeled, since siamangs are monogamous primates, I assume one was male and one was female. Physically, the siamangs are just a bit larger then the other gibbons however still small in comparison to the apes. They have no tails, are slender and long armed as they are arboreal lesser apes. They are covered with long dense black hair and have long hooked nails. Siamangs are also known to have large throat sacs which they can use to let out a very loud call to warn against predators. However, neither of these siamangs had the adaptive throat sacs. Also, there was not much difference in size between the male and female gender. After observing the two primate species and reviewing my field notes, I noticed the two species although both part of the ape family, are not that similar in fact. For example, the gorillas social organization consists of a one male, multi female group with the male being the alpha leader. He ensures that it is his genetics being passed on to the offspring and that is the only way he will protect and partake in the baby’s life. Due to being a one male, multi female group, it is not uncommon for gorilla males to kill any infant they assume is not theirs. There also seemed to be a sense of hierarchy amongst the females themselves, with Kabibe’s mother, at the top of the female group. However, the male silver back Oscar Jones, was still maintaing authority amongst the entire group by charging the females. On the other hand, the siamangs are a pair bonded group whom select mates for life and have a family. In the enclosure I observed, there were only two siamangs present who behaved very differently from one another. One siamang continued to be very active, swinging throughout the cage and constantly climbing up and down the metal fence. However, the other siamang, which I believed to be female, sat on a small rock towards the bottom corner of the enclosure and did not interact with any bystanders or the other siamang at all. Also, my friend and I noticed this sitting siamang also seemed to appear as if it were depressed. Many times the active siamang would swing down and try and interact with his partner and the other siamang would just ignore him and continue staring down or out the glass. One of the gorillas I was observing displayed a way of acquiring food which I thought was quite intelligent. She grabbed a thin leaf filled branch from a tree and placed her hand at the top of the branch. Starting from the top she pulled her hand down towards the other end pulling any leaves out together instead of one by one. She then disposed of the branch by throwing it a few feet away from her. This showe d a level of intelligence I have not seen in other primates. The gorillas mainly stick to eating leaves and vegetation found in their enclosure from many trees and plants around. This similar to their natural habitat, does not offer them lots of nutritional value, however is available in large quantities and available year round. I am also assuming they are fed fruits by zoo employees as well for nutritional quality and value. The three females outside in the enclosure seemed to be isolated about 20 feet away from each other and spread around the enclosure. They did not seem to be sharing any source of food or interact much with one another unless they were nearing the cage door within the enclosure. The siamangs did not seem to display any signs of higher intelligence. One continued to constantly move around the cage by climbing up then swinging back down. The other siamang just sat in isolation and was not physically active much at all. They did not share anything amongst themselves and did not interact much either. The two primate species I observed did not have much in common, except for their diet. Both the gorillas and the siamangs are both primarily vegetarians and consume different types of leaves, fruits, and other plants found in their habitats. I was not able to observe how the siamangs acquired their food or how they react to â€Å"meal time†, however based on my observations I assume the siamangs would not share much either due to their lack of interaction with one another. This throws me off because according to what I have learned in class, the siamangs are in fact mates with one  another for life and yet they did not interact with one another at all durin g my observations at the zoo. I believe these similarities in diet exist because that the siamangs and gorillas are part of the ape family. However, the differences in behavior, mating, social organization, and intelligence also exist due to the fact that they are separated between the â€Å"lesser apes† (siamangs), and the â€Å"great apes† (gorillas). Another reason why these differences might exist is due to where the species originated from. Gorillas originally were from Africa while Gibbons were found from Southeast Asia. Overall after reviewing my notes, I noticed that the Siamangs are much less intelligent then the gorillas, yet more active. I believe this is because the siamangs are much smaller, requiring less energy to move about their enclosure in such a fast and excited manner. The gorillas on the other hand are much more complex in behavior as they actually interact with one another by expressing sounds and or physical actions. They also seem to be aware the fact that many people are around them watching, and they also react to this by hiding back in the cages or moving away behind a tree or rock structure. I have always believed that being held captive in a zoo, is no where close to being free in your natural habitat. How can one take an animal who should have the ability to roam endless land and have the need to survive in the â€Å"natural† world and put them in a restricted enclosure, a fraction the s ize of their natural habitats and claim that these animals are happy there? I personally believe being in captivity and on display in a zoo has many negative effects on these animals. While observing the gorillas, they seemed to be heavily affected by their environment and surroundings. In a gorillas natural habitat, you would most likely find them playing with one another, acquiring food, and being active. However, most times in zoo’s you simply find the gorillas not really doing anything besides just sitting there. These are most likely due to psychological effects brought on by being captive and put on display to thousands of people all the time. While observing, I noticed the gorillas did not really do much besides move around to their own spot of the enclosure, about twenty feet away from one another, and just sit there and stare at the people watching them. Also, these gorillas suffer mental trauma from being teased or provoked to a level where they feel threatened by all these yelling kids and or adults. I do not believe the behaviors  exhibited by gorillas in captivity are â€Å"natural† due to the fact that gorillas are very intelligent. According to GorillasWorld.com, â€Å"As humans are watching them they will be watching as well. This is why they often pick up behaviors from people.† As a result, behaviors seen by gorillas in a zoo would not be the same behaviors shown by wild gorillas in natural environment. With thousands of people standing around the enclosure yelli ng and making gestures towards the gorilla, it is safe to say the gorillas observe the humans behavior and repeat behaviors they have learned. The siamangs I observed also display a bit of natural and unnatural behaviors as well. For example, siamangs are arboreal primates who live in tree top canopies and are rarely seen walking on the ground. They use their long limbs and fingers as hooks to swing from branch or vine to another and that is how they maneuver throughout the forests. One of the siamangs I was watching was very active and continued to swing back and forth throughout his enclosure almost the entire time I was watching. He would use logs and ropes to climb up to the top corner of the cage, then he would observe from up there for a few seconds. After, he would make his way back down towards the bottom of the enclosure and would leap around. This is natural behavior to be seen by a siamang even in the wild. However, the other siamang within the enclosure exhibited some worrying signs of unnatural behavior. This siamang was sitting on a rock of some sort around the enclosure floor and would stare down towards the ground or look out the glass. However, she would not move at all throughout my entire observation time and really seemed depressed. At one point, the other active siamang swung down and got very close to her and still she did not move or interact at all. Im assuming this is a psychological effect brought on by being trapped in such a small con tainment instead of being able to roam about the forest and be free. I believe that this specific siamang has been held in captivity for a while longer due to the behavior shown. Observing these primates in their natural wild environment would have significantly different behavior observations. Living in the wild, these primates experience struggles to survive such as finding sources of food, competition for mating, and also predators and dangers. These are not really things captive animals in zoos experience due to human intervention. For example in the wild, gorillas are moving to a new â€Å"camping ground† very often due to predators such as large cats and build a  sleeping nest to stay protected. This is natural adaptive behavior found in gorillas; however, you will not see this in captive gorillas because the only predators they experience are humans taunting or screaming at them and they do not have enough space available to travel distances. As a result of these observations, primates and other animals in captivity may not exhibit natural behaviors observed in their natural environment. After spending the day observing the behaviors of both the gorillas and the siamangs, I see some behavior patterns that I also see in humans. For example, the siamangs find mates for life and raise a family and that is their social group. This is basically most families around the world. Our social group normally consists of us with a single mate whom we raise children with. I believe the fact that we as humans ideally choose to settle down with a single partner and raise children has to do with our culture and not necessarily as an instinctual choice such as the siamangs. As humans most of us find it wrong to have more then one mate or parter and we call it â€Å"cheating.† However, based on my observations of the primates, it is a natural and instinctual decision to try and mate as much as possible to ensure your genetics being passed on and carried through the future since that is life’s main objective. Another example is the effects of captivity the depressed siamang suffered from. This is very common in humans as well to become anti social or depressed when placed in a small room such as a jail cell. Studying primates can help us understand more of where humans came from due to our recent shared common ancestor. We are able to see some behavior patterns from the primates found in humans as well, however there are many behavioral patterns in the primates which is uncommon for humans. For example, the gorillas tended to be in isolation and spread out throughout the enclosure for most of the time. Humans on the other hand, if having to live together for a long period of time such as the gorillas, are more likely to build a tight knit group and have lots of interactions with one another. Based on my observations, there are some behavioral patterns found in both primates and humans. However the cause of these patterns differ based on instinct and adaptations in primates compared to culture and morality in humans. I believe that by studying and observing behavioral patterns in primates, we can better understand where some of our own actions and  behaviors derived from, and whether its something that is instinctual and preprogrammed, or if it is something we have created and added to part of our culture as humans. Works Cited Cawthon Lang KA. 2005 October 4. Primate Factsheets: Gorilla (Gorilla) Behavior .

Thursday, January 9, 2020

The Never Before Told Story About Ap Us History Topics for Essay That You Must Read

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