Taban Peter Ali Impact of Deforestation on Human Health: A Comparative Study of Health Impacts of Deforestation, Southern and Northern, Ghana Thesis Submitted for Master of Science Degree in International Social Welfare and health Policy (MIS) January, 2012 Faculty of Social Studies Oslo and Akershus University College of Applied Sciences MIS 2009/2010 DEDICATION This thesis is dedicated to my beloved daughter, Fatirika Ali and all my friends both in Ghana and abroad. 2 ACKNOWLEDEMENT This research was able to reach its final stage due to numerous contributions and support in diverse forms from many persons. First of all my sincere thanks go to my supervisor, prof Einar Øverbye for the constructive criticism, professional guidance and inspiration offered me through out my writing of this thesis. I am also very much grateful to the entire staff of international social welfare and Health Policy programme and the staff of the library all of Oslo University College, Norway for their immense help to me. I, also sincerely thank my nephew, Napoleon Foam and the family for their immeasurable support to me in terms of accommodation, Feeding, finance, orientation, advice and inspiration. I would not forget to appreciate his daughter, Yennuloom Foam who happened to be my Norsk tutor for all this while.Yennuloom, “Tusen takk, og jeg savner deg veldig mye”.Lastly, my greatest gratitude goes to the entire family of Jatong in Nakpanduri and its environs in Northern Ghana for their love and words of encouragement during my studies in Oslo, Norway. 3 ABSTRACT Ghana, which used to be dominated by forests, is now faced with massive destruction of its vegetative cover, with concomitant environmental and human health hazards. Rain and savannah forests are now metamorphosing to secondary forests, and which has serious implications on human health. This thesis therefore explored desk studies of relationship between deforestation and human health and also made comparative analysis isolating Southern and northern Ghana on impact of deforestation on human health. There were revelations of negative impacts of deforestation on human health which seem to skew to north than south of the country. Institutional failures on the part of the central government regarding implementation of policies to curb destruction of forest cover which led to many forest resources attaining defacto open-access regime was discovered and workable policies discussed. 4 TABLE OF CONTENTS DEDICATION .................................................................................................................................. 2 ACKNOWLEDEMENT .................................................................................................................... 3 1. CHAPTER ONE........................................................................................................................ 7 1.1. 2. 1.1.1. The Research Question ............................................................................................... 7 1.1.2. Introduction ................................................................................................................ 7 1.1.3. Background ................................................................................................................ 7 1.1.4. The Study Area .......................................................................................................... 8 1.1.5. The Northern Ghana ................................................................................................... 9 1.1.6. The Southern Ghana ................................................................................................... 9 1.1.7. Rationale of the Study .............................................................................................. 10 1.1.8. Significance of the study........................................................................................... 10 CHAPTER TWO ..................................................................................................................... 11 2.1. 3. Introduction and background .............................................................................................. 7 Literature review .............................................................................................................. 11 2.1.1. Introduction .............................................................................................................. 11 2.1.2. The Relationship between Deforestation and Human health ...................................... 11 CHAPTER THREE ................................................................................................................. 17 Research Methodology ................................................................................................. 17 3.1. 4. CHAPTER FOUR ................................................................................................................... 19 4.1. Discussion........................................................................................................................ 19 4.1.1. Introduction .............................................................................................................. 19 4.1.2. Is the health impact of deforestation likely to be the same or different in northern and southern Ghana? ...................................................................................................................... 19 5. CHAPTER FIVE ..................................................................................................................... 25 5.1. Causes of Deforestation in Ghana ............................................................................................ 25 5.2. Proximate/indirect Causes ............................................................................................ 25 5.3. Distal/indirect Causes ................................................................................................... 27 5 6. 7. 5.4. Similarities and Differences of Causes of deforestation in North and south of Ghana .... 28 5.5. Theoretical framework ................................................................................................. 29 5.6. The Conventional theory of Common- pool Resource ................................................... 29 5.7. Dependency theory/ world systems theory .................................................................... 30 5.8. Economic Forces and government policies ................................................................... 30 5.9. Delayed Model of Demographic Transition .................................................................. 31 5.10. Forests ownership in Ghana ...................................................................................... 31 5.11. Stakeholders ............................................................................................................. 32 5.12. Land tenure Systems in Ghana .................................................................................. 32 5.13. Forest reserves .......................................................................................................... 32 5.14. Communal forests..................................................................................................... 33 5.15. Sacred grove............................................................................................................. 34 5.16. The Taungya system ................................................................................................. 34 CHAPTER SIX ....................................................................................................................... 34 6.1. Possible Solutions to Deforestation in both south and North of Ghana .............................. 35 6.2. Reduction of deforestation in the southern Ghana ............................................................. 35 6.3. Reducing Deforestation in Northern Ghana ...................................................................... 36 CHAPTER SEVEN ................................................................................................................. 39 7.1. Conclusion ....................................................................................................................... 39 REFERENCES................................................................................................................................ 40 6 1. CHAPTER ONE 1.1. Introduction and background 1.1.1. The Research Question What are the effects of deforestation on health? And or are there reasons for assuming that deforestation has different effects on health in northern and southern Ghana? This paper therefore seeks to: (1) Examine the relationship between deforestation and health (2) In particular, examine if the impact of deforestation on health is likely to be the same or different in northern and southern Ghana. (3) Give possible future solutions to the adverse impact of deforestation 1.1.2. Introduction Deforestation is the clearance or destruction of any amount of forest cover or woodlands. (Angelsen and Kaimowitz 1999, 73). It is the complete long term removal or loss of forest cover. The practice is increasingly and continuously common globally and more severe on the African continent especially in the West African countries. (World Resources 1986, cited by Mann 1990) the world average forest loss is seven times less than some West African countries such as Ghana, Liberia, Ivory Coast or Nigeria. Deforestation is worsening across the length and breadth of Ghana. The rate of deforestation in Ghana is 2% annually or in absolute terms 22 hectares yearly (Gills, 1998). However the significance of forests to mankind is numerous, such as health, recreation, cultural, and religion. This study is to survey literature on relationship between deforestation and human health and make comparative analysis of the relationship, if exist on Northern and southern Ghana. 1.1.3. Background The world’s most challenging environmental problem currently is the destruction of its forest cover. The general forests are under tremendous pressure and many concern people are of the belief that something needs to be done if the forests need salvation. This practice is ongoing for many reasons which will be elucidated in the course of this master thesis. The importance 7 of the natural resources to humanity cannot be over emphasised. The livelihood of mankind is dependent on these resources with no exception of the forest cover. Human beings have been always to some extend use the forests for habitation, protection against enemies, food security, source of medication and above all as their environment. Biblically, Deuteronomy 20:19, King James Version, says “…for the tree of the field is man’s life”. In this light, to possess a forest is a blessing. It could also imply that man has connection with forest and the demise of forest means the end of mankind. The magnitude of forest destruction in Ghana could be described as terrifying and will become more devastating in the near future if nothing is done to curtail the practice. The forest cover in Ghana has been decreasing rapidly and significantly over the past two decades (FAO, 2001). Ghana like any other sub- Saharan African country continues to lose its vegetation at a fast rate. The forest reduced from 8.2million ha to an estimated 0.836million ha representing 89.8% loss (EPA Ghana, 2004). The current rate of deforestation in Ghana is approximately 2.8% or 22,00ha/annum. The effect of deforestation could be widespread, besides its effect on biodiversity, ecological processes and environmental functions; it may also have effect on the human health. Deforestation is the prime factor for loss of biodiversity including human populations. It causes depletion, not only to the forest but the species that reside in the forest and some also use it for food and other several purposes. The non-timber products are used by a large section of the Ghanaian population. It is estimated that 75% of Ghana’s population depends on bush meat as source of protein which is obtained mostly through forest fires as method of hunting. Forest loss also results in land degradation which leads to soil nutrient loss are increasing becoming a serious problem in the northern Ghana (falconer, 1990). In Ghana, the clearing of the forests cover cuts across the length and breadth of the country but in different forms for area specific (Northern and Southern Ghana), considering the reasons for cutting the vegetation material. 1.1.4. The Study Area Ghana is located on the west coast of Africa continent. It shares boundaries with Burkina Faso in the north, Ivory Coast to the west, Togo to the east and Gulf of Guinea to the south. It occupies about 23.9 million ha and situated at the north of the equator and completely within the tropics. The country is made of four ecological divisions- wet evergreen, moist evergreen dry semi deciduous and moist semi deciduous classifications. The high forest ecological zone is located in the south- western part of the country. This particular zone is made of the rain forest (moist and wet evergreen) and also the semi deciduous (moist and dry semi deciduous 8 forest) and occupies an area of about 8.1 million ha. The savannah zone is mainly located in the north and covers an area of approximately 14.7million ha and a transition zone with an area of about 1.1 million ha (ITTO, 2005). The main ecological areas of timber of production are the evergreen and deciduous in the south-western part of the country. In the colonial era, the country was divided into southern and northern administrative sectors but after independence it was then subdivided into ten (10) administrative regions with two or more ethnic groupings found in each region. The southern Ghana in this paper is taken to be situated in the forest zone whiles the northern is located in the savannah vegetation zone. Farming and fishing are the main occupations for majority of Ghanaians. 1.1.5. The Northern Ghana As far as this study is concern Northern part of Ghana comprises the Northern, upper west and upper East. The area is within the savannah zone of the country. The savannah zone is typically woodland and thick vegetation whose density decreases towards the upper East region of the country. Subsistence farming activities, charcoal burning, and bush fires are causing much damage to the forest cover annually. The area experiences almost equal months of dry and rainy seasons. The dry season is always from November to April and rainy season from May to October. Average yearly rainfall is approximately 11 00 mm and yearly average temperature is about 30 degrees Celsius. The area was once the stock of different kind of wild animal species but hunting expedition and trypanosomiasis in addition to the end of the Tsetse Fly Control programme have had impact on reduction of the wild life population in the area. 1.1.6. The Southern Ghana The southern Ghana is made up of Ashanti, Brong Ahafo, southern Volta, western, central, and the Greater Accra and Eastern regions. It is situated in the high forest vegetation zone with annual mean rainfalls of 21,150millimeters and mean annual temperatures are approximately 28 degrees Celsius. The area is characterised by four separate seasons. Heavy rains fall from about April through late June. After a relatively short dry period in August, another rainy season starts in September and last through November, before the harmattan season sets in to complete the cycle. The southern Ghana has several forest reserves and as result, a home of many timber firms. It also produces several cash crops such as cocoa, palm nuts, and plantain. Illegal logging, surface mining activities, agricultural activities, and bush fires have contributed immensely in the destruction of the forest cover. It is estimated that 9 some forest reserves in the south have been destroyed close to 50-70% of their total land area (England, 1993). In the North, bushfires caused by hunters and farmers, charcoal production, and fuel wood for domestic consumption contribute greatly to destruction of forest material. It is evident that the two sectors of the country experience deforestation either similarly or in different forms. 1.1.7. Rationale of the Study Many legitimate concerns have been raised recently about limitations to health as a result of massive destruction of natural resources including forest among populations in Ghana for agricultural activities hunting, expedition, timber production and or fuel. Many trees that serve as medicines to rural and urban populace are destroyed through deforestation. Fertile croplands have lost nutrients since there is no vegetative cover to check erosion leading to famine with its attendant medical consequences. These and more challenged the researcher to find out whether there is any link between deforestation and health of the local people in Ghana where deforestation is at its highest ascendency. And or examine if human health in Ghana is hampered by causes of climate change such as forest destruction. 1.1.8. Significance of the study The significance of this detailed study is first and foremost going to improve the academic ascendency of the researcher. It is to also fulfil the requirements of the Master of Science (Msc) degree in international Social Welfare and Health Policy (MIS). The study may yield several results and information that might be very beneficial to Ghana forestry Commission, Ghana Health Service, Ghana School of Forestry, Non -Governmental Organisations that are into forestry and also policy makers. 10 2. CHAPTER TWO 2.1. Literature review 2.1.1. Introduction This particular chapter reviews existing related literature on the research topic. This section will give an insight to the researcher on what other researchers did on the research theme. As noted by Chambliss and Schut (2006) a good literature review reveals that research question or problem has ever been investigated, and it may highlight on particular areas of the research problems mostly. 2.1.2. The Relationship between Deforestation and Human health There are several practical environmental linkages to health. However, limited to this research, the relationship between specific environmental problem, deforestation and health is presented. In general, vector-borne conditions such as malaria are strongly affected by Changes in climate and the environment and have many direct and indirect effects on human health. Temperature and humidity affects the commonness and distribution of vectors and intermediate hosts. Warmer temperatures allow insects and pests to survive winters that normally would have limited their populations. An increase in malaria in Rwanda coincided with record of high temperatures and rainfall. In 70 communities in Mexico, median temperature during the rainy season was the strongest predictor of dengue fever with vector being mosquitoes: higher temperatures increased vector efficiency (Wilson, 1995). Causes of climate change such as deforestation can influence higher temperatures. That is why mosquitoes are very common in Africa, Asia and Latin America due to higher temperatures. Sarah et al(2010) conducted research in county (município) of Mansion Lima, Acre State, Brazil and Cumulative percent deforestation was calculated for the spatial catchment area of each health district by using 60 Cumulative percent deforestation was calculated for the spatial catchment area of each health district by using 60 × 60–meter, resolution-classified imagery. Statistical associations were identified with univariate and multivariate general additive negative binomial models adjusted for spatial effects. The cross-sectional study shows malaria incidence across health districts in 2006 is positively associated with greater changes in percentage of cumulative deforestation within respective health districts. Forest cover protects human lives and property in cases of torrential rains culminating in floods but rapid deforestation taking place in some parts of the globe would minus these 11 qualities of the vegetative cover resulting in losses of human lives and property by floods. Southern Ghana has now 1.7m ha of forests; these are being destroyed at the annual rate of about 2% of the total area (ROG, 1991). In the North of Ghana, woodland and park savannah are experiencing serious depletion at the rate of about 20,000 ha year (Friar, 1987). In DAKAR, 13 September 2007 (IRIN) - Government figures indicate that in northern Ghana flooding has affected more people than in all other West African countries combined, yet the disaster has received little international attention compared to floods elsewhere in the region. Corey J et al (2007) conducted a study using data collected from 1990 to 2000 from 56 developing countries, they show using generalized linear and mixed-effects models contrasted with information theoretic measures of parsimony that flood frequency is negatively correlated with the amount of remaining natural forest and positively correlated with natural forest area loss (after controlling for rainfall, slope and degraded landscape area). During the decade investigated, nearly1 0 0 0 0 0 people were killed and 3 2 0 million people were displaced by floods, with total reported economic damages exceeding US$ 1 1 5 1 billion. These associations are very significant as far as the dynamics of flood is concern. An increased in diarrhoea mortality/ cases was observed after flood events in Khartoum, Sudan(Woodruff et al, 1 9 9 0 ) and in Bangladesh a cross-sectional survey of households flooded in 1 9 9 8 found that seven people died during flood out of whom two died of apparent diarrhoea and two were suspected to have died of heart attack(Kumi et al,2 0 0 2 ). They admit that the weak evidence might have been due to lack of equipped hospitals to identify and diagnose cases. Soil erosion is second only to human population growth as environmental and public health issue facing the world today. About 99.7% of human food and food nutrients for human health comes from cropland which is being degraded by more than 10million ha a year as a result of deforestation (FAO, 1998). The loss of cropland due to loss of vegetative cover is a serious problem because many soil nutrients important for humans and food production are washed away. The loss of soil fertility and thus declining crop yields resulting in direct and indirect hunger and nutritional deprivation among the poorer segments of the society and therefore increase health problems (Ruddle, 1996). World Health Organisation (WHO) notes that more than 3.7 billion are malnourished in the world. A nutritional survey in northern Ghana showed that 65% of pregnant and 45% of non pregnant women showed systems of protein Energy Malnutrition (PEM) compared with 43% pregnant women and 30% non 12 pregnant women in the southern Ghana (IBRD, 1989). Iodine deficiency disorder(goitre) is a particular problem in the northern Ghana where 10.7% Besides, erosion increases the amount of particulate matter carried by wind which not only acts as abrasive and air pollutant but also carries with it approximately 20% of bacterial organisms of many human infectious diseases including Anthrax and tuberculosis (Pimentel, 2006). The loss of soil fertility and thus declining crop yields resulting in direct and indirect hunger and nutritional deprivation among the poorer segments of the society and therefore increase health problems (Ruddle, 1996). WHO notes that more than 3.7 billion are malnourished in the world? A nutritional survey in northern Ghana showed that 65% of pregnant and 45% of non pregnant women showed systems of protein Energy Malnutrition (PEM) compared with 43% pregnant women and 30% non pregnant women in the southern Ghana (IBRD, 1989). There is a popular consensus that the earth is warming, due to emissions of green house gases caused by human activities such as deforestation. With the growing recognition that tropical deforestation contributes about 20 percent of green house gas emissions worldwide and is thus an important cause of global warming, there is great interest in approaches to reducing emissions from deforestation in developing countries (Metz et al. 2007, Ramamurthy et al. 2007). According to the Intergovernmental Panel on Climate Change (IPCC) deforestation, mainly in tropical areas, account for up to one-third of total anthropogenic carbon dioxide emissions. Deforestation and combustion of biomass produce excessively greenhouse gases such as carbon dioxide (CO2) that helps contribute to global warming. The health impact of global warming could be related to heat strokes and penetration of ultra-violet B (UV-B) rays into human tissues leading to non-melanoma cancers as a result of depletion of the ozone layer. Cardiovascular diseases, cerebrospinal meningitis (CSM) and respiratory disease like asthma are at times manifestations of global warming. People living with cardiovascular conditions suffer more because it puts additional workload on heart to work harder and keep the body system cool in hotter temperatures. Ozone protects us from the harmful UV rays, however when combine with dust, chemical fumes and smoke on the earth surface will lead to fog formation which is a pollutant and has the ability of damaging the lung tissues especially asthmatic patients. Penetration of the zone by the UV-B radiation causes astronomical increases in the temperature which catalyses growth of bacteria and the spread of many tropical diseases such as CSM. The Who’s partial estimate of climate change health impacts in the year 2000 (McMichael et al., 2004), an estimated 200 000 deaths currently occur each year in the world’s low-income countries from a subset of climate-sensitive health 13 outcomes –crop failure and malnutrition, diarrhoeal disease, malaria and flooding. Around 85% of those deaths are in children. Studies in the UK, Australia and Canada have shown a clear relationship between short-term (e.g. weekly) temperatures and the rate of occurrence of salmonella food-poisoning. Bush fires either natural or human- induced produces a lot of particles into the atmosphere that have a limiting effect on human heath. A relationship between forest fires and health care needs was also demonstrated in the US. In 1998, there were extensive wildfires in Florida. As compared to the preceding year, emergency department visits increased 91% for asthma, 132% for bronchitis with acute visits increased 91% for asthma, 132% for bronchitis with acute exacerbation and 37% for chest pain (CDC_US 1999). However, these examples might not be conclusive they give insight on the impact of deforestation through bush fires on human diseases. In a retrospective evaluation of the health impacts of a large wildfire in a northern California Indian reservation, visits to the local medical clinic for respiratory illness increased by 52% over the same period the prior year [146]. During the ten weeks that the fire lasted, PM10 levels exceeded 150 μg/m3 (24-hr average) 15 times, and on two days the levels exceeded 500 μg/m3. Weekly concentrations of PM10 were strongly correlated with weekly visits for respiratory illness during the fire year (r = 0.74), but not in the prior year (r = -0.63). In a community survey of 289 respondents, more than 60% reported respiratory symptoms during the smoke episode; 20% reported symptoms persisting at least two weeks after the smoke cleared. Individuals with pre-existing cardiopulmonary diseases reported significantly more symptoms before, during, and after the fire than those without such illnesses. The investigators also retrospectively evaluated the efficacy of several public health interventions in symptom reduction: (1) filtered and unfiltered masks distributed free of charge; (2) vouchers for free hotel accommodations in towns away from the smoke to assist evacuation efforts; (3) high efficiency particulate air (HEPA) cleaners distributed for residential use; and, (4) public service announcements (PSAs) about exposure reduction strategies. Mott and colleagues found that increased duration of use of a residential HEPA air cleaner was associated with decreased odds of reporting increased symptoms (OR = 0.54, 95% CI (0.32 - 0.89)), with an inverse trend of symptom reporting with increasing duration of use. Similarly, ability to accurately recall a PSA was also associated with reduced odds for respiratory symptoms. In contrast, there was no detectable beneficial effect of evacuation from smoky areas or of the use of masks. However, the timing and duration of evacuation were not optimal: on the days with the highest recorded smoke concentrations, over 80% of 14 the subjects had not evacuated. That mask use was not protective is unsurprising; the masks were distributed without fit-testing and had variable filtration efficiencies. Moreover, none of the interventions was randomized, and in fact individuals with smoke-related health effects or a prior diagnosis of respiratory or cardiovascular disease were given priority to receive hotel vouchers and HEPA air cleaners. More recently, Sutherland and colleagues reported an increase in an index of respiratory symptoms (dyspnoea, cough, chest tightness, wheezing, and sputum production) amongst a panel of 21 subjects with COPD associated with two days of elevated ambient particle levels resulting from a forest fire near Denver. On the two days in which symptom scores were increased, average PM2.5 concentrations increased to 63 μg/m3 relative to an average of 14 μg/m3 on control days [147]. Many forests around the world, especially the rainforest contain medicinal plants that provides important component of health care delivery across the world. For instance Some 120 prescription drugs sold worldwide today are derived directly from rainforest plants. And according to the U.S. National Cancer Institute, over more than two-thirds of all medicines found to have cancer-fighting properties have their sources from rainforest plants. Again the U.S. National Cancer Institute confirms that extracts obtained and synthesized from a nowextinct periwinkle plant found only in Madagascar (until deforestation wiped it out) have increased the chances of survival for children with leukaemia. The forests plants are also invaluable for their medicinal and pharmacological uses (Burley and Styles 1976).The rapid destruction of the forests subjects the formal and informal pharmaceutical industries of lack of potential new drugs due to loss of genetic resources. Many trees are cleared in Ghana to pave way for irrigation project developments. Certain diseases are linked to irrigation developments. One of such disease is filariasis, commonly known as elephantiasis. Filariasis is caused by a mosquito-borne helminth. Outbreaks often occur from rising water tables following water project developments. For instance, in Ghana the rate of infection, worm annual bites per persons and annual transmission potential have been found to be higher in irrigated communities than areas without irrigation projects (Appawu et al, 2001). This was confirmed by another observation where opening irrigation channels during the dry season resulted in a significant increase of filariasis vectors. 15 Causes and health impacts of deforestation Distal/indirect causes •Population growth •Poverty •International/trade •Weak government policies Proximate/direct causes •Logging •Mining •Agricultural activities •Fuel wood/charcoal production •Bushfires •Grazing Deforestation Indirect impacts •Food insecurity •Loss of medicinal plants •Irrigational facilities Direct impacts •Higher temperature/Malaria •Global warming/Cardiovascular •Biomass combustion/ respiratory diseases Figure 1: Schematic diagram of health impacts of deforestation 16 3. CHAPTER THREE 3.1. Research Methodology 3.1.1. Introduction Given the research questions and the inability of the researcher to obtained data from the field, secondary data is used to conduct the research. This area also describes the research design and also gives reasons for selection of the study area. It also discusses the procedures, techniques and methods that were utilised throughout the research process. It explains the type of data used to inform the study. It further describes the study locations and their characteristics and differences and similarities between the study locations. 3.1.2. The Research Hypothesis The research is a comparative study on the health effects of deforestation in Northern and Southern Ghana. The study also explores relationship between deforestation and health. In this light, the tentative proposition of this study that the researcher tries to find out is the assumption that: Deforestation has health implications or effects on the local people. 3.1.3. The Research Design This thesis comparatively aimed at describing relationship between deforestation and health and also to explain differences and similarities of deforestation in both southern and Northern Ghana. Babie (1992) noted that it was seen inadequate to collect data from the field. Due to time constraints the researcher relied on related secondary literature both locally and internationally to inform this study. This comparative study, excluding other reasons is for the fulfilment of the Master of Science in International Social Welfare and Health Policy (MIS) programme. 3.1.4. Types of Data Due to the nature of this comparative research and the researcher’s inability to visit the field, the study solely depended on the existing related literatures from libraries. The main data sources used to inform the study were books, articles, journals, dissertations and also searching from the internet. 3.1.5. Technique of Data Analysis Based on the type of data that was used to inform this research, content analysis was used as the main technique of data analysis. As noted by Chambliss and Schutt (2004), content analysis is a form of research method or technique for systematically analysing and making 17 inferences from texts. In the broader perspective, content analysis could also mean a survey of documents to make inferences (Rubin and Babie, 2004). 18 4. CHAPTER FOUR 4.1. Discussion 4.1.1. Introduction This chapter analyses how deforestation impacts on the health of the occupants of the north and south of Ghana. However, due to the inability of the researcher to travel to the study areas in Ghana he used his personal discretion and few literature reviews to speculate the health impact of deforestation on the two colonial administrative divide of the country, the northern and the southern Ghana. 4.1.2. Is the health impact of deforestation likely to be the same or different in northern and southern Ghana? The over dependence on natural resources specifically the forest cover in rural areas in Ghana where more than 60 percent of Ghana’s 20 million people depend directly on clearing it for agriculture due to part, lack of secure livelihoods subjects them to the impacts of localized disasters such as droughts, local floods, epidemics and wildfires in both southern and northern Ghana. Plasmodium falciparum malaria which is very severe and common in Africa continent and Latin America yearly causes at least one million deaths, most of which occur in Africa and children below five years of age and pregnant women. Malaria is the most common infectious disease that takes many lives especially women and children in the northern Ghana than southern Ghana due to much forest loss (deforestation) causing climate change that will consequently promote mosquito breeding. The relatively higher rates of deforestation in the north of Ghana are directly proportional to incidence of malaria disease. This is consistent with the research results of Sarah et al (2010) who opined that incidence of malaria is directly associated with the rates of deforestation. The forest floor primary growth is thick and well shaded and with rich layer of acidic organic material that renders unfavourable conditions for mosquito bleeding. But many of these forests is destroyed for agricultural activities or burnt for charcoal or in search of bush meat in the north exposing the deforested area to sunlight which raises the temperature favourable for mosquitoes bleeding. This may be consistent with Patz et al, 200 who opined that cleared lands are more generally sunlit and prone to the formation of puddles with more neutral pH which favours specific anopheline larvae development. 19 The much loss of forest cover in Ghana has rendered many parts of the country’s land barren and subjects it to effects of excess rains (floods). The forest plays an important role in checking floods. Floods have been a common phenomenon of recent in Ghana especially in the three northern regions and have led to many losses of lives and property and poor health. For instance in 2005 Ghana was one of the worst hit by flooding in the West Africa. Reports (Daily Graphic, 2005) indicated that this flooding led to 20 people killed across the Upper East, Upper West and Northern regions of the country. The estimations of National Disaster Management Organisation (NADMO) had it that about 350,000 people were severely affected during these flooding incidents and several hundred hectares of crops of farmland were completely washed away whiles In June 2001 torrential rain caused widespread flooding in southern Ghana and particularly Accra, leaving 11 people dead and over 100,000 without homes. This is synonymous to Correy et al (2007) research results which concluded that floods frequency is inversely correlated to the amount of remaining forest directly proportional to natural forest loss. During the decade investigated, they found out that nearly100 000 people were killed and 320 million people were displaced by floods, with total reported economic damages exceeding US$1151 billion. The northern and southern Ghana is faced with soil erosion and its effects as loss of soil fertility due mainly to loss of vegetative environment that controls erosion. Soil erosion wipes away many nutrients significant for human and plant health. Comparatively deforestation in the southern Ghana is at the annual rate of about 2% of the total area (ROG 1991). The woodland and park savannah in the north is facing serious depletion at the rate of about 20,000 ha year (Friar, 1987). The link between deforestation and soil erosion or loss of soil fertility is confirmed by (Ruddle, 1996) who concluded that loss of soil fertility and thus declining crop yields resulting in direct and indirect hunger and nutritional deprivation among the poorer segments of the society and therefore increase health problems. Malnutrition is not uncommon all over Ghana but worst in the three northern regions. This is confirmed by( IBRD, 1989) whose research results show that 65% of pregnant and 45% of non pregnant women showed systems of protein Energy Malnutrition (PEM) compared with 43% pregnant women and 30% non pregnant women in the southern Ghana (IBRD, 1989). It is also consistent with (ROG 1986) that Iodine deficiency disorder (goitre) is a particular problem in the northern Ghana where 10.7% of the surveyed population is afflicted. This is because soil erosion in the arid areas (northern Ghana) has stripped away the iodine content in soils such that it cannot be absorbed by crops (ROG-UNICEF 1990).Approximately 99.7% of human 20 food and food nutrients for human health comes from cropland which is being degraded by more than 10million ha a year as a result of deforestation (FAO, 1998). The health impact of causes of climate change in Ghana, specifically deforestation cannot be overemphasised especially in the three northern regions of Ghana where most households depend on rain-fed agriculture such as peasant and commercial farming to fend for their families and also derive proceeds accruing from the sale of farm produce. The northern Ghana relies on only one unreliable rainy season for food production. Inconclusively the unreliability rainfall pattern is due to elements such as mass deforestation that is leading to climate change in the north. The woodland and park savannah in the north is facing serious depletion at the rate of about 20,000 ha year (Friar, 1987). Food production is therefore very unreliable and low, high malaria incidence, deaths due to floods in comparison to the south that have double rainy season, less deforestation rate and thick forest low malaria incidence and low frequencies. This is linked to less deforestation in the southern Ghana as the annual rate of about 2% of the total area (ROG 1991). The estimate of WHO about climate change health impacts in the year 2000 (McMichael et al., 2004), an estimated 200 000 deaths currently occur each year in the world’s low-income countries from a subset of climatesensitive health outcomes –crop failure and malnutrition, diarrhoeal disease, malaria and flooding. There are several evidences that show that harmful particles such as carbon monoxide emanating from forest fires are very harmful to human. A study showed relationship between forest fires and health care needs was demonstrated in the US. In 1998, there were extensive wildfires in Florida. As compared to the preceding year, emergency department visits increased 91% for asthma, 132% for bronchitis with acute visits increased 91% for asthma, 132% for bronchitis with acute exacerbation and 37% for chest pain. (CDC_US 1999). There are also similar results on a retrospective evaluation of the health impacts of a large wildfire in a northern California Indian reservation, visits to the local medical clinic for respiratory illness increased by 52% over the same period the prior year [146]. During the ten weeks that the fire lasted, PM10 levels exceeded 150 μg/m3 (24-hr average) 15 times, and on two days the levels exceeded 500 μg/m3. Weekly concentrations of PM10 were strongly correlated with weekly visits for respiratory illness during the fire year (r = 0.74), but not in the prior year (r = -0.63). In a community survey of 289 respondents, more than 60% reported respiratory symptoms during the smoke episode; 20% reported symptoms persisting at least 21 two weeks after the smoke cleared. Individuals with pre-existing cardiopulmonary diseases reported significantly more symptoms before, during, and after the fire than those without such illnesses. The investigators also retrospectively evaluated the efficacy of several public health interventions in symptom reduction: (1) filtered and unfiltered masks distributed free of charge; (2) vouchers for free hotel accommodations in towns away from the smoke to assist evacuation efforts; (3) high efficiency particulate air (HEPA) cleaners distributed for residential use; and, (4) public service announcements (PSAs) about exposure reduction strategies. Mott and colleagues found that increased duration of use of a residential HEPA air cleaner was associated with decreased odds of reporting increased symptoms (OR = 0.54, 95% CI (0.32 - 0.89)), with an inverse trend of symptom reporting with increasing duration of use. Similarly, ability to accurately recall a PSA was also associated with reduced odds for respiratory symptoms. In contrast, there was no detectable beneficial effect of evacuation from smoky areas or of the use of masks. However, the timing and duration of evacuation were not optimal: on the days with the highest recorded smoke concentrations, over 80% of the subjects had not evacuated. More recently, Sutherland and colleagues reported an increase in an index of respiratory symptoms (dyspnoea, cough, chest tightness, wheezing, and sputum production) amongst a panel of 21 subjects with COPD associated with two days of elevated ambient particle levels resulting from a forest fire near Denver. On the two days in which symptom scores were increased, average PM2.5 concentrations increased to 63 μg/m3 relative to an average of 14 μg/m3 on control days [147]. The above studies have several structural limitations, however especially community exposure to biomass smoke show a generally reliable relationship between exposure and increased respiratory symptoms, increased risk of respiratory illness, including hospital emergency room visits, and decreased lung function. There are no available data on empirical studies on bushfires and respiratory diseases on both northern and southern Ghana, however since bushfires are one of the main methods used to clear forest for agricultural activities and hunting expeditions in the northern Ghana it is by implication useful to speculate that respiratory diseases might be more common in hospitals outpatient attendance and admissions than southern Ghana where logging and mining activities deforest the vegetation cover. 22 Global warming has numerous negative effects on human health. Penetration of the zone by the UV-B radiation causes astronomical increases in the temperature which catalyses growth of bacteria and the spread of many tropical diseases such as cerebrospinal meningitis. The global warming has effect on the northern Ghana increasing the already high rocketing temperatures which promotes high incidence of infectious diseases. The north has lost a lot its vegetative cover through deforestation. Temperatures in the south are comparatively lower in the south and therefore lower disease incidence. In the light of this, northern Ghana experiences high incidence of CSM than south due high temperatures caused by deforestation even though first case of meningitis was discovered in the south, Cape Coast among east Africans who was brought in to campaign against the majority tribe in the south, Ashanti in 1900(Waddy, 1957). Ghana and for matter northern Ghana CSM outbreak occurs 8-12 years interval. Retrospectively, epidemics occurred in 1919/21, 1939, 1944/45, 1948/50 (Waddy, 1957), 1960/61, 1972/73 (Belcher et al., 1977) and 1984. In1996/97 Ghana experienced the biggest epidemic which recorded 18703 cases and 1356 deaths (Woods et al., 2000) with Kassena Nankana District (KND) in the northern Ghana recorded 1396 cases with 69 deaths (Enos, 1997). This is synonymous to. The Who’s partial estimate of climate change health impacts in the year 2000 cited in (McMichael et al., 2004), an estimated 200 000 deaths currently occur each year in the world’s low-income countries from a subset of climatesensitive health outcomes –crop failure and malnutrition, diarrhoeal disease, malaria and flooding. Around 85% of those deaths are in children. Studies in the UK, Australia and Canada have shown a clear relationship between short-term (e.g. weekly) temperatures and the rate of occurrence of salmonella food-poisoning. They care delivery is much changing in Ghana. While many major centres are better served, the rural areas have often no modern health facilities. As a result, traditional and herbal medicine is providing the most important accessible source of health care in the rural settlements in Ghana (Abbiw et al, 2002). Medicinal plants have been used and well accepted by mostly the rural population in Ghana (Ekpe 2002). (Burley and Styles 1976) opined that the forests plants are also significant for their medicinal and pharmacological uses .The rapid destruction of the forests subjects the formal and informal pharmaceutical sectors of Ghana lack of potential new drugs due to loss of genetic resources. This impact is severe in the north since deforestation is rampant relative to the south. Irrigation facilities are much needed in the northern part of Ghana to sustain farmers’ income all the year round, due to the one-time rainy season as compared to double wet season in the south. But constructions of such facilities deforest much vegetative cover and also raise the 23 water table that promotes incidence of vector-borne diseases. This is similar to research conducted 1by (appawu et al 2001) that annual transmission potential of lymphatic filariasis (elephantiasis) have been found to be higher in irrigated areas than communities without irrigated in Ghana.Filariasis is caused by a mosquito-borne helminth. Outbreaks often occur from rising water tables following water project developments. This was confirmed by another observation where opening irrigation channels during the dry season resulted in a significant increase of filariasis vectors. 1 Filariasis vecotors are mosquitoes that transmits filariasis to humans 24 5. CHAPTER FIVE 5.1. Causes of Deforestation in Ghana There are several direct and indirect linkages of deforestation to human health in general. However these health impacts are sparsely distributed across Ghana. To therefore find remedies to alleviate these unhealthy situations created by deforestation in Ghana, if not completely eradicate them, it is prudent to identify the main cause(s) of the disease(health impacts) and destroy it or break the chain of connections between deforestation and human health in Ghana. This study has in no small measure identified several distal (indirect) and proximate (direct) causes of deforestation which leads to unhealthy effects on human beings in Ghana. Forest loss in Ghana has therefore been caused by the interaction of different factors identified as distal or Underlying driving forces such as poverty, international trade/dependency theory, population growth and weak government policies and the proximate (direct) causes of forest loss which include fire, mining, but more importantly logging and farming (ITTO 1996). 5.2. Proximate/indirect Causes 5.2.1. Agriculture The fast growing population of Ghana has much pressure on land for agricultural activities such that people even encroach into forest reserves. (Kartawinata, 1997) Growing populations need expanding food supplies so forests are destroyed by shifting cultivators for annual or permanent crops (Rates of forest clearing are likely be higher in countries where little or no progress has been made in agricultural productivity or where land productivity falls after the natural land is removed(world Bank 1978, 18-19). Forests in generally are disappeared both in countries still reliant on shifting cultivation and in those making the transition to permanent copping patterns. 5.2.2. Logging Ghana over the period 1996–2005 based on a definition that emphasizes the violation of established forest management regulations. Of the total harvest, 70% or 2.3 – 2.7 million m3 annually is considered to be illegally logged. Chainsaw operators, who supply most of the domestic or local lumber demand, account for two-thirds and the export timber industry 25 account for one-third of the illegal harvest. The most valuable timber species dominate the illegal harvest and they appear to originate mostly from forest reserves, which as a consequence are seriously threatened. Commercial logging operations deplete forest stocks (Eckholm 1976, 39). Regulated timber extraction should not permanently damaged the forest (Schmithusen 1976) but when it is not controlled, mechanised logging or even selective timber harvesting may severely change the character of the forest (World Bank 1978, 19). Regulated or unregulated timber extraction involves road constructions which indirectly cause deforestation because it gives accessibility to agricultural populations in search for virgin lands to deforest and start farming. 5.2.3. Mining Ghana is blessed with a lot of natural resources such as petroleum products, gold, bauxite, diamond and manganese. However these minerals are deposited in the southern Ghana and much into its many forest resources. Mining of these minerals has resulted in massive destruction of forest cover leading to deforestation. Extraction of these resources depends on expertise and technology which lacks in the country. The government of Ghana established motivational schemes such as tax exemptions which attracted a lot of mining companies into the country which are sparsely distributed across the southern sector and with the use of sophisticated machines destructing the natural forests. For instance, at around 1990, there were as many as 60 mineral extraction mining companies in Ghana (ISSER 1999). The activities of artisanal miners or small scale miners (galemsey as called in Ghana) have similar impact on the vegetative cover of southern Ghana. 5.2.4. Bush fires and Grazing Deforestation occurs in several ways either than clearing or wood removal. In Ghana, especially the northern parts of the country bushfires are used for clearing of farmlands through slash and burn and during hunting expedition to chase game out of habitation. Besides bush fires many subsistence farmers rear animals of different kinds in addition to farming (mixed farming), however these animals graze indiscriminately on every reachable forest. The practice of annual burning in many areas prevents forests re-growth (FAO 1980c, 2-5), and grazing by goats, sheep and cattle has much the same effect (World Bank 1978, 34). This practice may lead to compact of the soil or erosion of the soil. 26 5.2.5. Fuelwood/Charcoal production Most populations across the globe especially the third world countries depend on wood fuels as energy. Firewood and charcoal are mostly used domestically for cooking and heating. In many parts of Africa, wood fuels account for as much as 95 percent of total energy use, including energy for industries such as brewing, baking and brick making (Cecelski et al. 1979; Dunkerley et al. 1981, 48-57). Fuel wood and charcoal account for over 75% of the total energy consumption in Ghana (Sayer et al. 1992). In Ghana, especially the northern Ghana it is very common to see woman walking for long distances to harvest fuel wood which is the major source of energy for the households(Ardayfio- Schandorf, 1993)The demand for wood energy has been augmented by the recent dramatic increases in oil prices, which have prevented the switch to non-wood based fuels. Such use of woodlands and forests, including forests reserves by growing populations in search of wood fuels is one of the most commonly cited causes of deforestation (Allen 1983). 5.3. Distal/indirect Causes 5.3.1. Poverty The concept of poverty is complex and due to its complexity, poverty has series of meanings. However, poverty focusing on income and consumption which allows for poverty lines distinguishing poor from the rich using government sample surveys is used here to drive home point. According to World Bank individual is poor when his or her consumption or income levels fall below some minimum level necessary to meet basic needs. According to Ghana Statistical Service, 1994 31% of the total population in Ghana had their yearly expenditure below the nation’s poverty line of 132230 cedis (17US dollars). Rural population constitutes 65% of the general population of the country which contributes 80% of the national poverty. The rural population destruct much forest cover since it relies solely on the surrounding natural forests for food, bushmeat and fuelwood. They people of Ghana therefore destroy the vegetation cover because there is no any other alternative that can alleviate their poverty than the proximal natural forest. Poverty has however increasingly become an environmental problem (Durning, 1989) 5.3.2. International Trade/dependency theory 27 Many third world countries supply primary goods of different kind to the West to earn tertiary goods in return. By application, the OECD countries depend on the low income countries for some selected primary commodities to feed their market and placed certain trade restrictions on many commodities in the low income countries that the West has them in abundance. Ghana supplies cocoa, gold and timber to OECD countries in return for tertiary goods but due to trade restrictions to exportation of other goods the country has rather expanded production of these goods by overexploiting the natural vegetation such as cutting down more trees for timber, destroying vegetation cover by mining companies to reach more gold and destroying forest for cocoa plantations by farmers just to meet the demands of the international market. As opined by political ecologists, external factors should not be ignored in the analysis of causes of deforestation. Similarly dependency theory has it that low income countries or developing countries implement policies that favour exports such as timber to these markets and eventually augment unsustainable activities resulting to deforestation, (Walter stein; Chase-Dunn 1998). 5.3.3. Misguided Government policies Some policies of the government of Ghana meant to attract foreign investors into the country rather help promote the destruction of the country’s forests by these investors. For example, the 1985 investment code of Ghana gave many privileges to foreign investors such as tax holidays up to five years and 20% tax reductions for newly established mineral extraction companies in the rural communities whose activities lead to deforestation. 5.4. Similarities and Differences of Causes of deforestation in North and south of Ghana Some or all of the above causes of forest loss in Ghana are either practised in south or north or both due to different motives. Farming activities, bush fires, fuelwood, poverty and charcoal production are the main causes of forest loss in the three northern regions of Ghana. However, all except for agricultural activities are less in the South. The double wet season in the south makes it very cumbersome for fuelwood harvesting and charcoal production due to lack of dry forest material. In this light, the North therefore feeds the South with charcoal and fuelwood since there is extraordinarily higher demand down south for these goods (dependency theory). This supplier and consumer link has impacted negatively on the forests resources of the north as many people unusually cut down life trees for fuelwood and charcoal for domestic use and meet the market demand down south. Also poverty as a distal 28 link to causes of deforestation in Ghana is relatively widespread in the dry savannah region that covers roughly two thirds of Ghana’s northern territory.Available statistics indicates that Ghana’s average of poverty is estimated as 39 percent while in the Northern Region it is 69 percent, Upper East Region 88 percent and the Upper West Region 84 percent (Ghana News Agency, 2002). Unlike the south, where there is double growing seasons, the northern plains are drought-prone and people have fewer economic alternatives and so they overexploit the forest resources for livelihoods leading to deforestation. As poverty-environment thesis speculates; poor people are often impoverished by a declining resource base, and thus forced by their circumstances to degrade the environment further. (World Commission on Environment and Development 1987; Durning1989; Cleaver and Schreiber 1994; Ekbom and Bojo 1999). Illegal and legal logging, agricultural activities and mineral extraction are the strong proximate causes of forest loss in the south. Cocoa is an export commodity and in high demand by the first countries capitalist oriented markets and therefore Ghana as satellite (developing country) undergo mass clearing of its valuable forests for cocoa plantations and transfers the produce to the metropolis (developed world). Mining activities is mainly practised in the south due to its endowment with many natural resources. As a result foreign mining companies are concentrated in the south and causing a lot of destruction to the forests. Legal and illegal loggings have damaged forest cover in the south due to the higher demand of timber by OECD countries. Government policies governing forest resources are so weak across the country and so there is illegal logging and massive encroachment into even forest reserves designated by the state. 5.5. Theoretical framework The below theories tried to provide explanations to the destruction of the biosphere some of which might give an insight into the research topic. 5.6. The Conventional theory of Common- pool Resource In this theory, it is assumed that a resource such as forest, generates a highly predictable, finite supply of one type of resource unit (hardwood timber or fuel wood for example) in each relevant time period. Users are assumed to be homogeneous in terms of their assets, skills, discount rates and cultural views. They are also assumed to be short-term, profit-maximising actors who possess complete information. In this theory, any one can enter the resource and appropriate resource units. Users gain property rights only to what they 29 harvest, which they then sell in an open competitive market. The open-access condition is a given. The users make no effort to change it. Users act independently and do not communicate or coordinate their activities in any way. The prediction from this theory is that overharvesting will result (Feeny et al, 1996). 5.7. Dependency theory/ world systems theory This theory has been termed dependency by development economists and world systems theory by sociologists. The nations of the world are organised into “a world system” based on capitalism and market connections, (Walter stein; Chase-Dunn 1998). Nations are unequally advantaged in this system, with the “core” nations having the most power in the market and in the organisation of the world. Core nations used their power to maintain their privileged position through the exploitation of “peripheral” and “semi-peripheral” countries. Core countries are more developed. Economically contain the head quarters of most transnational corporations, and wield considerable political influence over peripheral a semi-peripheral countries. A poor countries export capitalism, peripheral and semi-peripheral countries are drawn into world economic markets. This unequal organisation and the diffusion of capitalism affect a host of economic outcomes. Consider land use and its effects, it is very important to food markets. The low income countries or developing countries implement policies that favour exports to these markets and eventually augment unsustainable activities resulting to deforestation. 5.8. Economic Forces and government policies A different body of theory focuses on economic factors as the affect land use and leads to deforestation. Kaimowtz and Anglsen (1998) have undertaken the most exhaustive review of economic models of deforestation. The most general source of deforestation in tropical areas that they identify is the crop areas and pastures (pastures expansion) which is common in Latin America and Africa. This is consistent with the type of general equilibrium models posited by leading economists such as Deacon. General equilibrium models explore the cumulative effect of decision by actors in an economy under devise taxes and inducements. If there are no policies related to land use changes from forested to agriculture or pasture uses, general equilibrium model posit that inefficiency will exist since standing forest and the ecosystem services produced by them are not given any value in such a setting. 30 5.9. Delayed Model of Demographic Transition This type of demographic transition is common in low income countries. The delayed transition means that both the onset of the decline in mortality occurs at a late stage in history and that the decline in fertility is further delayed in respect to a relatively rapid decline in mortality. This has resulted in very fast population growth in many African countries (Omran 1971). Especially rapid population or dense population can increase demands for land and wood, finally exceeding the capacity of forest that is supposed to give food, protection and wood fuel (Brokensia and Asman 1979). It is very much not uncommon to see people in Ghana illegally destroy forest reserves set aside by the central government to get access to land for cultivation of crops to feed their numerous family members. 5.10. Forests ownership in Ghana In the twentieth century, the forest area of Ghana covered approximately 34 percent of the total land area. Forest reservation was started in 1927 by the colonial administration and ensured the reservation of 11 percent of the country’s total forest area. In all, 282 forest reserves and 15 wildlife protected areas, occupying more than 38 000 km2 or about 16 percent of the total land area, were established and gazetted in Ghana. There was an additional 4 000 km2 of forest outside this gazetted area. The main aim of the reservation programme was to ensure the protection of substantial areas of forest, but the process of forest land reservation ignored the traditional tenure system, which led to a negative attitude to reserves among the forest owners and for that matter the general population, especially in forest fringe communities. This situation was aggravated by a failure to inform forest communities of their usufruct rights and therefore focusing on forest management on forest protection by the central government. All forest lands in Ghana are held in trust by the government, which manages them for the stool landowners. The Forest and Wildlife Policy of 1948 stipulated that the government manage forest resources single-handedly, without the collaboration of forest fringe communities, and this did not yield many positive outcomes. Passage of the current Forest and Wildlife Policy of 1994 led to some progress regarding stakeholder collaboration, but did not solve the ownership issue regarding trees outside forest reserves and on farmland; the lack of clear ownership status calls for a policy review. The forest sector faces a lot of challenges related to forest ownership, resource tenure and the lack of effective participation from resource owners and local communities in forest management decision-making. 31 In Ghana, forest ownership is derived from the system of land inheritance. There are two forms of inheritance: the patrilineal system and the matrilineal system. Because of the different historical settings of these two systems, they have different concepts of land, land acquisition and landownership. Under the patrilineal system which is practised in north, inheritance passes directly down the male line, while in the matrilineal system practised in south, succession to property and land passes along the matrilineal line according to primogeniture in the following order: brothers, sisters’ sons, sisters, and sisters’ daughters (Agyeman Dua, 1991). These systems of land inheritance do not necessarily include tree tenure right. 5.11. Stakeholders The stakeholders in the forest protection in Ghana, both on- and off-reserve, include the central government through its Ministry of Lands, Forestry and Mines, the Forestry Commission, stool landowners, district assemblies, forest fringe communities, nongovernmental organizations (NGOs), timber contractors, administrators of stool lands, and private plantation developers, both local and international. It is important to emphasize that in Ghana ownership of land does not necessarily imply the ownership of and right to fell, extract and convert logs into lumber without permission from FSD. It is an offence to fell timber, convert it into lumber or convey it without the relevant permission stipulated by law. Regarding stakeholders’ rights and responsibilities, only the government − through its various ministries, department and agencies − has asserted its rights and responsibilities. This is mainly the result of the government’s failure to formulate policy and define roles for ensuring sustainable forest resource use, and of inequitable benefit sharing arrangements. 5.12. Land tenure Systems in Ghana The term land tenure refers to the various laws, rules and obligations that govern the holding and/or ownership rights and interest in land (Kasanga, 1988). Generally the land tenure system of a particular area depends greatly on the traditional or local political organization within that particular community or locality in Ghana. The below land tenure types are practised in Ghana. 5.13. Forest reserves 32 Forest reserves are fully vested in the State through the Forest Ordinance of 1927, and all forest and timber resources are held in trust by the government on behalf of the stool landowners. Although land ownership did not change at the time of reservation, traditional owners are denied rights of access to trees or land in reserves unless they have a permit from FSD. Since its onset, this law has created animosity between local communities and FSD, because of foregone benefits and the view that reserves were created without consultation. The management of trees within forest reserves, and the rights to own, plant, use and dispose of them are controlled by the State through the Forest Protection Decree of 1974. (Asare, 2000) ownership of forest is closely linked to the indigenous system of landownership. Land is communally owned and held in trust on behalf of the people through the stools and skins. Landowners exert substantial control in deciding whether an area should be set aside for reservation. Although national law grants the government the authority to constitute a reserve on any land it deems appropriate, landowners must be consulted through an arbitration process that is under the jurisdiction of a reserve settlement commissioner, who must take landowners’ concerns into consideration. Some proposed reserves have had to be abandoned because of strong opposition from landowners. Asare also reports that in some instances, such as wildlife reserves, the government purchases the land outright from the landowners, thereby becoming the property owner and enjoying the same rights as any other landowner. In effect landowners − whether stools, skins, the government or individuals – wield immense power on the setting aside of an area as permanent forest estate, and always have rights to revenue from the exploitation of the resource. 5.14. Communal forests Communal forests are woodlands outside forest reserves; most of them are in northern part of Ghana. Unlike the off-reserve forests of the south, which have economically exploitable timber trees, the trees in communal forests can be used only by households as sources of fruits, other food, medicines, etc. Communal forests are either natural or established by communities with support form FSD and NGOs. Trees in these forests cannot be owned or inherited by individuals, but usufruct rights − such as collection of herbs and fuelwood − can be, according to the relevant rules and regulations. In Upper West region for instance, some communities have reserved areas of land for fuelwood production. 33 5.15. Sacred grove Sacred groves are forests that communities have reserved on communal land. They occur in both southern and northern part of Ghana and are usually very small in size. No individual has the right to plant, use or inherit trees and other tree products in most of these traditional forest groves, which are of great socio-cultural and religious significance. The rich histories of these natural enclaves are diverse, but most are related to the beliefs and values of local people. Traditional authorities employ indigenous strategies to exclude human activities from sacred groves, retaining them in or near their original natural state. The most common of these strategies are taboos that restrict people’s entry altogether or on particular days. In some cases, the community’s fetish priest is the caretaker of its sacred groves and is usually granted limited rights to sell tree products, but not the land; no individual has the right to dispose of such land. 5.16. The Taungya system Taungya is a system of forest plantation in which small-scale farmers are given the opportunity to cultivate crops between the seedlings of a forest plantation for the first few years after planting (Amanor, 1996). The system was established in 1928 to restore Ghana’s forests, solve the land shortage that farmers living near forest reserves were facing, and finally provide the Forestry Department with human labour for plantation improvement. Since then, lack of ownership rights to trees planted on reserved land has proved to be a grave disadvantage for forest protection and sustainable management. 6. CHAPTER SIX 34 6.1. Possible Solutions to Deforestation in both south and North of Ghana The health impact on people of Ghana by deforestation is enormous and needs to be curbed. The root causes of the health impacts have been identified by this study as those mechanisms that promote occurrence of deforestation. The mechanisms are therefore the distal and proximate elements that bring about deforestation. Taking the research findings into consideration, using laws as usual, in curbing the proximate causes without tackling the distal causes will not yield maximum results since it is the distal causes that give birth to the proximate ones. In this light, the study will first of all summarily deal with the solutions to the distal causes of deforestation and thereafter give solutions to check proximate causes based on where it occurs in terms of South and North of the country. Chiefly, government should support family planning units of health institutions across the country in terms of finance and logistics so that they can consistently educate the masses on birth con troll measures. Poverty in Ghana is much within the informal sector. Banks can give loans and training to the poor to go into income generating venture such as bread baking, fishing, hair dressing and many others. This will give alternative sources of livelihood to complete dependence on forest sources. Many misguided laws designed by government should be reviewed by all stakeholders. For instance, the 1985 investment code that gives five-year tax holiday and 20% tax rebate to newly established companies operating in rural areas should be reviewed since it attracts many mining and timber companies to forest areas with their attendant effects on forests. Dependency theory states that nations of the world are organised into “a world system” based on capitalism and market connections, where some nations are not favoured in this system, with the western nations having the most power in the market and used their power to maintain their privileged position through the exploitation of third world countries (Walter stein; Chase-Du1998). From the theory it implies the West is part of causes of deforestation in developing world and for that matter Ghana. The West can therefore help reduce forests loss in Ghana by taking of certain trade restrictions that prevent Ghana and other low income countries to diversify their export commodities which will limit pressure on timber products. 6.2. Reduction of deforestation in the southern Ghana In connection with mining, logging and agriculture as proximate causes or reasons why there is occurrence of deforestation in the southern Ghana, the following important areas may be taken into consideration as practical measures to alleviate deforestation in the south Evidently, in Ghana agricultural activities in both south and north are still being characterised 35 by elements of shifting cultivation including slash-and-burn deforestation preparing lands for cultivation. Alternative livelihood and income generation measures encouraged such as snail farming, apiculture, bee keeping and fish farming should be encouraged with motivations such as subsidies and provision of technical know-how by the central government to attract farmers who are solely dependent the forest lands. These practices have shown to be potential alternative sources of income and employment, which could move people away from the forest resources (Appiah, 2003). Farmers should also be educated by agriculture extension officers on improved or modernised methods of farming to increase yield on the same farmyard instead of destroying virgin forests for more yields. Most forest resources in Ghana faced ownership problems hence lack control. The Government have ownership rights for forest reserves and even timber trees outside the reserves especially in the southern Ghana where logging is practised, excluding fringe communities from the benefits accruing from the resource. Meanwhile the state lacks the capacity especially adequate funds and personnel to enforce its ownership and user laws (rights) to control forest resources. The forest resources therefore become a de facto tragedy of the commons (open- access) and gives room for illegal logging or chainsaw operators to maximise their utilities. It is estimated that in 1999, more than two-thirds of the wood harvested in Ghana in the country was illegally harvested and dominated by activities of chain saw operators(Gayfer et al, 2002). The many existing laws in the forest sector should be implemented and enforced by the main institutions. These institutions should be provided with the required human resource and logistics to carry out their functions without shortages. Rural populations should be educated on the laws and consequences of flouting them. Government should therefore formulate policy framework that promotes community forest and encouraging communities to create forest reservations for them. This will drastically nullify the negative effects of the 1974 Trees and Timber Decree, which gives ownership rights of all timber trees in Ghana to only the government. The many laws in the forest sector should be implemented and enforced. Rural populations should be educated on the laws and consequences of flouting them. Laws should be enacted that will compel the mining companies to refill pits after mining and re-plants trees. This will not only curb deforestation but also prevent breeding sites for mosquitoes. 6.3. Reducing Deforestation in Northern Ghana The proximate causes of deforestation characterising the North are fuelwood and charcoal production, bush fires, animal grazing and agriculture. However agriculture is well dealt with 36 in the previous page since it is one proximate cause that cuts across equally between north and south. To begin with it is not an exaggeration to say that almost every household of northern Ghana depends on fuel wood for cooking and heating. Burning of biomass definitely leads to deforestation and apparently releases carbon dioxide (CO2) and other greenhouse gases that cause universal climate change and its attendant effects. Policies that will embrace introduction of improved stoves in the developing world will have the ability to reduce much of these problems. The government of Ghana if would revisit the improved stoves project for the three northern regions of the country which depend largely on forest resources for domestic energy and income will check forests loss immeasurably. Furthermore, land/forest rights of ownership do not favour women in the North unlike their counterparts down south. There are no known customary laws that spell out their illegality to ownership rights. This is worsening by the scarcity of farmlands making sons and family heads to assert male claims and lineage principles strongly (Nukunya, 1972). In the three northern regions of Ghana, women and children are responsible for harvesting of firewood and production of charcoal for sale and for domestic use and so they overexploit the forest resources maximise their utilities leading to deforestation. There should be transformation in customary laws that will give women and daughters the right to own and to succeed family and private lands. This will help woman protect and manage their forests in a sustainable manner. Bush fires is a common phenomenon in Ghana and mostly used by farmers, hunters and cattle rangers to clear the forest for crop cultivation, chase game and to promote fresh vegetative growth for animals respectively. As Dagomba saying goes “As far as the bushfires continue, the grasshoppers cannot congratulate each other".Dagomba is the biggest tribal group in northern region as well as the entire northern Ghana. It is very common to see articulated lorry trucks loaded with hunters from this tribe hunting expedition. Bush fires are used in such ventures to reach game. The government of Ghana charge the body concerned to enforce the an anti-bushfire law of PNDC Law 46, which prohibit the setting of fires except for certain agricultural, forestry and game management purposes. Hunters could also be motivated with technical know-how and loans to go into rearing grasscuters, rabbits, local and exotic poultry to help meet their protein and income needs. Agriculture extension workers should teach cattle owners to harvest and dry cattle feed during the wet season to be used in dry season will help reduce incidence of bush fires in the North. 37 38 7. CHAPTER SEVEN 7.1. Conclusion The study tried to find out if there is correlation between human health and deforestation and if or no is that relationship similar or different in the southern from the northern Ghana. There were revelations of impacts of deforestation on human health which seem to skew to the north than south. Institutional failures regarding implementation of policies to .curb destruction of forest cover which led to many forest resources attaining defacto (open-access) tragedy of the commons was discovered and workable policies discussed. Causes of deforestation were identified as proximate and distal causes. The distal causes were the underlying causes such as misguided government policies, poverty and population growth which influenced the appearance of proximate causes such as logging. Solutions to loss of forest cover were therefore explained according to proximate and distal elements. 39 REFERENCES Agyeman, D.J. 1991. Culture and location of the Akan people. Pioneer No. 11161. Kumasi. Allen, J. C. and D. F. Barnes. 1985. The causes of deforestation in developing countries. Annals of the Association of American Geographers 75:163–184. Angelsen, A. and Kaimowitz, D. 1999. Rethinking the Causes of Deforestation: Lessons from Economic Models, the World Bank Research Observer, Vol. 14 (1), pp 96-104 Anon.1996. World Resources: A guide to the Global Environment 1996-1997, London, Oxford. Appiah, M. (2003). Domestication of an indigenous tropical forest tree. Silvicultural and socio-economic studies on Iroko (Milicia excelsa) in Ghana (104p). Doctoral thesis. University of Helsinki Tropical Forestry Reports 25. Ardayfio, E. (1986): The Fuel wood/Energy Crisis in Sub-Saharan Africa. Web Journal, United Nations University Press. http://www.unu.edu/unupress Asare, A. 2000. Operational guidelines on community forest (management) committees. ITTO/FSD Collaborative Off-Reserve Forest Management Project Belcher DW, Sherriff AC, Nimo KP, Chew GL, Richardson WD, Voros A, Feldman HA, Richardson WD, Feldman HA, 1977. Meningococcal meningitis in northern Ghana: epidemiology and control measures. Am J Trop. Med Hyg. 26: 748-755. CDC_US (1999). "Surveillance of morbidity during wildfires-central Florida, 1998." Morbidity and Mortality Weekly Report 48: 78-7. Chamblie, s and Schuutt. (2006). Making Sense of the Social World, Method of Investigation, Second Edition, Pine Forge Press, SAGE Publication, London. 40 Cleaver, K.M., and G.A. Schreiber. 1994. Reversing the Spiral: The Population, Agriculture, and Environment Nexus in Sub-Saharan Africa. Washington, D.C.: World Bank Corey J. A. Bradshaw, Navjots. Sodhiw, Kelvin S.-H. Pehwz and Barry W. Brook (2007). Global Change Biology (2007) 13, 2379–2395, doi:10.1111/j.13652486.2007.01446.x. Global evidence that deforestation amplifies flood risk and severity in the developing world. Durning, A.B. 1989. Poverty and the Environment: Reversing the Downward Spiral. Worldwatch Paper 92. Washington, D.C.: Worldwatch Institute. Charkraborty M 1994.An Analysis of the causes of deforestation in India. In K Brown, and D.W Pearce (Eds), the causes of Tropical deforestation (pp, 226-238). London: UCLpress. C.P. Hansen and Treue (1998). Assessing illegal logging in Ghana. Danish Centre for Forest, Landscape and Planning, Faculty of Life Sciences, University of Copenhagen, Rolighedsvej 23, 1958 Frederiksberg C, Denmark. Ehrlich, P.R. & Ehrlich, A.N. (1990). The population explosion. A touchstone book, New York. Enos K. Cerebrospinal in Ghana meningitis in northern Ghana: the experience of the War Memorial Hospital, Navrongo. 1997. Ministry of Health, Ghana. Dan Kammen.Disseminating Efficient cook stoves in Tanzania E. Wolfson, Brooklyn, NY. Tropical Rainforests: Nature’s Medicine Cabinet Falconer, J. 1992. Non Timber Forest Products in Ghana. Ghana. FAO 1999. State of the World’s Forests, the Food and Agriculture Organisation of the United Nations, Rome. 41 FAO 1997. Update on Sustainable forest management and certification: Example from developing country-Ghana, advisory committee on paper and wood products thirty eight sessions. Rome, 23-25 April, 1997 FAO 2001. Deforestation continues at a High Rate in Tropical Areas, State of World’s Forests, The Food and Agriculture Organisation, (FAO), Ro Flavio S. Anselmetti, Daniel Ariztegui, David A. Hodell Mark Brenner and Michael F. Rosenmeier. Quantification oil erosion rates related to ancient Maya deforestation Geology, October, 2007, v. 35, p. 915-918, doi:10.1130/G23834A.1. Feeny DH. 1988. Agricultural expansion and forest depletion in Thailand, 1900.1975. In World Deforestation in the Twentieth Century, ed. JF Richards, RP Tucker, pp. 112.43. Durham, NC: Duke Univ. Press Ghana Statistical Service (1999). The 1998 Ghana demographic and Health Survey (GDHS) Report. Accra. Gross, J. (2002). "The severe impact of climate change on developing countries." Medicine & Global Survival 7(2): 96-100. Hall, J. B. and Swaine, M. B. 1981. Distribution and Ecology of Vascular plants in Tropical Rainforest. Forest Vegetation in Ghana. 383 pp. Haines, A. and J. A. Patz (2004). "Health effects of climate change." Jama 291(1): 99-103 Hawthorne, W. D. 1989. The flora and vegetation of Ghana's forests. Ghana Forest Inventory Project. Proceedings of a seminar. J. Wong (Ed.). Accra. 29 h - 30th March 1989. ISSER. (1999). the state of the Ghanaian economy. University of Ghana, Legon. 42 IPCC. 2007. Climate change 2007: the physical science basis (summary for policy Makers), IPCC. ITTO. (2005a). Status of tropical management: ITTO Technical Series Note 24: Ghana (pp 98-104) J.K.A. Benhin and E.B. Barbier (1998).The Effects of Structural Adjustment programme on deforestation in Ghana. Kaimowitz, D. and Angelsen, A. (1998) Economic Models of Tropical Deforestation: A Review. Centre for International Forestry Research (CIFOR), Bogor, Indonesia. Kartawinata, K. 1994. The use of secondary forest species in rehabilitation of degraded forest lands. Journal of Tropical Forest Science 7: 76–86. Kant, S., Redantz, A (1997). An econometric model of tropical deforestation. Journal of forest economics 3(1), 51-86. Kasanga, K.R. 1998. Land tenure and development dialogue: the myth concerning communal landholding in Ghana. Occasional Paper No. 19. Cambridge, UK, Department of Land Economy, University of Cambridge. Kasanga, K. R. 2002 - Paper delivered to the Regional House of Chiefs in Kumasi, Ghana. Kotey, N.A., J. Francois, J. G. K. Owusu, R. Yeboah, K. S.Amanor, and L. Antwi. 1998. Falling into place. Ghana Country Paper. Policy that Works for People Series No. 4 International Institute for Environment and Development (IIED), London, United Kingdom. Retrieved 24thNovember 2004.http://www.iied.org/docs/flu/ptw/4ghana.pdf Kremen, C., J. O. Niles, M. G. Dalton, G. C. Daily, P. R Wilson Mary E. Infectious diseases: an ecological perspective. Departments of Population and International Health and Epidemiology, Harvard School of Public Health, 677 .Huntington Avenue, Boston, MA 02115-6023, USA. 43 Mott, J.A., et al., Wildland forest fire smoke: health effects and intervention evaluation, Hoopa, California, 1999. West J. Med, 2002. 176: p. 157-162. Nanang D. M. 2011. Analysis of export demand for Ghana’s timber products: A multivariate co-integration approach. Journal of forest economics 16(1)-47-61. Nsiah-Gyabaah K. 1996. Bureau of integrated development. IFFN No. 15 - September 1996, p. 24-29. University of science and Technology, Kumasi Ghana. Mann, R.D. (1990). Time running out: The urgent need for tree planting in Africa. The Ecologist, 20 (2). Manya Krobo District Assembly. Ekbom, A., and J. Bojö. 1999. Poverty and Environment: Evidence of Links and Integration in the Country Assistance Strategy Process. Africa Region Discussion Paper 4, World Bank, Washington, D.C. Ollenu, J. 1962 - Traditional Customary Practices in Ghana. Omran AR. The Epidemiological Transition in the US: Population Bulletin 1997; 32:3-42 Ostrom, E. 1990. Governing the Commons: the Evolution of Institutions for Collective Action. Cambridge: Cambridge University Press. Owusu-Bi, K. 1989. Environment development and vulnerability problems and prospects for environmental development in Ghana. Seminar paper. 2nd biennial SPRING Forum, U.S.T. Kumasi, April 1989. Pandey MR, Neupane RP, Gautama A, Shrestha IB. Domestic smoke pollution and acute respiratory infections in a rural community of the hill region of Nepal. Environ Int 1989; 15: 337–4. Potthoff, K. (ed.) 2005. Human Landscape Ecology (MNFEL 330/RFEL 3031). Selected TermPapers 2003/2004. Acta Geographica–Trondheim, Serie A, Nr. 10. Department of Geography, NTNU, Trondheim. 101 pp. ISSN 1502-2390 44 Professor Anthony J McMichael (1999) National Centre for Epidemiology and population health, the Australian national University, Canberra, Australia. Sarah H. Olson, Ronald Gangnon, Guilherme Abbad Silveira, and Jonathan A. Patz. 2010. Deforestation and Malaria in Mâncio Lima Count y Brazil. Sutherland, E.R., et al., Wildfire smoke and respiratory symptoms in patients with chronic obstructive pulmonary disease. Journal of Allergy and Clinical Immunology, 2005. 115(2): p. 420-42. Sutherland, N. 2002. Zambia: From Copper to Cultivation, Oxfam International, London. Waddy BB, 1957. African epidemic cerebrospinal meningitis. Journal of Tropical Medicine and Hygiene 60: 179-189. 8. White, F. 1983. The vegetation of Africa: A descriptive memoir to accompany the UNESCO/AETFAT/UNSO vegetation map of Africa. Natural Resources Research 20, UNESCO, Paris. 356 pp. Wilson, E. 2003. The Earth’s Environmental Woes: Is Agriculture Part of the Problem or Part of the Solution? World Development, Vol. 31 (11). Woods C, Armstrong G, Sackey S, Tetteh C, Bugri S, Perkins B, Rosenstein N, 2000. Emergency vaccination against epidemic meningitis in Ghana: implications for the control of meningococcal disease in West Africa. Lancet 355: 30-33 World Bank 2004. Implementation of completion report on a loan/loan/Grant to repulic of Ghana for national resource management. World Bank (1991) World Development Report 1991: the Challenge of Development. Oxford University Press, Oxford. World Commission on Environment and Development. 1987. Our Common Future, Report of the World Commission on Environment and Development. Oxford: Oxford University Press 45 46
© Copyright 2026 Paperzz