Human Form versus Nature Essay Example | Topics and Well Written Essays - 2000 words

Human Form versus Nature - Essay Example The Romans were influenced by these thoughts and also sought to portray man as a superior being. Here the emphasis is on man’s power as opposed to the lesser importance of people as seen in Eastern art where nature has a much more dominant role. The sculptures of Michalangelo are famous for the way the human body is treated. With his excellent skill at carving the marble his work stands as some of the greatest ever created in this style. In China, the philosophical principles of Daoism and Confucianism play a big role in the way of life and the way of thinking is a guide to live by. One of the facets of Daoism is the relationship of nature in relation to its various elements and to man. Man is taught to follow the principles of nature. Nature in art is illustrated as the central element in a great many pieces. Nature as a dominant theme has lasted more than a thousand years. By the late Tang Dynasty, landscape painting had evolved to depict man as seeking an escape from everyday life to commune with nature in all its beauty. The influence of China spread to Japan, as did the philosophy of Buddhism. In Japanese art people are often portrayed as a small part of the vast landscape. They are only a part of the world and the powerful forces of nature are seen as great in comparison. Hokusai’s 36 Views of Mount Fuji beautifully illustrate this theme. â€Å"A hint to solving our current questions of what nature is, how it should be faced and how to coexist with it should be hidden within these art pieces that have viewed nature.† (Sakagami 1) References 1. Nature in Japanese Art after the Experience of the Earthquake, Keiko Sakagami, Web. 10 Nov. 2011. http://www.yomiuri.co.jp/adv/wol/dy/reviews/110422.htm Writing Assignment: The Afterlife Across Cultures The afterlife has long been a theme in art. From Ancient Egypt, Greece, Africa and other Far Eastern cultures the attitudes and beliefs about a supernatural transformation that takes place after a person dies has inspired many objects to be placed with them at the time of their death. In Ancient Egypt people were buried with objects that they might have used in their life on earth. This practice stems from the belief that the person will be living in another realm after their death in a similar fashion. They therefore will need the things they had with them in their former life. Depending on the place in society and economic class the t hings they will need vary. A member of the royal family may have statues of soldiers and musical instruments buried with them while a farmer might have animals and tools and pottery with them. These things relate to their lifestyle as it was. The idea of immortality was also ceremonial zed in the elaborate coffins the dead were buried in. The Egyptians believed that these complex burial rituals help to ensure the person would arrive safely in the afterlife. The coffins themselves were decorated with symbolic images that were believed to guarantee this passage into the next life. Many of these artifacts have been uncovered in tombs of the dead and survive in museums today. In Ancient Greece they believed that the spirit of a person left the body at the time of death and went to a place known as Hades. In the Underworld all of the dead resided. In honor of the deceased elaborate preparations of the body were made and large stone structures marking the grave sites were built. Sculpture s and other objects also decorated the graves. In addition to the actual site of burial, vases were decorated with scenes commemorating the person’s life in homage to them. The immortality of a person lay in their

Effects Pine Beetles Have on the Forests

Effects Pine Beetles Have on the Forests Climate change and the effects pine beetles have on the forests. Introduction The ever growing effects of natural and man-made climate change are having a wide-spread effect on many mixed and coniferous forest ecosystems. Particularly as average annual temperatures increase, the habitat for the mountain pine beetle, Dendroctonus ponderosa, has expanded, because the beetle is able to occupy new habitats at higher elevations, which were previously too cold for it. The mountain pine beetle habitat extends from Mexico through the Western United States and up to Canada. The damage caused to cone-bearing trees by the mountain pine beetle is threatening the strength of the North American mixed and coniferous ecosystems at every trophic level, as well as affecting the mountain forest carbon cycle and watershed hydrology. This damage has combined with the effects of human logging practices in the coniferous forest to drastically alter these ecosystems. Though these areas have been severely degraded, there are solutions that can slow or reverse the damage that has alrea dy been done. Background Human-caused climate change is having a pronounced effect on many different ecosystems. One of these effects is the spread of mountain pine beetles through the forests of the Western United States and Canada. Mountain pine beetles inhabit many species of coniferous trees such as jack pine, whitebark, lodgepole, Scotch, ponderosa, and limber pines. Pine beetles typically attack and inhabit trees at lower elevations, but the effects of climate change have allowed them to inhabit ever higher elevations. With mild winters and warmer summers, the pine beetles have been able to infest mature pine trees that could resist the beetles before the change in average temperature (Carroll et al. 2003). There were many pine beetle outbreaks in Canada and the U.S. Rockies since the 1940’s but they are considered mild compared to the more recent outbreaks. The earlier outbreaks were partly contained by human intervention and were ultimately ended by severe winter conditions, the natural regula tor of pine beetle populations. As climate change undermines this natural regulation system, the current infestations are much larger in scope and much harder to contain through human intervention (Ono. 2003). Mountain pine beetles spend their life cycle in four stages: egg, larva, pupa, and adult. In the summer the adults migrate and infest new trees. During the stages of their life they live under the tree bark where they feed and lay their eggs (Carroll et al. 2003). The mountain pine beetles’ life cycle and survival rate is regulated by the temperature of their habitat. Temperature at a particular time of year helps regulate the life cycle stage of the beetles, determining in part when eggs are laid, when the pupas become adults, when they migrate, and ultimately when the beetles die. A rapid decrease in temperature can kill an entire population of beetles. Other factors for survival include the dryness of the tree and the amount of snow insulation, but mainly the change (drop) in temperature is what keeps beetle populations in control (Creeden et al. 2013). Effects on the Ecosystem Changing climate and weather conditions in the higher elevations and their forest ecosystems are expanding the survivable habitat for the mountain pine beetle. The climate change occurring in these areas is weakening the overall strength of mixed and coniferous forest ecosystems. Hotter summers with less rainfall have caused many tree species to lose their natural defenses. Drought conditions have long been an indicator of previous outbreaks and are now a predictor of new pine beetle outbreaks. In turn, extended drought can also have a negative effect on the pine beetles if the drought lasts too long and the number of available hosts drops. Rising temperatures creates tree loss from drought and fires that hinders pine beetle migration (Creeden et al. 2013). At the same time, climate change exposes beetle infested conifers to a greater risk of fire and drought, reduces their resistance to both, and threatens both the beetles and the trees. Climate change is not only affecting the pine beetles, but species at every trophic level. One of the biggest food sources in the forest is new tree growth and seeds from mature trees. With changing climate conditions trees are not able to reproduce at the pre-climate-change rates. This is especially true in drought areas where the mountain pine beetle has infested the trees. The pine beetles weaken and destroy trees and reduce the rate of seed production and new tree growth, which affects small mammals such as squirrels that rely on the seeds pines produce. Decreasing food supply for smaller animals affects the population size of these species, which in turn affects their larger predators on higher trophic levels (Bartos et al. 1990). Climate change and the spread of pine beetle habitat are having such large effects on mountain ecosystems that it can change the diversity of species in the forests. The mountain pine beetle is no longer just an important species in the forest ecosystems they normally in habitat, they have becom e an important indicator species for ecological problems areas they normally do not inhabit. The expansion of their habitat demonstrates that climate change is having an effect on the entire ecosystem. Moreover, climate change is having an immediate effect on biodiversity and the ecosystem of conifer forests, which is increasing and accelerating (Logan et al. 2003). This is why it is important to keep track of the health of the ecosystem and make quick decisions when detrimental changes are observed. Effects on the Carbon Cycle Climate change and pine beetle outbreaks are also having an adverse effect on the carbon feedback cycle. Currently in British Columbia, Canada the outbreak of mountain pine beetles is so large that Canadian conifer forests have turned from carbon sinks to sources of carbon. Because of the combined effects of mountain pine beetle infestation, logging, and forest fires, large sections of forest are being damaged, which increases the amount of carbon dioxide. It is estimated that 435 million trees have been lost to the combined effects of climate change. This is having a big economic effect on the timber industry. The industry has responded by increasing the rate of harvesting and moving into areas that have not previously been logged. (Kurz et al. 2008). In these area loggers are stripping the biomass of the forest and turning it into, among other things, wood pellets as an energy source for Europe. Combining the damage from the mountain pine beetles, increased forest fires, drought, a nd all the commercial uses, these forests will release more carbon dioxide than they absorbs. This will increase both the causes and effects of climate change and worsen the situation years from now (Lamers et al. 2014). Kurtz modeled the effects of the mountain pine beetle in a test area of 374,000 km ² during the years 2000 to 2020. The study estimated that 270 megatons of carbon would be released during the pine beetle outbreaks in the test area. The model showed that if an area was untouched by pine beetle infestation but had moderate timber harvesting and fires, then the test area was a slight carbon sink; in the control scenario the area averaged 1 to 5 megatons of carbon release per year between 2007 and 2020. Two test scenarios were modeled, one in which the forest was infested with mountain pine beetles and one that included both infestation and additional timber harvesting. The scenario with mountain pine beetle infestation and normal harvesting showed the forest to be a net carbon source ranging from 10 to 20 megatons of carbon per year during 2007-2020. The scenario with the section of forest infested with mountain pine beetles and having additional harvesting due to timber damage showed that the forest was a net source ranging from 10 to 25 megatons of carbon per year for the years 2007 to 2020 (Kurz et al. 2008). This model shows that in the forests of British Columbia mountain pine beetle infestation combines with natural disasters and timber harvesting to help drive climate change (See fig 1). Effects on Watershed Hydrology Increased destruction of forests by the mountain pine beetle is causing a large effect on the hydrology of pines forests and the watershed. The increase in dead trees is having an effect on evapotranspiration as less of the sunlight evaporates water from live trees and instead heats the surrounding surface, raising local temperatures. This is turn is causing a change in hydrology locally and in areas downstream. The damage to the trees is also having an effect on the water quality and the biochemistry of the area (Mikkelson et al. 2013). The snow packs are also being affected; there has been an increase in canopy transmittance and a decrease in the amount of snow that is stored in the canopy. As more trees die solar radiation has been able to penetrate farther causing an increase in evaporation and a change in albedo (Winkler et al. 2012). Once an area of forest is affected, it takes several years for the changes in the canopy cover to effect a complete change. It takes an average of two to three years for the needles of the pine trees to change from green to red. During this time only a small portion of the canopy cover is lost and results in only a small change in interception. A few years after the needles turn red is when the trees turns gray and the majority of the needles are lost to the forest floor. During this stage pine needles and branches fall to the forest floor and eventually the entire tree falls and decays. This increases the amount of nutrients in the soil such as carbon, phosphorus, and nitrogen, which leads to nitrification of the water supply (Mikkelson et al. 2013). These changes alone will cause noticeable changes in the quantity and quality of the water. Adding more numerous forest fires and increased timber harvesting can have a drastic effect on the local watershed (See Fig. 2). Rita Winkler and her colleagues studied the effects of snow accumulation, forest structure, and snow surface albedo in the Rocky Mountains after a mountain pine beetle infestation. Over a seven-year period they studied these effects in areas that were clear cut, mixed, or young pine forests. Their study showed that areas that were primarily infested young pines completely lost their canopy within six years. Due to the loss of their canopy the snow accumulation decreased while transmittance and snow surface albedo increased when trees turned from green to gray. The study found that as trees turned from green to gray the rate of snow water melt increased. In areas that had mixed species of trees the effects were not as drastic as the areas with only young pines. The primary reason that snow accumulation and surface snow albedo were not as affected was due to a large diversity of tree species. In these areas there was also a more developed understory that reduced the effects seen in areas that were primarily young pine. Moreover, while the effects increased from mixed species areas to young pine areas, the affects in neither area compared to the far greater affects in areas that were clear cut (Winkler et al. 2012). It is easy to see from this study that the type of forest, level of beetle infestation, and timber harvesting practices will have a significant or large effect on the water cycle and the hydrology of the surrounding watershed. In the Rocky Mountains this can have a particularly extreme effect on the quality and quantity of river flow in this region since the Colorado River is supplied largely by snow melt. If this trend continues, the amount of water coming out of the Colorado River will decrease, which could lead to increased water shortages in the Southwest. Managing Mountain Pine Beetle Outbreaks As the population and habitat of the mountain pine beetle continues to expand several types of management practices have been tried. Currently Western Canada is experiencing one of the largest expansions of mountain pine beetles, with estimates that over 13 million hectares of conifer and mixed forest have been affected. There are two main methods to manage pine beetle outbreaks, or at least slow their expansion. The indirect control is a preventative method that tries to limit host trees through prescribed burning and forest thinning. The direct method tries to limit the population and growth rate of the beetle by destroying infected trees before the beetles emerge to migrate and attack new hosts (Wulder et al. 2009). There have also been studies done using chemicals on non-infected trees to try and limit the expansion of beetles to these areas. While this type of managing technique is effective, it is too costly to use on a large area of affected trees (Fettig et al. 2007). Coggins and his colleagues completed a study in Western Canada to test which management practices were the most effective. In their study, they used two different areas and selected 28 sites with each plot of trees having a radius of 30 meters. Each plot was selected due to the age of the trees, elevation, and the severity of beetle infestation. They broke their plots into two groups. Eighteen of the plots were not managed while management practices were implemented on the other ten plots. For the ten plots that were selected for mitigation they used tree removal techniques to remove the infected trees before beetle migration. In their study, they calculated that at the beginning of their study, the average expansion rate was 0.29 for non-managed plots and 0.12 for managed plots. Over a ten-year period they showed that the plots of unmanaged areas grew exponentially. While during this same period the managed plots went to zero infected trees after ten years with a 43% detection rate. The s tudy found that the time to reach zero infected trees would be shorter if the detection rate was increased (Coggins et al. 2010). It can be concluded that managing practices will have an effect on the migration of the mountain pine beetle. The main problem with controlling their migration is detecting infected green trees. The problem is that they cannot be detected from the sky, so people have to actively go into the field to detect them. This causes a problem because some areas are inaccessible for a variety of reasons. Even with all of the problems associated with managing the mountain pine beetle, it is vital for the forest ecosystems of North America that these practices continue. Conclusion While the mountain pine beetles will continue to expand and inhabit new areas management practices need to be put into place. The main cause of the mountain pine beetle expansion is primarily due to climate change, particularly drier, hotter summers and shorter, warmer, drier winters. These insects in turn are also contributing to climate change. As their habitat expands, they are turning forests that were once net carbon sinks into net carbon sources. When infected trees die and decay, they release carbon dioxide and increase the amount of phosphorus and nitrogen in the ground. The damage the beetle is causing to forests is also changing the watershed in negative ways. Both the quality and quantity of water is being degraded, which affects the health of the ecosystem. All of these changes combined are having an extreme effect on the ecosystem and negatively affecting every species in it. At every trophic level there is some kind of effect as the mountain pine beetle expands and dest roys the forests. More studies must be done to help mitigate mountain pine beetle expansion and more money needs to be invested in managing them. As a society we will take a major economic hit if the timber we need is destroyed by the mountain pine beetle. Also, if their expansion continues in the Rocky Mountains and damages the watershed there, it could affect a large portion of the drinking water for the Western United States. We need to manage the mountain pine beetle as we reduce carbon dioxide emissions to curb the effects of global warming. Figure 1 Figure 2 Works Cited Bartos, D. L. and K. E. Gibson. Insects of whitebark pine with emphasis on mountain pine beetle. UT 84321. U.S. Department of Agriculture, Forest Service, Montana, United States. Carroll, A. L., S. W. Taylor, J. Regniere and L. Safranyik. Effects of climate change on range expansion by the mountain pine beetle in British Columbia. BC-V8Z-1M5. Canadian Forest Service, Pacific Forestry Centre, Victoria, British Columbia, Canada. Coggins, S. B., N. C. Coops, M. A. Wulder and C.W. Bater. 2011. Comparing the impacts of mitigation and non-mitigation on mountain pine beetle populations. Journal of environmental management 92: 112-120. Creeden, E. P., J. A. Hicke and P. C. Buotte. 2013. Climate, weather, and recent mountain pine beetle outbreaks in the western United States. Forest Ecology and Management 312: 239-251. Fettig, C. J., K. D. Klepzig, R. F. Billings, A. S. Munson, T. E. Nebeker, J. F. Negron and J. T. Nowak. 2007. The effectiveness of vegetation management practices for prevention and control of bark beetle infestations in coniferous forests of the western and southern United States. Forest ecology and management 238: 24-53. Lamers, P., M. Junginger, C. C. Dymond and A. Faaij. 2014. Damaged forest provide an opportunity to mitigate climate change. Bioenegy 6: 44-60. Logan, J. A., J. Regniere and J. A. Powell. 2003. Assessing the impacts of global warming on forest pest dynamics. Frontiers in ecology and the environment 1: 130-137. Mikkelson, K. M., L. A. Bearup, R. M. Maxwell, J. D. Stednick, J. E. McCray and J. O. Sharp. 2013. Bark beetle infestation impacts on nutrient cycling, water quality and interdependent hydrological effects. Biogeochemistry 115: 1-21. Ono Hideji. 2003. The mountain pine beetle: Scope of the problem and key issues in Alberta. BC-X-399. Canadian Forest Service, Pacific Forestry Centre, Victoria, British Columbia, Canada. Kurz, W. A., C. C. Dymond, G. Stinson, G. J. Rampley, E. T. Neilson, A. L. Carroll, T. Ebata and L. Safranyik. 2008. Mountain pine beetle and forest carbon feedback to climate change. Nature 452: 987-990. Winkler, R., S. Boon, B. Zimonick and D. Spittlehouse. 2009. Snow accumulation and ablation response to changes in forest structure and snow surface albedo after attack by mountain pine beetle. Hydrological Processes 28: 197-209. Wulder, M. A., S. M. Ortlepp, J. C. White, N. C. Coops and S. B. Coggins. 2009. Monitoring the impacts of mountain pine beetle mitigation. Forest ecology and management 258: 1181-1187.

Good Science :: Science Argumentative Persuasive Essays

Good Science Science has helped to improve the lives of people around the world. Today, science has improved human health and medicine to help people live longer, and help people live with diseases people had little hope of living with a few decades ago, such as AIDS. While our scientific advances continue, ethical questions arise about how science should advance, such as stem cell research. Mary Shelley, author of the novel Frankenstein, and Michael Bishop, who wrote the article Enemies of Promise, have different views about how scientific knowledge affects humanity. Mary Shelley was born the daughter of feminist Mary Wollstonecraft and political theorist William Godwin. While on vacation with her husband, she began to write the novel Frankenstein, about a scientist who created life. The scientists name was Victor Frankenstein. In a selection from the novel, Frankenstein says The dissecting room and the slaughter-house furnished many of my materials; and often did my human nature turn with loath ing from my occupation, whilst, still urged on by eagerness which perpetually increased, I brought my work near to a conclusion (232). Frankenstein is disgusted because he must go to a slaughter-house to get parts for his creation. Frankensteins disgust shows how horrible and demoralizing his scientific endeavors are, and he continues his experiment despite the negative affect his experiment has on his health. He realizes the study to which you apply yourself has a tendency to weaken your affections, and to destroy your taste for those simple pleasure in which no alloy can possibly mix, then that study is certainly unlawful, that is to say, not befitting the human mind (233). Frankenstein worked so hard to give life to his creation he thought of nothing else, and he was living his whole life to accomplish one goal. He realizes how much time he has been spending on his experiment and the effect his work is having on him, so he believes humans do not have the ability to deal with work in this manner. Therefore, scientific experimentation is not worth the negative effects the experiments have on the human mind. Eventua lly, Frankenstein accomplishes his goal, but his creation does not turn out like he expected. After giving his creation life, Frankenstein is horrified and leaves his home. Frankenstein concludes Learn from me, if not by my precepts, at least by my example, how dangerous is the acquirement of knowledge, and how much happier that man is who believes his native town to be the world, than he who aspires to be greater than his nature will allow (231).

Matrilineal Societies

Sociologyindex, Sociology Books 2011, Matrilineal Descent, Patrilineal Descent Matrilineal societies are those societies in which descent is traced through mothers rather than through fathers. In matrilineal societies, property is often passed from mothers to daughters and the custom of matrilocal residence may be practiced. In matrilineal societies, the descendants of men are their sister's children and not their own, who belong to their mother's matrilineage. Matrilineage is sometimes associated with polyandry or group marriage where women have a variety of sexual partners and lines of male descent are uncertain. Ancient societies are known to have recognised matrilineal descent. Matriliny is not the mirror image of patriliny. Matrilineal societies differ from both patrilineal and bilateral societies in that the institution of marriage tends to be, relatively weak (Schneider and Gough 1961, Goode 1963). In a gerontocratic matrilineal society, women's influence and prestige tended to increase with age and were usually expressed in informal settings, although there were offices of formalised informality such as â€Å"mothers† of matrilineages. Matriliny required the subordination of marriage and conjugal duties to loyalty to and participation in the descent group. This, combined with economic activities, farming, artisan work, and trading, gave women considerable independence. Women (like elders) had prestige in the matrilineal home town, where black stools symbolised the â€Å"seat of power. † (Bartle). In a matrilineal society, women generally have a greater autonomy in terms of sexuality and reproduction than their counterparts in male dominated societies. The woman in a matrilineal society represents the clan and her children carry on the name of her clan. Land Inheritance and Schooling in Matrilineal Societies: Evidence from Sumatra – Agnes R. Quisumbing, and Keijiro Otsuka Abstract: This paper explores statistically the implications of the shift from communal to individualized tenure on the distribution of land and schooling between sons and daughters in matrilineal societies, based on a Sumatra case study. The inheritance system is evolving from a strictly matrilineal system to a more egalitarian system in which sons and daughters inherit the type of land that is more intensive in their own work effort. While gender bias is either non-existent or small in land inheritance, daughters tend to be disadvantaged with respect to schooling. The gender gap in schooling, however, appears to be closing for the generation of younger children. – capri. cgiar. org/wp/capriwp14. asp Gough, K. (1961) â€Å"The modern disintegration of matrilineal descent groups,† in D. M. Schneider and K. Gough (eds. ) Matrilineal Kinship, Berkeley, U. Calif. , pp. 631-54 Oppong, C. (1974) Marriage Among a Matrilineal Elite, Cambridge University Press. Matrilineal Society in India – Dr. Madhumita Das When most of the people in the world follow the patrilineal system, there exist a few groups here and there who believed to be the descendants of Japheth (son of Noah), and are followers of the matrilineal system (Syiemlieh, 1994). At the global level, the existence of matrilineal society is found among the tribes of African countries, in some part of Southeast Asia and among three groups of India. It is the Minangkabaus of West Sumatra, Indonesia, comprising the largest ethnic group in the world who follow a matrilineal system (Tanius, 1983). In Indian context, the matrilineal social system is found only among small pockets of south the and northeast India. The Nairs and Mappilles in Kerala, the tribal groups of Minicoy Island and the Khasis and the Garos of Meghalaya are the followers of matrilineal system. However, the matrilineal system of the African countries differs considerably from that of the Southeast Asian groups. Even within India, the system differs from one group to another (Kapadia, 1966). Among these groups, difference is mostly observed in the type of residence after marriage. The pattern of duo-local residence exists among the Ashanti of the Gold Coast in Africa, Minangkhau of Sumatra and the Nayars of Central Kerala. However, the Khasis of Meghalaya, generally follow the residential pattern known as â€Å"matrilocal residence†, where the husband resides with his wife's matrilineal kin or in other case couples settle down together in a new residence in and around his wife's maternal place (neo-local residence). Methodology This work discusses the changes that are occurring among the only few existent matrilineal setup in the world in terms of their attitudes and behaviour. In order to discuss the changes, the existing literature has been reviewed and they are supplemented by in-depth interviews of a few key informants. The key informants include eminent academicians, elderly persons of different localities, local heads, social workers and persons representing the younger generation. In addition, two focus group discussions (FGD) were done with women from different age groups. The idea behind this exercise is to clearly identify those features that have been characterising the matrlineal system of the Khasi tribe these days. Along with the qualitative analysis, the profile of women living in original matrilineal arrangement as against those who have completely transited in the form of percentage distribution is also presented. A few socio-economic, demographic, and developmental characteristics of both women and her husband has been taken into consideration. Lastly, a multivariate analysis has been undertaken to substantiate the findings from bivariate analysis and to find out the factors, which brought changes among the society. Study Area The basic aim of the study is to understand the structure of matrilineal system and the changews that has taken place in it over the period of time among the Khasis of Meghalaya. In Meghalaya there exists three tribal groups, namely Khasi, Jaintia and Garo. The state is predominantly inhabited by the Khasi tribe, who are known for their matrilineal social system. The sample design adopted was a multistage design, fitted to the study requirements. Given the resources available, it was decided to cover 600 eligible women (currently married Khasi women age 15–49 years), all from (erstwhile) East Khasi Hills district. The choice of East Khasi Hills over West Khasi Hills was purely purposive. According to 1991 census, little over 33 per cent population of the East Khasi Hills district live in the urban areas. Thus, it was decided to cover 200 eligible women (33 per cent of 600) from the urban areas and the remaining 400 women from the rural areas. The Khasi Matriliny: An Overview The term matriarchy or matriliny has become inseparably associated with the Khasi social organisation since it was first used in 1914 by Gurdon to describe Khasi social customs (Das. Gupta, 1964). Although the term is used to explain the pattern of residence after marriage among the Khasis, it is, however, known that matrilocal residence is not an invariable concomitant of matriarchal or matrilineal society. As among the Nayars of India, though they are also the followers of matrilineal system, the residential system among them is duolocal, where husband is usually the night visitor to their wife. Before we begin to understand the nature of Khasi social organisation, it becomes necessary, to clear that the general rule of matrilineal system is that females inherit property. However, it must be noted that at the outset the system of inheritance is governed by some code of rules, which, if taken in its totality and richness, can hardly be described as simple. In fact, the Khasi society is more complex and vivid than what is it apparent. The Khasis have matrilocal residence and matrilineal descent. Participation in the family religion and the common sepulchre, where bones of the members of the family are interred after death, are the two elements that bind the members together. Besides the matrilocal residential pattern and matrilineal descent, family property is mainly transmitted through the female line. The children of the male do not belong to the family. The youngest daughter, Ka Khadduh, in a Khasi family is in charge of the family religion. She cremates her mother and inters her bones in the common sepulchre (a place where the bones are kept with a huge stone over it which is different in shape for males and females). Marriage is a great social institution among the Khasis, as it determines the system of matrilocal residential pattern among them (Sinha, 1970). Being the followers of a unique social system of matriliny, the Khasi women enjoy a special place of status and dignity (Kyndiah, 1990). A Khasi woman is the guardian and preserver of the family goods. She plays a crucial role in the affairs of the family. However, she is not the head of the family, as this is left to a male member. The father of the family has a definite role to play in the household affairs. However, his role is limited to the final word of the maternal uncle. When Christianity came, the Khasi family was aced with the question whether a â€Å"Ka Khaduh† could hold the family property if she would convert to the Christianity. In 1918, the Government ruled that Christian converts should be allowed to inherit the ancestral property. Property is thus divorced from religion. Though religion was divorced from the traditional rules, because of the modernisation process, such as, educational development along with the spread of Christianity, that had somehow changed the traditional system in many respect (Roy, 1964). The original system and moral efficacy has now a days been largely distorted (Bareh, 1994). The literature shows that a shift is taking place in the matrilineal society towards parental or patrilineal one (Tanius, 1983; Syiemlieh, 1994). Syiemlieh (1994), in his write-up on the Khasis and their matrilineal system has explained that due to some basic reasons there exists a transition in the matrilineal set-up in Meghalaya. This transition in the matrilineal society is due to the changes in the overall set-up. Such changes can be the result of factors like the intermingling with other neighbouring patriarchal communities, the advent of missionaries and spread of Christianity among these tribal groups. The spread of urbanisationand urban development along with the spread of Christianity have changed the perception and attitude of people among the Khasis ( Kapadia, 1966; Syiemlieh, 1994). Thus from the above review we get the idea that over time these matrilineal societies are undergoing changes in its characteristics. On the basis of the above literature, each characteristic feature has been given weightage to categorize the sample women in two groups, viz. , Traditional: Women fulfilling all three criteria or those who possess at least ownership right along with matrilocal residential pattern or matrilocal residential pattern and descent through female. Transitional:Women who follow none of the criteria or only descent. It is found from the above categorisation that 55 per cent of sample women are from the traditional group while the remaining 45 per cent are from the transitional group. The Traditional women will be refereed to as ‘traditional women’, whereas women in Transitional group will be referred to as ‘transitional women’. It may be relevant to mention here that these nomenclatures are used for the purpose of conceptual categorisation of these two groups of women according to their characteristics assessed at the time of survey. Yet another issue that needs to be kept in mind is that the term ‘traditional’ is not used as opposed to ‘modern’. It may be emphasised that women in traditional group are the followers of all the three or the first two important characteristics of the matrilineal system, i. e. , property ownership right, matrilocal residence and/or family name through mother’s side. Socio-economic and Demographic Characteristics ofWomen in Matrilineal Set-up Type of Residence Type of residence is one of the important determinants that has its effect on the changes that take place in any society, as well as, on the changing perception of people towards traditions. Women from traditional group are mostly concentrated in rural areas (79 per cent). What is, however, more interesting is that 21 per cent women following the matrilineal system live in urban areas and also almost half of the women who have deviated from matrilineal system continue to live in rural areas. This indicates that the transition that we witness in Khasi society is a complex phenomenon operating at family level than merely the outcome of urbanisation and modernisation process.

Argumentative Essay Essay

Governments should be more involved in citizens diets Modern age supermarkets selling off the shelve foods are normal nowadays. Unfortunately the knowledge of what is healthy and what is not had been effected by this. People should be better educated on what is healthy and what is not. Healthier diets make healthier citizens and healthier citizens will save a lot of money in health care, bad diets do cause expensive health problems. Although it is general knowledge that unhealthy products are cheaper than healthy products, it is not general knowledge that products claiming to be healthy are usually full of harmful and unhealthy ingredients. It is time the government steps in to protect the population. Firstly, health problems caused by bad, unhealthy diets weigh heavily on health care expenses. Several population-based prevention policies can be expected to generate substantial health gains while entirely or largely paying for themselves through future reductions of health-care expenditures according to The Lancet (Cecchini et al., 2010). Just by eating healthier a reduction will be made possible, this alone should be reason enough for a government to get more involved Secondly, people will be stimulated to choose healthier products when prices for unhealthy products will be raised. The current situation is just the other way around. The healthier choice is more expensive. â€Å"With proper nutrition and regular exercise, you can reduce the costs of health insurance premiums, the amount you spend on medicines and the number of co-pays for doctor visits† according to Livestrong (Ellyn 2011). However true this may be, as long as healthier products cost more instead of less people will be inclined to buy more unhealthy products. Thirdly, in order to make the healthier decision, information about unhealthy ingredients should be clearer and more visible. Reading food labels is strangely enough rather difficult, excellent vision and extensive knowledge on what the ingredients mean are necessary to understand the labels. â€Å"It makes it easier to compare similar foods to see which is a healthier choice† according to the Mayo Clinic (2012), however easier to understand labelling, easier to read labelling will enable more people to making that choice. In conclusion, if governments decide to invest in educating the population it will enable and stimulate citizens to make healthier choices. In order to reach this goal the government should demand clearer and more visible information on products concerning the ingredients put a fairer price on healthier products.