Landscaping More than Just Beautification

The article Transforming Inner-City Landscapes queries the inner-city residents response to landscaping projects in their courtyard. It generally dwells on the relationship of the incorporation and placement of trees, and grass vegetation in urban public housing with the residents preference and sense of safety. The responses of surveyed individuals would give land developers a general idea of residents preference and are primarily important so to assess if landscaping is a better idea, and if yes, what technique or style to be conducted.

    The research design was conducted by surveying 100 residents of Chicagos Robert Taylor Homes. Photo simulations of the neighborhood courtyard were shown depicting tree density, tree placement,  and  grass maintenance whereas surveyed residents were asked to rate photos they felt more beautiful and more safe living into (0 not at all and 4 very much). Average ratings have shown that the bare arrangement of the present courtyard was less appealing to residents (M  0.3 rating for the current courtyard look).  On the other hand, the presence of trees had very strong and positive effects on the residents (M  1.3)2. According to the article, tree density and grass maintenance have a direct relationship with residents preference and sense of safety. The presence of trees does make them feel more secure and more fond of to the open space.  On the other hand, tree placement has inconsistent correlation with the residents sense of safety. The effect of the trees spatial distributions vary significantly for the respondents, but it was observed that the blocked views lessen residents sense of safety.

    In effect, the research has shown that residents have a positive feedback to landscaping inner cities. Not only does it increase the beauty of the neighborhoods open space, it also adds to the sense of security of its residents. In addition, landscaping can also mitigate unconstructive environmental impacts of urban development, help lessen overcrowding in housing units, provide a play haven for children, boost physical and psychological health of residents, and potentially decrease crimes in the neighborhood.

    Primarily, the purpose of the study is to discern whether landscaping is a viable idea. As shown by the respondents, incorporation of trees and grass vegetation have positive effects. On another note, the respondents only constitute a very small portion of inner-city residents population and the results shown may not be same in all cases. It is essential to conduct more research andor surveys to the concerned population so to determine if landscaping should be done in a certain neighborhood.

Biodiversity and Stability

It has become evident in the world that biodiversity is fast declining.  It has been documented that about one third of the world plant and animal species in most countries are faced with the risk of extinction. This is considered a monumental problem as it poses a risk to the continued existence of world biodiversity (Colyvan 147). Owing to the risk faced, scientists have gone back to the debate of ecological diversity and stability. The current research and debate on the future of ecosystem viewed in lenses declining biodiversity is supported by the fear of unknown. The biodiversity-stability debate looks into the future of the world ecosystem based on theoretical bases. What will happen to the stability of the world ecosystem with the declining biodiversity

The world flora and fauna is disappearing at an alarming rate.  It is considered that the extinction of the world flora and fauna is faster than the mass extinction events. Ecological findings also evidence that species invasion has been happening at an alarming rate thanks to the increased globalization (Lodge 135). These two events are putting the ecosystem at a greater stress which has made it important for scientific world to understand the relations existing between change in ecological biodiversity and the stability.   The issue at hand at hand is the continued deconstruction of earth in assumption that the ecosystem has developed its own ability to cope with species assault and extinction.

The old debate shows that in a way, diversity and stability are correlated. Increased biodiversity is correlated with ecosystem stability.  Although it does not infer that diversity is the main driver of ecosystem stability, there is sustainable evidence which shows that diversity is a passive recipient of the different ecological mechanisms which drives stability in the ecosystem (Yodzis 675).

One of such mechanism has proposed that in an ecosystem, there are weakly interacting species which tend to stabilize communist dynamism and enhance increase stability (Odum 324). This means that the existence of more of such species will end up creating a more stable ecosystem.  This has been further supported by empirical description of interaction distribution theory.  If this theory is assumed to be true, it is therefore evident that decrease in biodiversity  is accompanied by increase in average interaction strengths between species in an ecosystem and therefore in the long run will create a decreased stability in the ecosystem (Cooper 530).

Earlier studies in diversity-stability debates showed that there was a positive interaction between the two aspects.  One of the strong proponents Charles Elton argued that simple communities tend to be upset faster compared to richer communities.  This implied that simple communities were prone to destructive oscillations in their population and were also more vulnerable to species invasion (Castle 155).  This presumption was supported by works of other ecologists who supported the argument that simplified terrestrial communities were prone to violet population fluctuations compared to diverse terrestrial communities. For example they showed that species invasion mostly occurred on lands which have been cultivated since they have been left with simplified ecosystems (McArthur 534).  They also showed that attacks of phytophagous insects were more common in boreal forests while less attacks were experienced in diverse tropical forests.  These and other observations led to conclusion that the presence of a diverse ecosystem with predators and parasites was important to prevent explosive growths in such ecosystems.

However, studies carried out consecutively in 1970s using mathematics linear models showed the opposite.  Through use of statistical universe which had randomly constructed community which had been assigned interaction strengths showed that diverse made the ecosystem weak and less stable. However, opponents argued that these studies used weak model to study the diversity-stability relations and hence there is need to carry out more research to authenticate the reliability of this model (May 18).

A long term study that was carried out by David Tilman in 1982 looked closely into this relationship. The study was aimed at delineating experimentally the existing relationship in plant communities.  It was carried out in four grassland fields located in Cedar Creek in Minnesota and was further divided into 200 experimental plots. The study collected information on richness, community biomass, and population biomass over a long period of time.  The study showed that diversity in the ecosystem was   positively correlated to stability in the plant community (Riciardi 123).  This means that biodiversity is related to decreased coefficient of variability in the community biomass.  Biodiversity-stability relationship among these primary producers can be supported by averaging effect and covariance effect hypothesis. Both hypothesis argue that diversity tend to increase stability since diverse communities respond differently to variable background process.  The sum in differential population responses over a long time brings about stable community dynamics (Elliot 35).
Research findings shows that biodiversity leads to ecological stability. A model diverse ecosystem is in a better position to withstand the effects of population fluctuations. A diverse community also withstands the invasion of species. In long term, withstanding population fluctuation and species invasion creates stability in the ecosystem.

Improving the Role of Environment in UAE Mangrove

Did you know that lack of mangrove plantations across the globe would lead to the breakdown of environmental systems and in the economy in general Did you also know that there is a high decline on the mangrove populations in planet earth The earliest recorded reference in relation to mangrove forests was in 325 B .C. by Nearchus, a Greek explorer who traversed the Mediterranean Sea. The word mangrove is gotten from the word grove, which means a group or a stand of trees. It is also defined as a diverse group of predominantly tropical trees, shrubs, palms or ground ferns that generally exceed two feet in height, and grow primarily in the marine intertidal zone (Buck, 2000). This post will discuss how to improve the role of the environment in the United Arab Emirates.
Despite the fact that mangroves are classified as trees, they have a versatile form, in that they grow in harsh conditions and are quite low. Also, they have canopies which can attain a height of forty meters and above under favorable conditions. The habitat of the trees is known as mangrove or tidal forest. The mangroves can be referred to as the border between land and sea because they mark the inter phase between marine and terrestrial types. They are grouped in ecological groups which are similar in physiological terms (Biota, 2007).

Mangroves are commonly found in habitats which are salty and as a result, they have adapted to the saltiness of their habitats. Some of the adaptations include having glands that excrete salt near their leaves and having exposed roots specifically for proper gaseous exchange (Buck, 2000).Therefore, the mangrove is an important part of the ecosystem as seen from the discussion.

The Earth Summit
This was a conference held in Rio de Janeiro in 1992 which devoted great attention to the third world countries in matters regarding the global pollution that existed. According to the researchers, global pollution was as a result of greenhouse gases spawned by industrialized countries, particularly Europe and the United States. The summit also discussed in length on how to improve desert lands in the world by various ways of land reclamation and planting vegetation which are adapted to such situations. The U.A.E. is one of the countries in the world which has highly utilized all the resources it has so as to do avoid desertification (Smith A, 1999). 

The United Arab Emirates
The United Arab Emirates is a tropical region which has a lot of mangrove plantations in its coastal areas. The most common species of the mangrove tree in U.A.E. is known as the Avicennia marina. Mangrove colonies are present along Abu Dhabi, Khor Kalba and Ras Al Khaima islands. They contribute a lot to the reduction of desertification and improve the natural habitats in the coast for fish and birds. They are seen to be very important in reforming the environment of the U.A.E. This is because there is availability of a coastline which is long, several islands and lagoons and an impoundment of natural water in U.A.E.  In the United Arab Emirates, mangroves crop up in patches alongside the coast and occupy about 3,000 hectares of the total surface area of the country (UAE Government, 2010).

Benefits of mangrove forests
Mangroves in United Arab Emirates are considered natural habitats and nursery grounds for several crustacean and fish. Its wood is also used for making poles, fuel wood for constructing fishing gears, and also used in charcoal production. In addition, tannin which is used in timber industries is also produced by mangrove trees. Mangrove tees also contribute much to the prevention of soil erosion and coastline wave action as their roots hold firmly to the ground. They also increase the resistance of the cyclones and waves, and contribute to mud flats formation. Lastly, the animals get good fodder from the mangrove trees, mostly in the arid areas (UAE Government, 2010).

How does the environment affect the U.A.E. Mangroves
U.A.E. is a desert ecosystem and therefore it very difficult to come up with a project in such an area. This is because once a building is constructed in a desert area it adds complexity as far as plant and animal species are concerned. A good example of people who faced this kind of challenge was the Abu Dhabi workers. The construction of the Al Gurm five star resorts had to go through a lot of challenges during its construction in the year 2007.The contractors would not just construct the resort without caring for the environment as they would have to cope with a remote resort or dry land. The senior leader in the project, Mr. Twal stated that before the construction of the resort was done, a lot of considerations had to be made in regard to the mangrove plantations that existed. Therefore, an Environmental Impact Assessment (EIA) was done for the site. Before construction would go on, the environmental consultant had to give what was known as Construction Environmental Management Plan (CEMP) so that they could start the construction work (Conford, 2007).

The construction of the resort gives us a good situation where the role of the environment proved to be very crucial to the mangroves. It gives a good example on what can be done so as to improve human activities in the environment for purposes of protecting the mangrove vegetation and its ecosystem. Building and construction is one human activity which can destroy the mangrove vegetation. It would be very risky to destroy the vegetation as it is the only vegetation type which is largely responsible for preventing desertification in the coastal areas of the U.A.E. Therefore, in building and construction, careful practices need to be adopted to ensure that there is minimum impact on mangrove plantations (Conford, 2007).

To start with, there has to be careful procedures for burials and the instruments which cut off the flow of water to the plantations. This is because the mangrove plantations require water to wash off the salinity effect on the leaves .If the flow of water is cut, it would result to desertification (Conford, 2007).

Fuel is non bio-degradable, meaning that it cannot be decomposed. A lot of machinery is used in building and construction with fuel being used in most of those machineries. It is therefore important to ensure that during construction work, there is prevention of possible fuel leakage as it destroys the mangrove ecosystem. Constructors should also avoid using chemicals and solvents near the vegetation as it will also have the same effect as fuel has (Conford, 2007).

It is impossible to construct any machinery work without excavating large amounts of silt. Silt is also dangerous as far as mangrove vegetation is concerned as it is not suitable for the growth of the mangrove growth. Therefore, a silt screen should be constructed around the construction site perimeter so as to ensure that there is no silt or nutrients which migrate to the plantations. This can happen when there are strong currents created due to the changing environment (Conford, 2007).
It is not only the construction which can cause damage to the mangrove ecosystem. Pollution issues will be prevalent and therefore there has to be adopted a vacuum sewerage system. During the construction of the resort, the sewage pipeline was housed in a bridges deck and it connected to the residential developments through the mangroves (Conford, 2007).

It is difficult to plant trees on any kind of coastal arid land due to the salinity level of water. Agriculture is therefore a difficult thing in a coastal land and it is impossible to reclaim the land in large scale. The only growth that can take place is that of mangrove trees, specifically the gray mangrove trees. However, there must be sea water and nutrients for the effective growth of the mangrove trees (Smith, 1999).  

According to the ecological observations made in various UAE lagoons, there exist abundant fish resources where mangrove vegetation is present. Seawater from farms with fish and shrimps has a high content of dissolved feed and a lot of human waste which is a great pollutant to the marine environment (Smith A, 1999).

The U.A, E. Ministry of environment and water realized that it was important to plant mangroves in arid areas. In 1985, there was an afforestation program which was launched and following the launch, there was seedling cultivation in different localities. It was also discovered that mangrove swamps could play a very good role in fish breeding, as they could act as nursery grounds to types of crustaceans and species. This is because they identified a lot of fish larvae in the mangrove cultivated areas. Examples of such species were snappers, rabbit fish and sea breams. These observations by the Ministry of Water and Environment made the government to advocate and support all fishery resources in U.A.E (UAE government, 2010).

Mangroves in the U.A.E. are not highly threatened by the dwellers for firewood, unlike other countries. Therefore the cutting down of trees is minimal. The government has largely contributed to this by backing a planting program which has ensured that the intertidal flats have been fully covered by the mangrove vegetation. However, deforestation happens at times in the U.A.E. though it is a very serious crime. Some people cut down the mangrove plantations without replacing them with seedlings. This is a serious misdeed which contributes largely to soil erosion and thereafter desertification. The role of man is to protect the mangrove vegetation so as to ensure that there is reduction in the dangers of soil erosion and desertification in general. (U.A.E. Interact, 2010).

The U.A.E. citizens are encouraged to preserve the mangrove vegetation as it contributes to rainfall. Even though it is a desert area, there is coastal greening as a result of the mangrove vegetation and it attracts rainfall, even though minimal. The fresh rain water is important to the mangrove vegetation in that the salt excesses released from the pores are cleaned off, therefore making gaseous exchange happen effectively within the mangrove vegetation (U.A.E. Interact, 2010).

Ecologically, the mangrove vegetation is very vital for coastal greening, protecting the coastline and restoring the habitat. A variety of birds and marine environment get a breeding habitat which adds to the beauty of the region and in turn promotes eco-tourism. This is especially so in the hyper arid coasts where very few trees continue to exist and flourish (U.A.E. Interact, 2010).

In conclusion, it is the responsibility of every noble citizen in the U.A.E. to ensure that the process of desertification is reduced in all ways possible. The government of U.A.E. has tried so much in reclaiming the land which was once a desert through the planting of mangrove trees. It has also been extensively involved in environmental conservation. If the environment is conserved by checking the human activities, the Mangrove vegetation will continue to flourish along the U.A.E. coasts, which will improve the countrys economy in general.

Pollution Rights and Environmental Problems

Strategies to check environmental pollution have gone to the extent whereby there is a market for pollution rights. Companies are buying and selling pollution rights under this new environmental pollution control effort. Even with the idea of ensuring a sustainable world, the question of how effective trading pollution rights as a way of controlling environmental problems still lingers. This essay discusses the impact of this environmental issue on a sustainable world by providing a critical analysis of the issue. 

What is Pollution Rights trading
    When a company has pollution rights, the company is allowed to discharge an agreed amount of a specific waste into the environment (Byrns, 2010). The Environmental Protection Agency as a regulator of environmental pollution for instance suggests the use of the government-issued license to allow companies emit such given quantities of waste. When talking of tradable pollution rights, this means that the pollutions permits can be sold and purchased at free market prices (Social Change, 2006). What happens is that firms that emit pollutions below their accepted maximum amounts are free to put the remaining allowances in the free market whereby firms that are polluting above maximum allowed or those intending to emit wastes exceeding this amount can buy the allowances. The government may decide to trade the rights by simply selling them or otherwise it may opt to auction them with the highest bidder qualifying for the rights. The whole idea of pollution rights trading is also considered as the cap-and trade policy with the cap implying that a firm can emit pollution only up to a set maximum and trading the rights to higher polluters with adherence to market forces (Byrns, 2010).

Impact of pollution rights trading
    The concept of trading pollution rights is based on the take that open access to resources leads to pollution especially air and water pollution. Since there is no individualprivate ownership of these resources, it is suggested that individuals lack the sense of responsibility in preventing pollution (Social Change, 2006). It therefore follows that individuals would have incentives to control overexploitation of the resources and the pollution thereof if they were given a right to own the resources privately. It is important to bear in mind that tradable pollution rights came into implementation in the United States first and the idea was primarily to bring industry costs down as well as facilitate economic growth in areas that had high pollutions (Beder, 2001). Even with the adoption of this policy into environmental pollution control efforts, the initial idea of helping the firms seems to dominate over the solving of environmental problems and ensuring a sustainable world.

    Among the few environmental benefits attributed to trading pollution rights the idea that since pollution permits are issued and given by regulatory authorities, it is possible to control pollution levels. This can be achieved by having the regulatory bodies limit the number of permits available to firms. Additionally, it is argued that since a company would incur more costs by buying pollution rights, introduction of the permits would eventually lead to reduced pollution as companies seek to reduce their costs. The argument here is that if a firm were to continue polluting the environment, then it would have to spend more on purchasing the permits otherwise it would choose to save the costs by ensuring reduced pollution. It is also proposed that even companies with the ability to purchase pollution rights, the free market in pollution rights is an incentive that persuades such companies to reduce pollution by giving them a choice to sell initial rights (Social Change, 2006). 

    The introduction of tradable pollution rights was also based on the argument that companies that exceeded their upper limit of pollution would get a chance to buy the permits and continue emitting pollutants. On the other hand, the firms would also choose to channel their finances into innovations that would clean up the environment (Bush, 2009). Even with such an idea, it is unfortunate that only the firms seem to be benefiting from reduced costs whereas environmentally, encouraging progress has not been made. Firms seem to be polluting with protection from the law with maximization of profits ignoring the protection of the environment. Regulatory bodies seem to fail to see the harm that the free trading of pollution credits can hamper innovation geared towards reducing pollution. This is mainly an influence of a prospective seller (Dana, 2005). To this extent the feasibility of ensuring that the world is sustainable through reduced environmental pollution is far from being attained.

    It is appreciable that through trading of pollution rights, some areas have seen dramatic reductions in the amounts of waste emitted. Sulfur dioxide was for instance shown to have reduced dramatically due to the establishment of a cap-and trade initiative. There is failure however to see the danger of continued pollution resulting from the ability of some firms to buy any amount of pollution rights (Bush, 2009). The more the companies compete to buy the allowances, the more the likelihood of extending pollution levels to unmanageable levels. In fact, instead of the companies saving to invest in advanced methods of cleaning the environment, finances are turned into the rights market.

        The market for pollution rights does not really encourage reduction of pollution and sustainable world. So far, some countries such as Russia and European countries have pollution rights worth billions of money and as such, they produce wastes in billion tons. There is much worry that if such countries were allowed to still hold to the rights even after the set deadline of 2012 would only add to further pollution. The countries would amass huge profits by selling the excess rights but the environment would still remain polluted more so pollution in those countries (Bowen, 2009). The idea here is that firms are getting a go ahead to pollute so long as they can afford it in terms of money.

        Though it may seem appealing, the introduction of emission offset is a clever way of firms continuing to emit pollutants in a certain area. It does not work to reduce environmental pollution by having a heavy polluting firm to continue emitting its wastes just because it capably purchases the rights and convinces other firms to reduce their pollution. In this case, the effectiveness of trading pollution rights in controlling environmental pollution is unrealistic (Social Change, 2006). It is simply a shift of rights to pollute from one company to the other and not the real reduction of pollution. The same practice is propagated by the introduction of the bubble. The bubble policy argues that a firm can continue emitting a waste so long as another waste is reduced significantly by the activity (Social Change, 2006). Again the same phenomenon repeats itself whereby one pollutant is replaced by another.

Banking of emissions policy does not give hope to environmental sustainability either. Allowing firms to have credits permitting them to pollute beyond the maximum in the future is equivalent to postponing pollution. This puts more uncertainty on the sustainability of the environment even in the future. Not only is the future of the environment endangered by this policy but also the current time since the policy allows such firms to trade the credits to firms that would want to pollute above their limit.

    The effectiveness of trading pollution rights cannot be underestimated bearing in mind that some firms have successfully reduced pollutant emissions. It is also acknowledgeable that if firms were to seriously implement this policy, the great incentive for developing advanced technologies to clean the environment would be worthwhile in sustaining the environment. It is however worrying that instead of focusing on maintaining a sustainable world through control of environmental pollution firms have gone after profits blindly. High polluting wealthy firms have used their financial capability to buy off polluting power and forgotten their environmental responsibility of ensuring a sustainable world. Pollution permits are being traded from one firm to the other in a free market and firms seem to be competing on who can pollute most. It is even more worrying on the future of a better environment now that some companies can secure rights to pollute beyond their limit in the future. In essence, pollution rights do not effectively control environmental problems.

Copenhagen Climate Talks

The 192 countries meeting in Copenhagen in an attempt to hammer out a deal on combating climate change failed to reach any meaningful and quantifiable agreement. China and the USA, both responsible for 40  of the total global emission, are largely responsible for the state of affairs because of their mutual suspicion. During the talks, cost emerged as the biggest stumbling block to any international agreement. Economists have identified two types of costs that will arise in dealing with climate change. The first use will be in helping the fast industrializing countries such as Brazil and India convert to clean energy while the second use of the funds will be for helping poor countries cope with the negative effects of climate change. With the European Union having pledged to cut down its emissions by 20 by 2020, the onus is on China and the US to play their roles in combating climate change.

Topic With above average 2009, first decade of the 2000s is warmest on record
    The 2000-09 decade has now been found to have been the warmest on record. In particular, 2009 was found to have been 1.01 degrees above average, which makes the year the fifth warmest. This higher average of 2009 also helped push the decades average temperature to 0.96 above normal which surpasses a previous record held by the 1990s that stood at 0.65. This steep rise in temperatures is expected to bring about increased frequency of natural disasters, crop failure, disruption of wildlife patterns and loss of species that will be unable to adapt to the change. Last year also saw a number of climate milestones that included, winter drought in Texas, the worst tornado in Oklahoma, largest wildfire in Los Angeles County and many other unfavorable climate milestones. However, with all these tell tale signs the political leadership is still unable to hammer out a deal that would lead to a reduction of greenhouse gases.

ECONOMIC BENEFITS ENVIRONMENTAL IMPACT ASSESSMENT (EIA) OF THE PROPOSED CONSTRUCTION OF A SOLID WASTE TREATMENT PLANT

Economic benefits of the project
During the construction of the solid waste treatment plant, there will be employment opportunities for both professionals and unskilled workers. Several workers including casual labourers, plumbers and engineers are expected to work during the construction phase of the project. With labour intensive construction technologies, the project will provide employment for youths and also support to the Governments initiative on creation of jobs (Angerer, Heinzow, Reimann,  Lehnert, 2000). During the operational phase of the project, the facility will also be a source of employment to a number of people who will be engaged in collection, processing and disposal of wastes.

Through improved collection of solid wastes, recycling will be promoted. This will lead to the development of industries that will be involved in utilization of the recycled materials (Reid,  2010). In these industries, it is anticipated that there will be low cost of production and increase in returns since the production materials will be readily available as recyclables. These industries will economically empower a great number of people through the creation of employment. The gains from selling of the recycled materials to the industries will be ploughed back and used in the operation and maintenance of solid waste treatment plant (Department of Environment, Food and Rural Affairs 2009, Municipal Waste Management).

Overall, this project once implemented will reduce the uncontrolled dumping of wastes which often lead to wastage of materials that can be of high economic importance when recycled. A number of open dump sites will be rehabilitated for other economically viable projects which can lead to generation of incomes (Barbone, Stanta,  Lagazio, 1996).

2.0     Estimated cost of the project
The solid waste treatment plant which will be in the form of a sanitary landfill is estimated to cost  1,818,000. This includes the costs for detailed design of the treatment plant, site surveys and clearances, environmental impact assessment consultancy services, earth works, cell construction works, operation and maintenance, monitoring and evaluation, EIA licensing fees (Statutory Instruments, 2004). The cost break down for the treatment plant is as shown in Table 1.

Table  SEQ Table  ARABIC 1      Estimated cost of the project
COMPONENTESTIMATED COST ()Detailed design of the treatment plant  20,000Site surveys and clearances50,000Environmental Impact  Assessment ( EIA)  consultancy services 100,000Earth works 200,000Cell construction works 400,000Gas flare chambers, bio-filters  and support  facilities 200,000Operation and maintenance costs250,000Monitoring and evaluation costs 200,000Engineering consultancy services380,000Sub Total Costs1,800,000EIA licensing fees (1) 18,000GRAND TOTAL COSTS 1,818,0003.0     The need of the project

The overall objective of solid waste management is to protect the environment and human health through the proper management of wastes (Reid,  2010). The construction of a solid waste treatment plant is primarily intended to

Ensure proper management of solid waste that aim at reducing  any adverse impacts on the  public health and environment

Promote the reduction, reuse and recycling of solid wastes in environmentally sustainable manner (Statutory Instruments, 2004)
Reduce gaseous emissions to the atmosphere and enhance proper handling of leachate from the solid wastes and   

To protect against the undesirable impacts of uncontrolled waste disposal by ensuring orderly collection, processing and disposal (The Environment  Agency, 2010).

4.0     Environmental Impact Assessment (EIA) of the project
The objective of an environmental impact assessment (EIA) is to assess the proposed project with regard to the impacts on the environment, public health and safety (William,  Robinson, 1993). Thus, an EIA is a method of predicting the anticipated positive and negative impacts of the proposed project and determination of mitigation measures for the adverse negative impacts.

In the UK, environmental impact assessment (EIA) regulations of 1999 are implemented in the legislations through the Town and Country Planning Assessment of Environmental Effects. The directive requires that all types of developments that are likely to have significant environmental impacts on the environment be subjected to the EIA process (Bagchi,  Amalendu, 1990). The EIA study for this construction project involved the determination of environmental impacts and their mitigation measures, desk review of Government environmental regulations, evaluation of project alternatives and comparison of their environmental impacts. The topics covered under the EIA study are presented in the following sections (The Environment  Agency, 2010)

4.1    The likely environmental impacts of the project
The construction of a solid waste treatment plant requires development of various infrastructural works inform of access roads, site clearance and construction. This works will have significant environmental and social impacts (Dempsey,  Oppelt, 1993). The anticipated environmental impacts and their mitigation measures have been discussed in the following two phases of the project

Construction phase and Operation phase.
4.1.1    Impacts during project construction phase
4.1.1.1    Generation of noise
During the construction of the solid waste treatment plant, potential noise production will be due to the construction machinery during excavation works and delivery of materials to the project site.  Generation of noise would impact negatively on the construction workers and the local people. In order to mitigate the generation of noise, there would be the need for the project constructor to use the best available practices on-site to minimize occupational noise (UK Trade  Investment, 2009). The construction workers should also be provided with personal protective equipment such as the ear muffs.   

4.1.1.2     Dust emissions
The transport of construction materials, excavations and earthworks will lead to the emission of dust.  Dust is a form of airborne particulate matter and would negatively impact on the health of the construction workers and the local people within the proximity of the construction works. This would lead to respiratory problems and visual impairment. The generation of dust during the construction process would also interfere with traffic movement (The Environment  Agency, 2010).
In order to mitigate this impact, the project contractor will be required to ensure that excavation, handling and transportation of erodible materials be avoided during high windy conditions or when observable dust plume is present. Access roads and active construction sites which emit a lot of dust should be sprinkled with water on regular basis to keep off the dust.

4.1.1.3     Construction wastes
The generations of construction wastes will interferer with the aesthetic status and physical setting of the project area. Poor disposal of these wastes would result to pest breeding, pollution of water sources and informal recycling ((William,  Robinson, 1993).). Some of these wastes can cause physical injuries to the construction workers if not well managed (Bagchi,  Amalendu, 1990).
The project contractor will be required to reduce generation of wastes and also promote reuse and recycling. Any generated wastes should be properly handled and disposed off in a manner that is acceptable to the Environmental protection Act, 1990.

4.1.1.4     Loss of biodiversity
The construction of the solid waste treatment plant would lead to the loss and destruction of flora and fauna in the project area during exaction works and movement of machinery. It is anticipated that there will be changes in abiotic conditions, loss of endangered species and habitat fragmentation. Lower class animals and the insecta family will be highly affected in the process (Department of Environment, Food and Rural Affairs 2009, Municipal Waste Management). 
During the construction phase, there will be need to restrict machinery movement in the project area in order to minimize disturbance of flora and fauna. Once construction works are completed, there will be need to replant the lost vegetation.  

4.1.1.5     Workers accidents and injuries during construction 
It is anticipated that a number of construction workers are most likely to encounter injuries and hazards as construction works unavoidably expose workers to occupational health and safety risks. This risk of accidents and injuries can result from accidental falls, injuries from hand tools, poor handling of construction machinery and equipment usage (Mroszczyk, 2008). This impact on construction workers can be mitigated through the provision of appropriate personal protective equipment and safe and health operating environment for the construction workers. The workers should be trained on safe working practices and the need to use personal protective equipment. The project contractor should ensure that all equipment and machinery are tested for their safety before usage (Mroszczyk, 2008).

There will be need to monitor and report any occurrences of accidents and injuries during the construction process.

4.1.1.6    Changes in soil properties
Construction works will involve the use of heavy equipment and machinery for transportation, earth works and site clearances. This will lead to compaction of soils and thus alteration of soil structure and increase in soil bulk density. There will be poor infiltration rates in the soils and this will lead to increased run offs in the project area (UK Trade  Investment 2009, Information Sheet on Environmental Regulations in the UK).

The changes in soil properties can be mitigated by restricting earthworks to that land that is required for the works without necessarily disturbing adjacent land. The excavation works should be carried out during the dry spell to prevent soil erosion and compaction. Soil compaction and infiltration tests should be carried out in order to determine those areas that require soil breaking once construction works are completed.   

4.1.2    Impacts during project operation phase
4.1.2.1    Soil and water pollution
During the operation phase of the project, poor compost management practices would result to pollution of soil and water. Untreated leachate from landfills will pollute the surface and ground water resources and result into detrimental impacts on the ecosystem. Accidental leakages of used oil and chemicals would lead to the pollution of soil and water. The use of premature compost as organic manure will lead to addition of acidification of soil due to fermentation process. The increase in soil acidity would interfere with plant growth and uptake of minerals. Acids in the soils will interfere with the availability of important minerals required by plants. 

Best compost management practices should be employed during the disposal of biodegradable wastes to the treatment plant. Solid wastes should be thoroughly sorted before disposal in order to get rid of any toxic materials from finding their way into the compost (The Environment  Agency, 2010). The leachate from the landfill should be treated before discharging to the receiving water bodies and soils.  Encourage the use of mature compost in order to avoid further fermentation that would lead to increase in acidity levels in soil. 

4.1.2.2    Emission of noxious odours and gases
The emission of noxious odors from the solid waste treatment plant during the operational phase will lead to significant air pollution and human health impacts. The odors will originate from collection, transport, sorting and disposal of solid waste in the treatment plant. During transportation and sorting of wastes, gaseous fumes will be emitted from the waste delivery trucks and processing equipment. These gaseous fumes will be inform of methane, nitrogen dioxides and other forms of green house gases that contributes to global warming. Noxious odours and gas emissions will also cause health impacts to the workers and local people (Brereton, 1996).

In order to mitigate this impact, the waste delivery trucks should be kept in good working conditions so that they reduce the emission of gaseous fumes that can have detrimental impacts on public health and the environment.

The landfill should also be constructed to acceptable engineering standards and fitted with gas collectors and bio-filters that can reduce release of odors from the decomposing wastes.

4.1.2.3    Occupational health risks  
The anticipated occupational health risks include physical injuries and accidents while handling of solid wastes and operation of plant machinery. Other impacts will be inhalation of gaseous fumes during collection and processing of solid wastes (Mroszczyk, 2008). The mitigation of these impacts will involve provision of personal protective equipment to the employees who handle solid wastes. The employees should be trained on best solid waste handling practices that aim at safe handling and reduction of injuries while using different machinery and equipment while collecting, sorting and feeding of the wastes to the treatment plant. There should be a crisis management team that will handle and administer First Aid to the injured employees (Mroszczyk, 2008). The team should be trained on basic First Aid skills on regularly.

4.2    Government regulations
4.2.1    Framework for UK Government Environmental Regulations
The Department for the Environment, food and Rural Affairs (Defra) is responsible for protecting the environment which is the main key focus of the UK Government.  The Government has devoted to meet the Global targets that aim to reduce the environment impacts, including   the reduction of carbon-dioxide emissions by 80 by the year 2050. The government has a specific target of recovering 74 of the packaging wastes by the end of 2010 (UK Trade  Investment 2009).
The Institute of Environmental Management and Assessment (IEMA) is a competent body that has been established in the United Kingdom to promote best practice standards in environmental management. Their main focus is on promotion of sustainable development and capacity building of professionals in the environmental field.

4.2.2    UK EIA Regulations of 1999 (SI 1999 No. 293)
The environmental impact assessment (EIA) regulations are implemented in the Governments legislations through the Town and Country Planning Assessment of Environmental Effects. The directive requires that all types of developments that are likely to have significant environmental impacts on the environment be subjected to the EIA process. In the Part IV of the EIA regulations, there will be no implementation of a project that is likely to have a negative environmental impact unless an environmental impact assessment has been concluded and agreed in accordance with the provided regulations.

4.2.3    UK Environmental Information Regulations (EIRs) of 2004
The new Environmental Information Regulations (EIRs) of 2004 came into force in January 1, 2005. The Regulations gives a statutory right to access environmental information held in the public authorities and other bodies. The laid regulations in the EC Directive 20034EC and in the Aarhus convention bring the Government into line with the international requirements for public access to environmental information. 

This right to access environmental information is important in achieving sustainable environmental management though the promotion of transparency within the Government authorities.
 
4.2.3    General Health and Safety Regulations
The regulations that are applicable to the work places are as follows
Noise at Work Regulations of 1989 Requires employers to take action in order to protect the employees from hearing damages. This regulation will be applicable during the construction and the contractor will be required to provide ear muffs to protect employees from exposure to unacceptable noise levels (The Environment  Agency, 2010).

Provision and Use of Work Equipment Regulations of 1998 The regulation requires the use of safe machinery and equipment at the work place. This will act as a caution against any anticipated accidents and injuries during the construction and operation phases of the project (Mroszczyk, 2008).
Management of health and safety at work regulations of 1999 Specifies the need to carry out risk assessments and implementation of necessary measures that govern the management of health and safety. It is also a requirement in this regulation that competent people be employed and provided with appropriate training on safe operation of machinery. During the construction and operation phases of the solid waste treatment plant, qualified workers will be hired to operate machinery. Training will also be provided on the use of personal protective equipment and best working practices that aim at reducing accidents and injuries ( HSC, 2008).

Reporting of Injuries, Diseases and Dangerous Occurrence Regulations (RIDDOR) 1995 This is a health and safety regulation that requires notification of dangerous work activities, occupational injuries and diseases. It will be a requirement that during the operation of the solid waste treatment plant, all injuries and diseases be reported to the relevant authorities. The occurrences of injuries shall be monitored and reported throughout the project construction and operational phases (Mroszczyk, 2008).

Construction Regulations 1994 The regulation focuses on the design and management of construction sites. The project site will be demarcated and fenced off to prevent any unauthorized. The construction works will also be implemented to acceptable standards (Peavy, Rowe,  Tchobanoglous, 1985). 

4.2.3    Environmental Protection Act 1990
Part 3 of the Environmental Protection Act specifies the duty of the council to investigate any complaints that are related to odour and emissions nuisance that include smoke, gases, and hazardous fumes. In the act, the complaints are justifiable if the emissions affect public health and the environment.

Noise nuisance is covered by part III of the Act. The forms of noise complaints that are investigated include noise from construction works, vehicles and machinery among others. The Act empowers local authorities to deal with nuisance noise which is prejudicial to health and can cause any form of disturbance of life style.

4.3    Possible Project Alternatives
The evaluation of various project alternatives is a requirement in the UK Environmental Impact Assessment Regulations of 1999. This is an important step towards the selection of a viable and sustainable treatment plant for implementation. The main aim of the selection is to achieve solid waste disposal practices that are friendly to the environment and can meet the requirements of the present and future generation. Some of the considerations that are usually used in the determination of the best project alternative for implementation are economic, technical and environmental considerations of the available options.

The no project alternative considers a situation that will result if the project is not implemented. This alternative will maintain the current state of uncontrolled management and disposal of solid wastes in the open dump sites. This alternative is not considered legitimate and will continue the degradation of the environment due to the poor solid waste management practices. The anticipated economic impacts from recycling of the solid wastes will be lost.  For this study, the possible project alternatives are based on the conventional solid waste disposal methods that are widely applicable in the world. These alternatives include sanitary landfilling incineration and pyrolysis.

4.3.2     Sanitary landfilling
Sanitary landfilling is one of the widely used means of solid wastes in the UK. This method of disposal involves stacking of sorted wastes in a well designed and engineered landfill (Bagchi, J  Amalendu, E 1990).  The stacks of solid wastes are compacted to increase their density and stability. With proper sorting of the solid wastes before disposal in the landfill, the composted material can be a good source of organic manure. The quality of the organic manure will be affected by the level of impurities in the untreated solid wastes. Decomposition of the landfill wastes leads to the emission of leachate and green house gases (GHGs) such as methane and carbon dioxide. These will significantly impact on the environment and human health if the landfill is not properly designed and constructed. This alternative is considered appropriate for treatment of solid wastes due to the low initial capital and management costs. Secondly, disposal of solid wastes in the landfills is one of the major practices in the country. Hence, this alternative will be accepted by the concerned authorities and stakeholders responsible for solid waste management in the country.  An overview of a well designed landfill is as shown in figure 1 below

4.3.3     Incineration
Incineration is a form of thermal treatment processes that involves burning of solid wastes. Solids, liquids and gaseous wastes are disposed of through incineration method.  The major shortcoming of incineration is the emission of harmful pollutants that are in the form of stack gases, ashes and some other residue (The Environment  Agency, 2010). This method is not appropriate for large scale disposal solid waste due to high initial and running costs. The environmental and social impacts associated with incineration are not easy to mitigate due to high toxicity levels. Thus, this alternative was not considered.

4.3.4    Pyrolysis
This is a method of solid waste treatment that involves the conversion of wastes into gaseous, liquid and solids (Peavy, Rowe,  Tchobanoglous, 1985). The process involves loading of wastes into an enclosed vessel where they are anaerobically exposed to heat. In this technology, wastes are cooked to produce gaseous emissions that are then used as fuel for the treatment process of solid wastes. The products from pyrolysis process are in the form of liquid fuel and solid substances that resemble goal.
This alternative is one of the most expensive methods to implement and requires high operation and maintenance costs for it to sustainably manage solid wastes (The Environment  Agency, 2010).

4.4    Comparison of the environmental consequences of alternatives
4.4.1    Environmental consequences of sanitary landfills 
The decomposition of the landfill wastes leads to the release of considerable quantities of methane and leachate. The emission of methane gas which is considered as one of the green house gases (GHGs) would significantly contribute to global warming. The leachate from the landfill can leak and penetrate through the underlying strata and thus polluting the soils and underground water (Reid, 2010). This leachate can contain harmful contaminants which can impact negatively on the environment and human health (Reid, 2010).  

4.4.2     Environmental consequences of incineration
The incineration process leads to the generation of wastes in form of stack gas emissions, fly ashes and ash that is inform of slag that are deposited at  the bottom of incinerator. All the incinerators release such chemicals as volatile organic compounds (VOCs), dioxins, benzenes and heavy metals such as lead and mercury (Dempsey,  Oppelt, 1993). Most of these hazardous chemicals are known to be resistant to degradation in the ecosystem.  Their build up in the tissues of organisms leads to undesirable diseases and genetic mutations. Exposure to heavy metals from the incinerator would also lead to heart diseases, cancers and allergic conditions (Barbone, Stanta,  Lagazio, 1996). The dust emitted from the incinerator may be deposited in the surrounding grounds and this will lead to substantial pollution of soils and water sources.

These wastes may contain significant quantities of toxic substances that can impact negatively on the incinerator workers. Eikman (1994) argues that the greatest potential for exposure of the toxic compounds is during cleaning of the incinerator. The dioxins and other compounds in the wastes are also absorbable through the skin, thus posing great risks to the health of workers. There will be need for the workers to use high quality personal protective equipment that will minimize exposure to the incinerator wastes. 

4.4.3    Environmental consequences of Pyrolysis. 
Pyrolysis leads to the emission of harmful fumes which can cause adverse impacts on the environment. The gaseous fumes from this method contain high levels of carbon dioxide.  Carbon dioxide is one of the green house gases and continuous accumulation in the atmosphere will lead to the significant impacts associated with global warming. The use of pyrolysis will undermine the governments commitment towards meeting the global targets that aim to reduce the environment impacts, including   the reduction of carbon-dioxide emissions by 80 by the year 2050 (Department of Environment, Food and Rural Affairs, 2009,).

Non-technical summary
This assignment on environmental management project is on the economic benefits and the environmental impact assessment of a solid waste treatment plant (The Environment  Agency, 2010). The environmental impact assessment has been prepared to address the likely environmental impacts and mitigation measures of the project construction and operational phases. This section also covers a review of relevant government regulations to the project, analysis of project alternatives and comparison of the environmental impacts of the alternatives (Eikman, 1994). Some of the economic benefits anticipated from the construction of the project include creation of employment and increased incomes from recycling of solid wastes.

The solid waste treatment plant is intended to (1) ensure proper management of solid wastes that aim at reducing any adverse impacts on the public health and environment (2) promote the reduction, reuse and recycling of solid wastes in environmentally sustainable and friendly manner (3) reduce gaseous emissions to the atmosphere and enhance proper handling of leachate from the solid wastes and (4) protect against the undesirable impacts of uncontrolled waste disposal by ensuring orderly collection, sorting , processing and disposal.
As required in the Environmental Impact Assessment process, some of the Government regulations reviewed included
Management of health and safety at work regulations of 1999
Provision and Use of Work Equipment Regulations of 1998
Noise at Work Regulations of 1989
UK Environmental Information Regulations (EIRs) of 2004
UK EIA Regulations of 1999 (SI 1999 No. 293)
Reporting of Injuries, Diseases and Dangerous Occurrence Regulations (RIDDOR) 1995
Construction Regulations 1994
Environmental Protection Act 1990
The anticipated environmental impacts and the proposed mitigation measures associated with the project construction and operational phases are as shown in Tables 1 and 2.  The applicable Government ActsRegulations for each of the identified environmental impacts are also presented (The Environment  Agency, 2010).

Table  SEQ Table  ARABIC 2 Summary of anticipated environmental impacts and their mitigation measures during the construction phase of the solid waste treatment plant
Environmental ImpactsApplicable Government Acts Regulations Proposed Mitigation MeasuresGeneration of noiseNoise at Work Regulations of 1989The project constructor to use the best available practices on-site to minimize occupational noise.
The construction workers should be provided with personal protective equipment such as ear muffs.    Dust emissionsEnvironmental Protection Act 1990
Management of health and safety at work regulations of 1999
excavation, handling and transportation of erodible materials be avoided during high windy conditions
Ensure that dusty access roads are sprinkled with water to keep off dust Construction wastesConstruction Regulations of  1994
Environmental Protection Act 1990The project contractor to reduce generation of wastes and promote reuse and recycling.
Handle and dispose of generated solid wastes in acceptable waysLoss of biodiversityConstruction Regulations of  1994Restrict machinery movement in the demarcated project areas in order to minimize disturbance of flora and faunaWorkers accidents and hazards during construction  Reporting of Injuries, Diseases and Dangerous Occurrence Regulations (RIDDOR) 1995
Management of health and safety at work regulations of 1999
Provision and Use of Work Equipment Regulations of 1998Train construction workers on safe handling practices and the need for using personal protective clothing
Project contractor to ensure that construction machinery and equipment are in good working conditions all the times. Changes in soil propertiesConstruction Regulations of  1994Control and restrict earthworks to demarcated areas without necessarily disturbing adjacent land
Restrict excavation works to dry spells in order to prevent soil erosion and compaction.
Carry out soil compaction and infiltration tests to determine those sites that have to be rehabilitated after compaction.

Environmental ImpactsApplicable Government Acts Regulations Proposed Mitigation MeasuresSoil and water pollutionConstruction Regulations of  1994Promote best landfill management practices
Ensure sorting of wastes to be used for compost
Provide leachate collection pond in the design
Mature compost material should only be used as organic manure
Ensure proper monitoring of compost Emission of noxious odors and gasesEnvironmental Protection Act 1990Regularly service solid waste collection trucks to reduce emission of gaseaous fumes
Ensure proper operation and maintenance of the landfill
cover the landfill and include gas traps in the designOccupational health risks   Provision and Use of Work Equipment Regulations of 1998Train the personnel on best solid waste handling practices
Form a crisis management team and train on basic  First Aid skills

On project alternatives, the conventional solid waste disposal methods discussed included (1) Sanitary landfilling (2) incineration and (3) pyrolysis. Sanitary landfilling which is widely used in the UK was considered the best alternative for solid waste treatment due to its low initial capital and maintenance requirements. The environmental impacts of a sanitary landfill can easily be mitigated as compared to incineration and pyrolysis through proper designs and construction works (The Environment  Agency, 2010). Provision of gas traps and leachate ponds in the land fill are considered the most important requirements to minimize emission of methane and pollution of ground and surface water by the landfill leachate. The no project alternative is not desirable as there will be continued degradation of the environment due to the uncontrolled disposal of solid waste. For this alternative, the anticipated economic benefits from recycling of solid wastes will not be achieved.  The no project alternative will undermine the Government specific target of recovering 74 of the packaging wastes by the end of 2010.

Water Quality Management

Urbanization can essentially lead to Storm water pollution because of a number of reasons. Primarily, urbanization leads to more developmental infrastructure, such as parking lots, buildings, compacted soil, roads etc, thereby inhibiting the natural absorption of rain water into the ground (Guidance Manual for Developing Best Management Practices (BMP) 1993). This eventually leads to the accumulation of water on the surface which can cause the deterioration of water courses such as streams and rivers. Also, it can be the major cause of flooding if the stormrain water management system is inadequate (Trimble 2007). The accumulation of the water in itself is not the only problem in the sense that pollutants, deposited by human beings, are absorbed into the accumulated water which then seeps into the ground eventually polluting water supply under the surface as well as a river, lake or an ocean.

Storm water pollution can be a significant problem for public health in the sense that polluted water that eventually is absorbed underneath the surface or runs off into a river, lake or ocean primarily contaminates major human water supply (Trimble 2007). It can also significantly affect agriculture because polluted water absorbed by underground streams eventually leads to less arid soil as well as the fact that agricultural produce grown on such soil and the use of water from contaminated underground streams can result in crops and eventual food products to adversely affect people that consume those products (Schueler 2000). In some places, because of poverty, the only source of drinking water for people is through lakes and streams. Polluted rain water can eventually contaminate these sources of water thereby leading to various diseases and health problems.

Best Management Practices are primarily a concept developed by the United States in order to curb water pollution. It basically refers to ways through which a certain environmental protection agency works specifically to develop programs that deter pollution that is caused essentially through water. A BMP programs in regards to storm water management basically includes measures taken to change the condition of as well as the amount of urban run-off that occurs because of rapid urbanization (Guidance Manual for Developing Best Management Practices (BMP) 1993). One of the best BMP programs in regards to the appropriate management of storm water is treatment train which refers to the use of a number of physical storm water procedures in order to improve drainage water quality (Schueler 2000, Guidance Manual for Developing Best Management Practices (BMP) 1993).

One of the most important factors that can affect any storm water management program is the financial backing behind it. Firstly, initial finances will be used in order to setup the infrastructure that is required for the program to work with maximum efficiency and then eventually more injection of monetary aid would be needed in order to maintain the level of efficiency that is required. Therefore, a proper budget needs to be setup in regards to the successful working of an storm water management program.

Water Quality Standards and Criteria

Water Quality Standards defines the goal for a water source by its uses (as drinking water or for agriculture purpose), and criteria to protect those water bodies from pollutants. Water Quality Standards are set Clean Water Act. The Clean Water Act develops criteria for water quality that accurately reflects the latest scientific knowledge according to the Section 304(a) (1).  These criteria are based solely on data and scientific judgments on pollutant concentrations and environmental or human health effects. This act also provides guidance in adopting water quality standards. Water quality Criteria developed for the protection of both aquatic and human health. Clean Water Act came into existence from 1972, which established the structures for controlling the discharge of pollutants into US waters.  It became a law for protecting the rivers and lakes from different pollutants that are associated with agricultural, urban, and suburban activities, forest harvesting, mineral extraction, and atmospheric deposition. Both water quality standards and criteria are an important in clean water program.

This provides information about water quality and also for improving that quality, provides standards for toxic levels in water for protecting aquatic life etc. water quality standards and criteria are the foundation for a wide range of programs under the Clean Water Act. This strategy contains priority strategic actions that the Office of Science and Technology will undertake in collaboration with other EPA offices, states and authorized tribes over the next six years to strengthen and improve this foundation. All waters of the United States will have water quality standards that include the highest attainable uses, combined with water quality criteria that reflect the current and evolving body of scientific information to protect those uses. Further, standards will have well-defined means for implementation through Clean Water Act programs.

Food Security in the Middle East

The Middle East region has been faced with various challenges that are associated with food security. These are perpetuated by water scarcity, an increase in the population numbers in the region, climate change and unemployment. Notably, these factors are intricate and self augmenting and thus, the problem is very complex. Most recently, the theory of virtual water has been proposed as the best approach of addressing this scenario.

However, this study found out that various social, cultural, economic and political factors undermine its implication. The present trends indicate that the region is highly dependent on food imports and that the trend is set to increase in future. Besides highlighting the various challenges that the region faces in a bit to attain food security, this study presents viable approaches like the population control and the increased education levels and awareness creation that can be used to address the challenges in a sustainable manner.

Most challenges, that the population of the Middle East grapples with, emanate from weather related complexities. Of great reference in this regard is the food insecurity that threatens the very survival of the population. Essentially, about sixty percent of the region is considered to be hyper arid or arid. As such, food production in the region can not be entirely dependent on rain fed agriculture. Arguably, the region is considered to be experiencing the largest food deficit than any other region across the globe. This presumption is based on the increase in imports with regard to cereals for consumption. In this respect, the World Bank (2008) ascertains that apart from Syria, the remaining countries have consistently featured on the worlds greatest cereal importers chart since 2006. A comparative study carried out by Yemtsove (2008) indicated that in the year 2007, the amount of cereals imported by the region is equivalent to 2.9 billion cubic meters of water.

The increase in cereal imports is attributed to the rapid population growth being experienced in the region. Notably, the countries can be considered to have the fastest rates with regard to the populations growth. In addition, it is posited that the rising imports haves being experienced across the globe has also contributed to increased consumption of cereals in the region. This situation has further been compounded by the scarcity of water in the region. According to Naff (1995), this is the top most reason as to why food production and the overall food security in the region is at stake.

Food Security Present Trends
Numerous studies, including Dyson (2006), indicate that the food security situation in the Middle East continues to face various challenges. In the recent past, the region has experienced an unprecedented rise in food prices. This is because of lack of water that makes agricultural production very costly. The food production is further compounded by the long term neglect of agricultural production by the government. Initially, the food importation was less costly and as such, governments could cheaply import food, subsidize the same and avail it to the population at affordable prices. However, this has long changed as global food prices have increased significantly. More than ever, governments are finding it expensive to import food and subsidize the same accordingly. This is even more difficult for countries like Jordan, Egypt and Palestine that have low levels of income (Dorosh, 2008). The implications of rising food prices have been far reaching. In particular, Dyson (2006) indicates that this has led to instability that as been manifested through riots in Egypt and Jordan. This has even made the population more vulnerable as extremist groups use the opportunity to win the confidence of the citizens by offering subsidized services.

Indicators of Food Security
Global surveys have previously employed vital indicators in their classification of countries as either being food secure or insecure. In particular, food aid and the proportion of cereals consumed domestically are the key indicators of foods security. The latter is usually derived from the imports of a country. In this respect, it is believed that countries that tend to import more grays are usually at a higher risk of food insecurity in instances where global reserves decrease. Relatively, national wealth is also an indicator that has been used to determine the status of food security across the globe. In this regard, FAO (2009) posits that a wealthy country has the capacity to cater for its food requirements in a sustainable manner. This is regardless of the fact that the domestic consumption may constitute a great percentage of imports. In addition, Mrabet (2006) argues that the wealthy countries are usually cushioned from the negative implications of food insecurity and are unlikely to have a shortage of grain supply. In most cases, they are able to survive even in cases were the prices soar as they can easily make higher bids when the markets become competitive.

Food Aid
In this respect, Benson, Minot, Pender and Robles (2008) ascertain that food aid is the most obvious indication of food insecurity in a give region. Fundamentally, it is believed that any country that opts for food aid has supply problems.  Notably, six of the nine countries found in the Middle East have relied on food aid in 2008. Iran and Syrias pertaining to food aid have been considered to be insignificant at a national level because they were less than 0.15. However FAO (2008) considers Yemen and Lebanon to be middle size recipients of aid. In particular, 2.4 and 2.9 of Lebanons and Yemens domestic food consumption was attributed to food aid respectively. Then, Jordan and Palestine are considered to be the biggest beneficiaries of food aid in the region. Since 2008, FAO (2009) indicates that food aid in Palestine has risen to constitute 32 of the total consumption. Seemingly, Jordan also received a significant 15 of food aid in 2008.

Cereal Imports
In this regard, the countries are categorized in to three main classes those whose imports make up less than 50 of the national cereal consumption, nations whose imports make up 51-84 of its domestic consumption and finally, those whose imports constitute 85 of the domestic consumption. Notably, the first group is comprised of only two countries, Syria and Iran. According to FAO (2009), imports in these countries constituted only 10 and 30 respectively of the entire domestic consumption during 2008. Likewise, the second group constitutes two countries that include Yemen and Saudi Arabia. In particular, Saudi Arabia had 66 of its domestic consumption being comprised of imports while Yemen had 75 of its cereal consumption comprising of cereals (FAO, 2009). The remaining six countries constituted the third category.

Wealth levels
With regard to the wealth levels, FAO (2009) argues that the wealth levels in the region differ considerably. In particular, it indicates that Kuwait, the UAE and Saudi Arabia and Israel have been cited to have per capita incomes that are above 10,000. Then, Syria, Iran, Jordan and Lebanon are considered to have moderate incomes that range between 3000-7000. Finally, the population in Palestine and Yemen is considered to be on the lower side with its income ranging between 730 and 800 respectively (FAO, 2009).

Based on the above indicators, it is important to acknowledge that food security amongst countries in the Middle East vary considerably. Notably, the UAE, Kuwait and Saudi Arabia exhibit a high degree of food security. This is regardless of their high dependence on imports. The stable food status can be attributed to their relatively high income levels that empower them to purchase all their food requirements. This is augmented by the stable global market. Further, recent trends indicate that despite the fact that Saudi Arabia has experienced an upsurge in its population, it has been able to reduce its dependence on food imports.  In addition, Iran and Syria can also be considered food secure as they produce relatively high amounts of cereals than their counterparts.  Lebanon is considered to have a low status with regard to food production because of its over reliance on food aid. In addition, it also relies heavily on food imports. Seemingly, Palestine and Jordan can be considered to be food insecure. Palestinians in particular have the lowest income levels, are dependent on food aid and rely heavily on imports too.

Imports Vs Exports in the Middle East
There exists a sharp contrast between the imports and exports in this region. Essentially, Rutan (2002) contends that there has been a significant rise in imports as compared to the exports. In particular, wheat and other types of cereals have been identified to be the main types of food that are imported in the region. Statistical evidence indicates that in the period between 2008 and 2009, wheat constituted a significant 22 of the total imports. Barley on the other hand constituted 25 of the total imports in the region. In addition, it is indicated that the region is also a major importer of vegetable oil and other oil meals. In particular, this assumed close to 12 of the total imports between 2008 and 2009. Further, FAO (2009) indicates that these rates are expected to increase in future.

Notably, the increase in population growth and the diversification of the same has also led to diversification of diets and increasingly, more animal and dairy products are being consumed than in the past. In addition Gleick (2000) affirms that increased urbanization has also resulted in to the change in dietary patterns. The urban population is believed to prefer refined food, livestock and dairy products to grains and cereals.

An increase in imports in the region has been attributed to the increased demand for food and the decrease in the resources employed in the production of the same. Statistical evidence asserts that the imports have increased from 36.4 in 2000 to close to 44.2 in 2007 (WHO, 2008). This implies an estimated 3.5 rise in the imports. They are led by cereals and feed grains, then followed by cotton, tobacco and finally dairy and livestock products.  In his review, Cline (2007) indicates that the region also exports fruits, nuts, cereals, feed grains and vegetables. Currently exports constitute around 34 of the total production. These are mainly destined for the European Union countries, apart from a few vegetables and fruits.

The current state of food insecurity in the Middle East is further threatened by the implications of climate change. According to the report presented by the Food and Agriculture Organization (2009), climate change is likely to have more grave implications on food production in this region. These according to the report will hit the local farmers who entirely rely on rain fed agriculture the hardest. The four main facets of food security that are likely to be affected include food availability, accessibility, stability and utilization. As such, the population affected is expected to suffer from malnutrition and other nutritional related disorders. In particular, FAO (2008) indicates that the shifts in rainfall patterns are likely to avoid local production of vital staples like wheat and rice. This implies that here is a likelihood that the amount of food available to the population will decrease. Countries such as Yemen and Palestine have been particularly singled out to be at the highest risk because of the increase in population growth, low income levels and acute water shortages.

With regard to the food availability, climate change has had adverse implications on the fundamental elements employed in food production. The rural population is considered to be the most affected by various relative factors such as loss of livestock continued crop failure and reduced availability of natural resources from fisheries and forests. In addition, the change in weather patterns has culminated in an emergence of new and resistant pests and diseases that affect crops trees and animals. This has had direct negative effects on the quantity and quality of food and has led to a rise in food prices (WHO, 2008).

Further, the extreme weather conditions that are related to change in weather patterns has had various impacts on the assets and sources of livelihood of both the urban and rural populations. These have greatly threatened the supply of food in the region. In this regard FAO (2009) indicates that the countries in the Middle East are continuously struggling with prolonged droughts, increased intensity of rainfall and other implications associated with irregular weather patterns. Decrease in availability of food and water is likely to lead to sanitation problems and incidences of malnutrition. From the sociological standpoint, this would increase the incidence of conflicts and increase tensions between communities as they migrate to other regions in search of food (WHO, 2008). The concept of the newly hungry has also been cited by World Bank (2008) to be a result of climate change. This is attributed to the decrease in food production and the subsequent increase in prices of the food. As a result, there exists a segment of the population that has sufficient financial resources but can not afford food because of the increased prices. This will lead to an increase in nutritional disorders.

Addressing Virtual Water
As indicated earlier, the water problem in the Middle East is really pronounced. The region has very few water resources that are available for production. Presently, it is indicated that 60-80 of the available water resources are employed in Agricultural production (Benson et al., 2008). It is certain that water is very elemental in environmental wellbeing and economic prosperity. However, the Middle East experiences a significant shortage of this vital commodity. Although FAO (2009) demonstrates that water shortage problems are being experienced on a global scale, it is notable that the Middle East is the worst hit by this predicament. In this respect, the region is considered to have a high percentage of arid land and receives very little rainfall. Likewise, the demand for water in the region is increasing notably because of the invariable increase in population growth. This has led to a strain in water resources that are already limited. Current statistics show that 16 of the population lacks safe drinking water. Further, they show that more than 80 million persons in the region lack proper sanitation (FAO, 2009).

Furthermore, certain countries in the region compromise the availability of water by over mining, irrespective of the fact that the water resources therein have already been over exploited. Shortages are further compounded by incidences of water pollution that are related to contamination by pesticides and fertilizers, huge deposits of solid wastes along river banks, dumping of industrial as well as municipal wastes in the rivers and other sources of water and uncontrolled and persistent seepage of wastes from and fill. In this regard, Dyson (2006) asserts that not only do these wastes contaminate the fresh water resources, but they also expose the already vulnerable population to health risks.

With the projected increase in population, the demand in water resources is set to increase significantly. Statistics indicate that if population growth continues unabated, the countries will have only enough water for domestic production by 2030 and none for Agricultural purposes (FAO, 2009). This condition is likely to make it difficult for the region to assure its population of food security. The best option in this regard lies in the importation of affordable virtual water. This takes the form of viable food staples and is instrumental in assuring the region of food security.

Employment of virtual water refers to the importation of the consumption foods that require significant quantities of water to produce (Naff, 1995). These often take the forms of staples and can be easily shipped and stored for long periods of time. They are sourced from countries that have plenty of water from natural sources as well as arable land for food production. These staples include food oil, dried grains, dried beans, fodder and frozen fish and meat products. They are then stored in silos, cold storage facilities and warehouses. Buchwald and Shuval (2000) indicate that this presents a more sustainable and cost effective method of ensuring a steady food supply for the population in the region. This can then enable the countries to engage in minimal agricultural production to cater for the vegetables and salad needs. Comparatively, this requires less water than domestic production of cereals.

In his review, Cline (2007) ascertains that usually, the global market is characterized by huge amounts of water. For instance, it is indicated that in order to grow a ton of cereals, 1000 tones of water are required. Basically, this is the virtual values of water contained in grains. Likewise, producing one tone of maize or rice requires 1200 tones of water. World Bank (2008) indicates that since virtual water is intrinsically inclined in the political economy, every country has a right to trade in the same. Virtual water is considered very important especially because countries can not domestically provide for all their food requirements. It is in this respect that virtual water is considered very instrumental in curbing food insecurity. Participation in international trade implies that basically, all countries export and import virtual water

However, Buchwald and Shuval (2000) point out that the segment of the population that entirely depends on agricultural production as a form of sustenance is likely to suffer. In this regard, it should be acknowledged that there is part of the population in rural areas of Palestine, Israel, Syria and Jordan that derives its livelihood from agricultural production. However, Ruttan (2002) argues that the region is experiencing a transition from an economy that is fundamentally based on quasi agriculture to an economy that is entirely based on commerce, tourism and trade. In particular, Agricultural production is Israel has been cited to comprise of an insignificant 2 of the total Gross Domestic Product. In addition, World Bank (2008) posits that the participation in Agriculture in the region is driven by strife as a result of the current political situation and lack of employment opportunities in other sectors of the economy. It is also ascertained that the level of employment in the commercial sectors of the society are increasing. Viable prospects in this respect have been experienced in the tourism sector especially as the region attained its peaceful status.

However, the countries in the Middle East are likely to experience various challenges even when utilizing the virtual water concept. In the global market, Dyson (2006) points out that these countries are always at a great disadvantage because of various reasons. To begin with, they do not have sufficient resources to effectively compete with the farmers in the north who are provided with Agricultural subsidies. This implies that the cost of production at a local scale is likely to supersede the prices provide by the international markets. Then, Yemtsove (2008) indicates that the harsh climatic conditions do not allow them to practice large scale production like their counterparts in the temperate regions. In order to practice expansive agriculture, these countries tend to mobilize significant volumes of their water for irrigation. Usually, this happens at the expense of great environmental, economic and social costs.

A classic example in this regard is exemplified by the situation in Jordan. It is indicated that this country imports an estimated 6 billion cubic meters of virtual water on an annual basis (Buchwald  Shuval, 2000). Considering the fact that it has scarce water resources, it often imports Agricultural products that require huge quantities of water to produce such as wheat. Further, it exports services as well as products that need less water to produce as a strategy to relieve the unprecedented pressure on its water resources. Nonetheless, it still allocates close to 70 of its water to agricultural production. At this juncture, it can be noted that if Jordan reduced its water allocations and other levels of support, the result would have adverse implications on its food import strategy. In particular, food prices would possibly rise, resulting in to reduced calories for its poor population. Of great importance would be its inability to raise sufficient capital to cater for its import costs.

Another constraint that undermines the application of virtual water is the risk that increased food production is likely to compromise the political independence of the country. In this regard, Word Bank (2008) indicates that the notion of self sufficiency has always been at the core of policies of the countries this region. As such, any talks pertaining to water scarcity tend to be politically sensitive. Further, the environmental implications of adopting the virtual water strategy are massive. In particular, abandoning of the rural areas and allocating available water resources to the urban population is likely to make the countries loose their vegetation cover. Seemingly, this has negative impacts on wild life that would spill over to the tourism industry. Moreover, FAO (2008) ascertains that it would have discounting effects on the level of oxygen and carbon dioxide. In particular, it would increase the levels of carbon dioxide in the region and lead to climate change.

It is also indicated that the religious constraints prevent the holistic implementation of the concept of virtual water in the region. In this respect, Mrabet (2006) indicates that religious regulations are widely employed in charging water. The holy Quran directs that water resources should be shared with individuals who can not afford the same. In addition, religious teachings that are strictly adhered to by the population teach that people are partners with all forms of energy resources. Considering the fact that farmers in the rural areas of the Middle East are poor and entirety depended on rain fed agriculture, respective governments might find it difficult to alter the situation as it could disadvantage the farmers.

However, it should be appreciated that with the population in the region rising steadily, it is possible that food security would be affected. In addition, the probability that the increased population is likely to settle in urban areas is high. Subsequently, the demand of water in the urban areas is likely to rise because of an expected rise in the standards of living. Furthermore, Cline (2007) cites that most of the water available in the region is used for production of low value food crops at the expense of critical industrial demands and the need for production of high value food crops. Statistics also show that the municipal water in this region is often unaccounted for. It is against this background that it is argued that in order to meet the emergent needs of the rapidly growing population, there is need to reallocate the fresh water resources employed in Agricultural production to the domestic urban sector.
Notably, a viable solution does not lie in charging the rural farmers of the water they use or pushing them away from agricultural production. Rather, WHO (2008) indicates that the region needs to invest in technological advancements such as drip irrigation. These are instrumental in sustainable utilization of the available water.

Future Projections
The level of food prices in the Middle East in future is largely unknown. However, economic models ascertain that the demand of food in this region is likely to outpace the supply. Thus the current dependence of the region to imports is set to continue in to the future. This will ultimately increase the vulnerability of the region to food price shocks that are related to global production. In particular, it is projected that the dependence on grain imports will possibly increase by 63 by 2030 and further exacerbating the food deficit being experienced in Middle East (FAO, 2009). It is also posited that the increase in dairy and meat imports is also likely to increase in future. World Bank (2008) indicates that the driving force behind the increase in the net imports in the region will be increases population growth and low income.

The Way forward
The main challenge to curb food insecurity in this region should be based upon the need to increase food production and appreciate the increased reliance on food imports at the same time. In order to enhance sustainable living therefore, food production needs to be given a priority. One of the most viable approaches to this is to emulate the action that was undertaken by Brunei during the 1970s. After realizing that it is incapable of producing sufficient food for its population because of harsh climatic conditions, Brunei government purchased huge chunks of land in Australia. Food produced therein was imported to Brunei to complement local production. As a result, the country significantly reduced its dependence on foreign markets (Benson et al., 2008). As such, it became less vulnerable to the implications of fluctuations of food in the international market. Notably, part of the population in Saudi and Kuwait has assumed this trend and is scouring places in distant countries like Sudan. However, it is posited that this can easily lead to resentment by the natives who perceive the investors as intruders.

In order to address the problem of the population growth, there would be need to increase the accessibility of the population to effective family planning services. Present statistics indicate that this region has among the highest population growth rates in the world. Failure to intervene accordingly is likely to lead to doubling of the population by 2050.  This has various implications n the food security problem including increasing the need for food imports and increasing public food subsidy costs. Further, Dyson (2006) indicates that the population needs to be well educated about the importance of consuming a balanced diet. Healthy diets according to WHO (2008) are instrumental in reducing incidences of health problems such as malnutrition and non communicable diseases. This would goes a long way in cutting down the nations costs and channeling the resources to other projects geared towards social development.

In his review, Gleick (2000) indicates that there is an urgent need to diversify the economy in the region.  This is based on the realization that the oil reserves are dwindling and the world is moving towards the post oil era.  In addition, the decision of the International Oil Agency to invest in alternative sources of energy in a bit to curb global warming by 2050 is threatening global oil consumption. Furthermore, unemployment levels in the region are very high. This affects the level of income of the countries in the region. It is in this consideration that it is considered viable to diversify the regional economy away from oil. This will enable the locals to be able to cushion themselves against the implications of unemployment and beyond oil age era.

Furthermore, World Bank (2008) proposed the need for the region to invest in food production. In this respect, it is argued that investing in Agriculture has the capacity to diversify the economy and reduce unemployment. Then, Dyson (2006) argues that most governments are strategically working towards increasing food production. This has been influenced by the increase in the global population that has put pressure on the available resources. While it would be difficult for the region to cope without oil, Mrabet (2006) contends that it would be virtually impossible for it to survive without food.

However, it is worth acknowledging that agricultural production is limited by the harsh weather conditions. Indeed, Yemtsove (2008) indicates that the scarcity of land and water undermines extensive agricultural production. Since there is limited room for possible irrigation andor expansion of arable land, there is an urgent need to lay greater emphasis on increasing the productivity of food with regard to yields and value of the food per unit of water and land. In order to attain this, the region is faced with the challenge of investing immensely in research, technology transfer and extension.

Another logical solution to addressing the problems of effective agricultural production is for the region to adopt the virtual water theory (Buchwald  Shuval 2000).  For instance, in the case of a country like Jordan, the Jordan valley is suitable for Agricultural production. Compared to the rest of the country, this part has warm temperatures, fertile land and a suitable environment that supports production of food crops at a low cost. In this case therefore, the respective government needs to allocate sufficient financial resources in the Agricultural sector. Further, farmers in this region can be exposed to the modern water saving strategies, equipment, planning methods and high value crop patterns. In this case, the areas are likely to continue being productive as the government gradually reallocates the remaining sources of water to the urban areas.

In addition, Cline (2007) indicates that the region needs to consider other options that when employed would improve the efficiency of irrigation, pursue intensification possibilities and enhance the overall agricultural yields in both rain fed and irrigated agricultural production. More so, the region needs to exploit production of less water intensive but high value crops such a palm trees. Notably, these have a high market value as compared to the low value food crops produced in the region. WHO (2008) asserts that the promotion of this form of production is likely to take the virtual water theory politically acceptable.

Further, is it notable that since the region is likely to remain a key player in the import market, it will possibly continue being exposed to the implications of rising prices and the risks of thin markets. Nevertheless, the levels of these risks vary considerably in line with the ability of the country to enhance domestic production and the amount of resources that the country has. It is in his consideration that it is indicated that each country needs to domesticate the risk management strategies to ensure that they are applicable to its local needs. Primary strategies in this regard include improving the efficiency of a countrys supply chain in order to improve distribution and cut down costs, developing virtual stockpiles to address the quantity risk and investing heavily in infrastructure employed in production, storage and transport of food in order to reduce the exposure to incidences of cereal import volatility.

Also, it should be appreciated that water is fundamental for the food production and therefore influences food security too. Thus, the Middle East needs to adopt, implement and enforce a sustainable long term plan to address water scarcity. In addition, it needs to create viable policies that would be instrumental in not only addressing the problem of water scarcity but also changing the mindset of the youngest generation of farmers. In particular, this young generation needs to be trained and exposed to the education system that would effectively prepare them for alternative productive occupations that are readily available in the tourism, commercial, trade and industry sectors. Dyson (2006) argues that changing of the mindset should also be extended to the entire society. The academic society and the media should in this respect be employed in enhancing changes in attitude In particular these bodies should oversee the implementation process and enhance political support for the theory. Increased public awareness in this regard can be achieved through campaigns, workshops and seminars that are meant to educate the public about the importance of the strategy. In order to yield optimal results, FAO (2009) indicates that this plan needs to be self initiated, well financed and well planned in to different phases that can be implemented with ease.

More over, it would be imperative to ensure that the virtual waters are traded in a secure and just manner. This is critical in elimination of possible political conflicts in the region that are likely to stem from control of water resources and food prices. Thus the United Nations should endorse this virtual water theory and accord it a resolution status. This according to studies will enhance the credibility of the resolution and enhance accurate, effective and fair virtual water trade between global nations. Of great importance is the fact that it would overcome probable political conflicts and security concerns in the Middle East.

Furthermore, Cline (2007) proposes that the Middle East should liaise with the donor community to form a World Water Fund. This would be instrumental in assisting the poor nations that are found in the region. In this regard, it is worth noting that some countries like Palestine and Egypt are still in their transition phase and can not generate sufficient foreign currency to make food purchases that would effectively address their dietary needs at the current market prices. In addition, these countries have limited resources that do not allow them to benefit from the virtual water trade. Thus such a fund would go a long way in enabling such nations to have access to sufficient and basic food supplies.

In order to deal with the implications of climate change, various strategies can be adopted. To begin with, the governments in the Middle East need to take timely measures and improve the disaster risk management of the population. In this regard, the vulnerable population needs to be informed about its status in advance. Then, the communities need to be empowered accordingly to deal with the emergent risks. This requires partnerships and collaborations between major stakeholders. Most importantly, the strategies should be mainstreamed within the government plans and gaps between different sectors bridged accordingly.

Further, Cline (2007) indicates that respective governments need to strengthen the community based developments. This would be instrumental in enhancing the coping capacity of such populations and enabling them to rebuild their lives after a disaster. In addition, the governments need to ensure that all the communal structures are resilient to the effects of climate change. Of great importance however is to provide viable resources that would cushion the population against the after effects of climate change.

From the analysis, it is certain that food security in the Middle East is compounded by various complexities. This situation is contributed to by various factors that include climate change, population growth and most importantly, water scarcity. Coupled with lack of political will to invest in agriculture, these factors have greatly undermined agricultural production in the region. It is also clear that the complexities differ considerably between the countries found therein. This is influenced by the individual economic wellbeing of these countries. Seemingly, countries with a high level of income face minimal changes as they can easily buy food and subsidize the costs to make it affordable. Notably, the region relies heavily on food imports for its consumption. In particular, it imports cereals more than other food products. However, dairy and meat products are also being increasingly imported because of urbanization ad diversification of the population.

It can be ascertained that the challenges that the region is facing have far reaching implications on the wellbeing of its population. Engagement in virtual water trade has been proposed as the most viable approach of addressing the implications of water scarcity. However, the approach is faced with various challenges that range from social and cultural to economic and religious. These challenges need to be addressed before implementation of the virtual water theory. Alternatively, the region can embark on diversification of its economy to increase employment opportunities and raise the levels of income, control of its population growth by availing effective family planning services to the population and increasing the level of public awareness through education, public campaigns and workshops in order to change the mindset of the entire population. Notably, these would be instrumental in addressing food security in the region.