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Review Article
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Burden of Malaria at Household Level: A Baseline Review in the Advent of Climate Change
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Md. Shahin Mia,
Rawshan Ara Begum,
Ah-Choy Er,
Raja Datuk Zaharaton Raja Zainal Abidin
and
Joy Jacqueline Pereira
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ABSTRACT
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Malaria is the most serious public health problem in tropical and sub-tropical regions of the world. It has emerged one of the top three killers among the vector borne diseases in the world. Changes in climate factors greatly affect seasonal transmission and geographical distribution of malaria which causes great losses to the households in terms of costs of securing treatment as well as loss of output and income in endemic regions. This study aims to identify and review literature related to economic costs of malaria illness at household level. The study also focuses on the burden of the disease in terms of Disability-adjusted Life Years (DALYs) lost. Literatures were identified for review from various sources such as journals, reports, proceedings and other related documents by searching comprehensively both electronic and non-electronic databases. Websites of the organizations known to have undertaken research in this area were also searched to find related documents and reports. Based on the review of literature, it was found that costs of malaria vary by the socio-economic status of households and the poor spend a significantly higher proportion of their income on treatment and preventive measures for the disease. Direct cost of malaria consumed 28-34% of annual income of poor households and 1-2% of high income households. Studies revealed that indirect costs of malaria accounted for a significant portion of households annual income ranging from 2 to 6%. It was found that even under minimal climate change scenario, some African countries may face their inpatient treatment cost of malaria increase more than 20%. It can be concluded that illness of malaria imposes greater burden on poor households than the better-off. Minimizing the burden of the disease could help people, especially the poor to get out from the worst economic situation. Therefore, further research is urgently needed to ensure interventions to control the malaria disease more effectively in the advent of climate change. |
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How
to cite this article:
Md. Shahin Mia, Rawshan Ara Begum, Ah-Choy Er, Raja Datuk Zaharaton Raja Zainal Abidin and Joy Jacqueline Pereira, 2012. Burden of Malaria at Household Level: A Baseline Review in the Advent of Climate Change. Journal of Environmental Science and Technology, 5: 1-15. DOI: 10.3923/jest.2012.1.15 URL: http://scialert.net/abstract/?doi=jest.2012.1.15
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| Received:
May 04, 2011; Accepted: July 29, 2011;
Published: November 02, 2011 |
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INTRODUCTION
Malaria has emerged one of the most serious public health problems in the tropical
and sub-tropical regions (Lieshout et al., 2004)
which ranked major health and development challenges facing some of poorest
countries of the world (McCarthy et al., 2000).
The disease is prevalent in about 90 countries and territories in the tropical
and subtropical regions and almost one half of them are in Africa, South of
Sahara (Kumar et al., 2007). WHO
(2010) revealed that 35 countries in African region are high-burden countries.
It affects people of all ages, especially pregnant women and children as they
have less immunity. Similarly, people from all income levels (e.g., rich and
poor) within malaria-endemic regions suffer from morbidity and mortality of
the disease. In all infectious diseases, malaria continues to be one of the
biggest contributors to the global disease burden in terms of death and sufferings
(Martens et al., 1999). Egbendewe-Mondzozo
et al. (2011) reported that 243 million malaria cases and 863,000 deaths
occurred due to malaria in 2008 all over the world and 89% of the reported deaths
were in Africa. The geographical distribution of the disease is uneven as approximately
85% of all deaths and incidences of malaria occur in Africa (Lieshout
et al., 2004). It is one of the most serious vector-borne diseases in
the tropics. The vectors that harbor infectious diseases and transmit them to
humans are directly modified by ecological and meteorological factors (Patz
et al., 2005). The ecological factors also affect biologically productive
land and water resources and consequently humanity of a society (Begum
et al., 2009). Mosquito is a primary vector that infects human and
can transmit diseases such as malaria, dengue fever, Rift Valley fever, yellow
fever and West Nile virus (McMichael et al., 2006).
The female anopheles mosquitoes transmit the malaria parasites that cause malaria
infection in humans. The disease is governed by a large number of climate factors,
including temperature, rainfall and relative humidity which affect its reproduction,
distribution, seasonality and transmission intensity (Snow
et al., 1999; Zhou et al., 2004;
Garg et al., 2009; Halsnaes
and Traerup, 2009; Wandiga et al., 2010).
Climate change is adversely affecting not only public health but also other
sectors of the economy such as energy, industries, transport, forestry, agriculture,
water and coastal resources and waste sector (Begum et
al., 2011a). The impacts of climate change may vary across different
sectors of the economy and geographical location (Begum
and Pereira, 2011). For example, the study conducted by Mwang`ombe
et al. (2011) found that climate variability resulted in increased
dry conditions, crop failures, reduced livestock productivity and increased
livestock and human diseases, thereby complicating lives of communities in rural
areas of Kenya. The study on Jeddah city, Soudi Arabia reported that environmental
degradation affected adversely the water supply, air quality, health and safety
which resulted in increased economic costs to the community of the city (Magram,
2009).
Long-term climate changes, especially rising in temperature play a vital role
in determining the geographical distribution and severity of malaria, since
both vector and parasite of the disease are sensitive to temperature. Generally,
in warmer temperature, the anopheles mosquito develops more rapidly and feeds
more frequently and earlier in its life cycle and consequently the malaria parasite
within the mosquito develops and multiples more rapidly (National
Research Council, 2001). The major malaria parasite, Plasmodium falciparum,
can complete its development in most anopheline vectors at room temperature
(Ambu et al., 2003). Rainfall also contributes
significantly to malaria epidemiology. Malaria vectors e.g., mosquitoes breed
in standing water such as mud-pools, marshes and natural ponds. Therefore, rainfall
not only affects malaria transmission by increasing breeding sites for mosquitoes
but also increases the relative humidity which helps in survival and longevity
of adult mosquitoes (Martens et al., 1995; Garg
et al., 2009). Floods associated with increased El Nino rainfalls
have contributed to epidemics of malaria in Africa (Brown
et al., 1998; Greenwood and Mutabingwa, 2002).
In Iran, malaria transmission depends on seasonal and temperature variation
and reaches a peak in Autumn (November-December) when temperature increases
(Basseri et al., 2005). Another study assessing
the impact of climate change in Iran reported that malaria is prevalent in different
provinces of the country and the trend of incidence of the disease is on the
rise (Amiri and Eslamian, 2010). Similarly, in Uttaranchal,
India, malaria transmission is significantly correlated with climatic variables
(especially rainfall) and reaches its peak during monsoon and post-monsoon seasons
(June to September) (Devi and Jauhari, 2006). A small
seasonal change in host or pathogen factors may create large seasonal surges
in malaria incidences which may be important particularly in the context of
global climate change (Fisman, 2007).
Climate change increases the outbreak of malaria which places enormous burden
on humanity causing a lot of economic losses to the vulnerable people living
in endemic regions, in terms of costs of securing treatment as well as loss
of output and income. The poor and hardcore poor who have relatively larger
household members suffer most by the adverse impacts of climate change (Begum
et al., 2011b). Incidences of malaria also have huge welfare cost
and other impacts for individuals in the endemic countries (Halsnaes
and Traerup, 2009). In addition, the disease may impede the socio-economic
development of a country by imposing long-term negative impacts on trade, savings,
investment, tourism and human capital accumulation of the country. This study
aims to review studies that have measured the economic costs of malaria at the
household level. The study also focuses on the burden of the disease in terms
of Disability-adjusted Life Years (DALYs) lost. A number of studies have been
carried out mostly in low and middle income countries focusing on the economic
impacts of malaria for the patients and their families. Majority of them attempted
to measure direct and indirect costs of malaria illness to estimate the economic
impact of the disease at the household level. The Cost-of-illness (COI) method
is the most widely used approach for estimating direct and indirect costs. In
a few studies, a third category of costs of malaria illness has been described
as intangible cost. But it is the most controversial and not generally valued
(Chima et al., 2003). Recently some studies have
given effort to measure the burden of the disease in terms of Disability-adjusted
life years (DALYs) lost. However, this study does not focus on the macroeconomic
costs of malaria while a few studies have attempted to measure macroeconomic
impacts of the disease.
Technique of identifying and collecting literature: This study identified and selected literatures (for review) focusing on climate change and economic impacts of malaria at household level. Literatures were identified from various sources such as journals, reports, proceedings and other related documents by searching comprehensively both electronic and non-electronic databases. Literature searches from electronic databases were conducted mainly on Science Direct, Springer Link, Blackwell, Science Citation Index, Social Science Citation Index, Medline, PubMed, PubMed Central and WHOLIS using a range of key words relating to climate change and economic impacts of malaria illness. References cited in the literatures were searched and important studies were collected in full text. Websites of the organizations known to have undertaken research in this area were also searched to find related documents and reports. In addition, both electronic and non-electronic searches were also supplemented by a network of colleagues who provided related literatures and documents. In the review process, only the documents written in English were considered and there was no country restriction. This study reviewed the literatures that included discussion and demonstrated findings and evidences related to climate change, costing of malaria illness and its impacts on the household economy.
Assessing economic impacts of malaria at household level: This review
is based on data, information and findings from published literatures and documents
that focus on and discuss economic costs of malaria at the household level either
or not from the view of climate change, depending on the availability of literatures
and documents. Costing of malaria at the household level includes the direct,
indirect, intangible and total costs that are discussed below.
Direct costs of malaria at the household level: Evidences demonstrate
that households in malaria endemic regions face a substantial amount of direct
cash expenses which can be classified into two broad categories: expenditures
on malaria prevention and expenditures on treatment. With respect to malaria
prevention, households in endemic countries rely largely on insecticide treated
(mosquito) nets and indoor residual (house) spraying though they also use mosquito
coils and mosquito repellent lotions (Yukich et al.,
2008). Treatment seeking and usage of preventive measures for malaria vary
to different degrees across geographic and seasonal differences and accordingly
the costs for malaria prevention and treatment vary by different degrees (Ewing
et al., 2011). Table 1 summarizes households
expenses on malaria prevention and treatment from the different parts of the
world. The differences in expenditures for malaria prevention among households
might be due to epidemiological factors, e.g., the prevalence of different malaria
species and immunity levels and socio-economic factors, e.g., income levels.
For example, in Malawi, only 4% of very low income households spent resources
on malaria preventive measures compared to 16% of low to high income households
(Ettling et al., 1994). In the republic of Benin,
estimated annual expenditure on malaria prevention constituted 1.6% of rural
and 2.1% of urban household income (Rashed et al.,
2000). But there is still inadequate relevant data and information on this.
Moreover, most of the studies avoided estimating prevention expenditures on
annual basis and its consequent economic impact on households due to lack of
good information and data on seasonal distribution of malaria, households
economic activities and availability of cash throughout the year (Chima
et al., 2003).
Household expenditures on malaria related treatment include direct medical
and non-medical costs. Direct medical costs are the cash expenditures for doctors
fees, laboratory tests and drugs. On the other hand, direct non-medical costs
include direct payments for food, lodging, transport charges to and from health
care facilities or drug stores and miscellaneous expenses associated with seeking
and obtaining medical care as well as household members visiting patients at
hospital or clinic. Furthermore, Attanayake et al.
(2000) demonstrated complementary cost of treatment for malaria
which included cost of vitamins, nutritional food, special foods and drinks
and constituted a significant portion of the total treatment costs. Like prevention
costs, household expenditures on malaria treatment vary by different degrees
in different areas and households (Table 1). This difference
is due to user fees in public health care facilities, costs of drugs and laboratory
tests and so on. For example, in Sri Lanka (rural) households direct costs
for malaria treatment found much lower due to free treatment at public hospitals.
Free hospital treatment is a core component of the Sri Lankan governments
universal coverage policy that aims to protect the majority, particularly the
poor, from catastrophic illness costs (Russell, 2004).
It is also noticed that malaria treatment costs vary from rural to urban areas
in the same country or region.
Studies suggested that the direct medical costs constitute a higher proportion
of total treatment costs borne by households (Table 2). The
choice of households to use health care facilities is determined by many factors
such as accessibility to health services, availability of drugs, quality of
care, distance to the health care facilities from household, travel time, household
size and user fee policy (Rutebemberwa et al., 2009).
In Ghana, the comparatively high medical cost of malaria was linked to drug
costs at public health care facilities and private drug stores. On the other
hand, in Sri Lanka, the relatively low direct cost of treating malaria (Table
1) was due to low medical costs. The low level of medical costs was due
to free treatment in public hospitals in Sri Lanka.
Evidences indicate that the direct costs of malaria consume a significant portion
of households income, monthly or annually, as shown in Table
3. Households have to pay in full the expenses for treatment at the time
of illness when income may be lower than usual due to inability of carrying
out normal activities or attending the sick person for treatment. In addition,
households have to make informal payments (e.g., illegal payments) in public
health care facilities which contribute to the high cost of malaria treatment
(Onwujekwe et al., 2010). Households direct
costs are also inflated by peoples widespread preference to use private
doctors and pharmacies for outpatient treatment, particularly in urban areas
and even by the poorest. For example, In Ghana, malaria patients had to pay
quite a significant amount of money to purchase drugs from private drug stores
as public health care facilities could not provide all the drugs prescribed
(Asenso-Okyere and Dzator, 1997). Similarly, patients
receiving treatment only from private clinics had significantly larger average
cost of treatment in Vietnam (Morel et al., 2008).
Ettling and Shepard (1991) observed comparatively high
treatment costs from private health care facilities in Rwanda where households
direct expenses, on the average, were $0.39 in public health centers and $3.36
in private facilities (which is almost six times of expenses occurred at public
facilities).
| Table 2: |
Direct medical cost as a proportion of household is total
treatment cost |
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| Table 3: |
Direct costs of malaria to households |
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| Source: Adapted from Mia et al.
(2011) |
The factors that make people reluctant to use public health facilities are
limited resources, inadequate staff and lack of essential drugs (Hopkins
et al., 2007). Other factors are poor quality of care and lack of
services after working hour at public hospitals as well as better attention
to the patients at private clinics. Inadequate health-care infrastructure is
a major barrier for malaria treatment in many African countries (Moerman
et al., 2003). In coastal India, a higher proportion of malaria patients
did self medication usually with antimalarials and did not seek medical attention
(Unnikrishnan et al., 2008). A study conducted
in Nepal found that almost 50% of the respondents did not have information on
availability of free treatment of malaria though it is available in Nepal (Joshi
and Banjara, 2008).
Few studies compared how cost burdens vary by socio-economic status of households
and found that costs of malaria treatment were highly regressive, imposing a
greater burden on poor families than the better-off families (Table
3). For example, direct cost of malaria consumed 34% of annual income of
poor households and 1% of annual income of rich households in Northern Ghana
(Akazili et al., 2007). In the republic of Benin,
the direct cost of malaria among the rural households was 3.3% of annual income
while it was 2.4% of annual income of the urban households (Rashed
et al., 2000). The study conducted by Leighton
and Foster (1993) found that the typical rural households in Kenya and lower
income urban households in Nigeria were the hardest hit by the economic impacts
of malaria. The poor households have to meet the treatment costs and purchase
preventive measures for malaria out of their scarce cash reserves which push
them into vulnerable situation.
However, some studies also focused on the impact of seasonal variations in
the cost burdens of malaria. For example, a study in Kenya reported significantly
higher malaria transmissions in the wet season (64%) than in the dry season
(37%) (Chuma et al., 2006). The same study showed
that mean direct cost burdens of malaria were 7.1% of total household expenditure
in the wet season and 5.9% in the dry season. Present study also reported that
people were keen to avoid public health care facilities in the wet season and
were better able to meet relatively high private clinic costs.
| Table 4: |
Indirect cost of malaria morbidity as a proportion of households
total cost |
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| Table 5: |
Indirect costs of malaria as a proportion of household income |
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In Assam, India, Baruah et al. (2007) recorded
the highest overall density of malaria vectors during the monsoon period (June-August)
followed by post-monsoon (September-November) and pre-monsoon (March-May) and
lowest in winter season (December-February). This study also revealed that the
densities of malaria vectors were influenced by rainfall pattern. Unfortunately,
this study did not explore the impact of seasonal variations on direct costs
of malaria treatment.
Households indirect costs for morbidity and mortality of malaria:
Evidences show that households loss productivity due to morbidity and mortality
of malaria which can be termed as indirect cost of the disease. It is an important
determinant of economic costs of malaria. Households incur indirect costs in
terms of income or wage lost, school days missed and reduced productivity and
output due to morbidity of malaria. The scope of indirect cost measurement varies
considerably across studies: some only include economically active individuals
but others include children and the elderly; mostly measure the time spent seeking
treatment by the patient and caregiver and their loss of productive labour time
due to illness (Russell, 2004). Key variables are thus
the amount of productive labour time lost and the assumed value of that time.
But, there is a great variation between studies in the methods used for valuation
of productive labour time lost of the patient and caregiver. The method used
in most of the studies is the wage rate method which relies on the relationship
between wage and the value of labour. Some studies used age specific average
wage while others applied economic activity or gender specific average wage
to value the time lost. Other methods include mean daily income, average daily
output per adult, average income per day, average agricultural wage and market
value of average output.
Studies reveal that the indirect cost of malaria morbidity constitutes a significant
proportion of total malaria costs borne by households (Table 4).
Indirect cost due to malaria illness may be lower in settings where young children
are affected by the disease than in settings where both adults and children
are equally vulnerable to the disease (Chuma et al.,
2010). Evidences also showed that indirect cost of malaria imposed a greater
burden on the households, especially the poor. Table 5 shows
indirect costs of malaria that contributed to the proportion of households
annual income ranging from 2 to 6% for the Nigeria, Malawi and Sri Lanka. It
can be noticed that income losses due to illness of malaria can be of great
economic significance to households and poor families experience higher burden
than better-off families. For example, In Malawi, Indirect costs among the very
low income households were accounted to be 3% of the total annual household
income and 2% of the annual income among the low to high income households (Ettling
et al., 1994).
Households in malaria endemic regions are also affected by the disease through
its effects on their childrens attendance and performance at school. Repeated
illness of the school-age children from malaria causes high rates of absenteeism
which result in childrens poor educational performance, increased failure
rates, repetition of school years and drop-out from school (Malaney
et al., 2004). Holding and Kitsao-Wekulo (2004)
revealed that school-age children in endemic areas face 15% of health-related
absenteeism from school due to illness of malaria. For example, the study conducted
by Leighton and Foster (1993) in Kenya found that primary
school children missed an estimated 20 school days, on the average, per year
due to malaria which amounts to over 10% of the total school days. The study
also estimated that secondary school students missed 8 school days per year.
In Sri Lanka, children lost 10% of school days due to malaria during the high
transmission season (Konradsen et al., 1997).
Similarly, in Ghana, school children lost, on the average, 4 school days due
to malaria illness (Asante and Asenso-Okyere, 2003).
Malaria also imposes significant economic burden to households by causing the
permanent loss of productive labour time through premature death. With regard
to work output and earnings, life lost to disease through premature death is
an indirect cost to households and society in general (Asenso-Okyere
and Dzator, 1997). Premature death of an economically active workforce destroys
permanently the potential output to household. At the same time, his/her contribution
to the Gross Domestic Product (GDP) is lost to society. However, the estimation
of indirect cost due to premature death is difficult as it requires sophisticated
methods to value the stream of future earnings. In this case, the lost income
can be estimated by calculating the capitalized value of future lifetime earnings
that would have been gained by those who died prematurely from malaria (Halsnaes
and Traerup, 2009). Evidence on mortality costs of malaria found very limited
due to lack of adequate data on age and sex-specific causes of death. In Rwanda,
Ettling and Shaperd (1991) have attempted to estimate
the mortality cost of malaria by calculating present value of the stream of
future earnings lost due to premature death. Present study showed that mortality
cost accounted for 74% of total indirect costs of malaria in Rwanda. Approximately
50% of all reported malaria deaths were in adults. The significant proportion
of malaria mortality among adults in Rwanda made extremely high cost of premature
death. Perhaps, most of the studies avoided the estimation of economic costs
of malaria mortality, paying attention to the effects of morbidity only. Therefore,
it is necessary to focus more on the mortality consequences of malaria especially
in areas where adults are at risk of malaria.
Total costs of malaria: The direct and indirect costs of malaria have
been summed in order to get estimates of total economic costs. Several studies
estimated total economic costs of malaria in terms of the proportion of households
income as shown in Table 6. It is found that households suffer
greatly from the burden of malaria because the direct and indirect costs of
a single case/episoded deplete a significant portion of a households income.
For example, In Kenya, total cost due to illness of malaria consumed, on average,
28% of monthly income of the households (Chuma et al.,
2010). In Vietnam, households expenditure on malaria constitutes,
on average, 13% of their income per month (Morel et al.,
2008).
| Table 6: |
Total costs of malaria as a proportion of household income |
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It is also found that the poor households bear the greatest burden of malaria
as they have to spend a significantly higher proportion of their income on treatment
and preventive measures for the disease and loss income due to ill health or
attending the sick person for treatment. For example, the average total cost
of malaria among the very low income households was 32% of annual income compared
to 4.7% among the low to high income households in Malawi (Ettling
et al., 1994). A brief period of illness cause catastrophic consequences
for families which may push them into poverty or force into deeper poverty (McIntyre
et al., 2006). On the other hand, poverty can contribute to high
transmissions of malaria in the poor countries. For example, malaria is widely
prevalent in the poor countries of Africa and Asia. But malaria is not a direct
consequence of poverty. The incidence and severity of the disease are mostly
determined by climate and ecology (Gallup and Sachs, 2001).
This study was conducted by McCarthy et al. (2000)
also confirmed that climate played a dominant role in accounting for cross-country
differences in malaria morbidity. Recently, Egbendewe-Mondzozo
et al. (2011) conducted a study in 25 African countries to assess
the relationship between climate change and malaria incidences and attempted
to estimate the potential economic consequences from climate change. The study
was found that even under minimal climate change scenario, some countries, e.g.,
Burundi, Cote DIvoire, Malawi, Rwanda and Sudan may face their inpatient
treatment cost of malaria increase more than 20%. The subsistence farmers in
rural tropical areas, especially in Africa shoulder the greatest burden of the
disease because they are mainly dependent on agriculture and their margin of
survival is so fragile (Mia et al., 2011).
Intangible costs of malaria: There is another type of cost of malaria
illness, for example cost of pain, suffering and loss of leisure time due to
illness, that cannot be easily quantified monetarily and is known as intangible
cost (Massad et al., 2011). Although the Cost-of-illness
(COI) approach theoretically includes the cost of pain and suffering, it is
generally excluded from calculations because it is difficult to assess (Malaney
et al., 2004). An alternative approach that is capable of measuring
the intangible cost is the Willingness-to-pay (WTP) approach. This approach
was originally developed to assess the value of intangible items in the environmental
field such as clean air or improved water quality. However, WTP approach is
now frequently used in health, social and environmental programs for price setting
and cost-benefit analyses (Uzochukwu et al., 2010).
There are very limited studies focused on intangible cost of malaria. In Nigeria,
one study applied the WTP approach to evaluate the burden of malaria on households
through the contingent valuation method based on a cross-sectional household
survey (Jimoh et al., 2007). The study assumed
that the difference between the amount people are willing to pay to malaria
eradication and control and the current costs for malaria treatment and prevention
would be taken as the household valuation of the intangible costs of malaria
illness. The results of this study showed that households would be willing to
pay $3.6 in excess of the average current expenditure on malaria treatment per
month and $22.6 in excess of the current costs for protection and control of
malaria. The average valuation of households intangible costs represented
$5.1 per head per month, $61.2 per year. Asante and Asenso-Okyere
(2003) applied the WTP technique in Ghana, reported that households would
be willing to pay, on the average, $14.1 to avoid malaria. They also found that,
in general, as peoples income increase they would be willing to pay more
for the control/eradication of malaria in their household. However, the application
of WTP approach is limited due to difficulties in obtaining relevant data for
valuation. Moreover, there are many criticisms against this type of studies
for being too hypothetical and generating results with low validity, as the
results depend completely on the choice of the respondents (Saulo
et al., 2008). Since, a respondent in this situation does not have
to pay the amount he/she states, he/she may not provide accurate answers or
may respond technically to influence the outcome of the study.
Burden of malaria in terms of Disability-adjusted Life Years (DALY) lost:
Recently a few studies have attempted to estimate the burden of malaria in terms
of DALYs lost. DALY is a new indicator of the burden of disease which estimates
the amount of time, ability or activity lost by an individual from disability
or death because of disease (Murray, 1994). It is calculated
as the sum of: (1) years of life lost due to premature death (YLL) and (2) years
of life lived with disability (YLD). In DALY approach, effort has been provided
to better define disease-specific mortality rates (Snow et
al., 2003). Internationally this method has gained popularity in the
last decade. It offers a standardized measure of morbidity and mortality that
is comparable across various conditions and geographic regions, serves as a
useful tool for resource allocation, cost-effectiveness analyses as well as
assessment of the burden of disease (Clark et al.,
2005). In Africa, it was estimated that 39 million DALYs were lost due to
malaria in 1998 and 36 million DALYs in 1999 (World Health
Report, 1999). Present study by Dash et al. (2008)
reported that malaria might be responsible for loss of about 2.3-2.5 million
DALYs in the Southeast Asia region in 1998. Kumar et
al. (2007) computed DALYs lost because of malaria in India for 1997.
It was estimated that DALYs lost were 0.786 million years among females versus
1.074 million years in males. In Sudan, malaria related morbidity and mortality
caused loss of 2,877,000 DALYs in 2002 (Abdalla et al.,
2007). Present study also found males having the highest incidence and mortality
but females losing more DALYs. Unlike the Cost-of-illness (COI) approach, however
the DALY method does not provide any monetary value of the burden of disease.
CONCLUSION The fact is that there is very limited study on costing and economic impacts of malaria at household level, particularly in the advent of climate change. This is partly attributable to the limited availability of suitable data and information of malaria morbidity and mortality due to climate change as well as variation in methods and approaches to estimate and quantify the costing and impacts of the disease. The comparison of results and findings from different studies cannot be done directly due to lack of common methodology. In particular, there is limited study on economic impact of malaria by socio-economic status of households and especially its impact on the poorest. Poor families are the hardest hit by the disease due to climate change because they are not financially sound enough to purchase preventive measures and to seek prompt effective treatment. To select the suitable approach that meets the needs of the research and study is also difficult due to limitation of existing data, assumptions and estimates. Therefore, future research is very much needed for understanding the impact of climate factors on malaria and monetary valuation of economic burdens of the disease in order to set target and control efforts in a more effective manner to minimize the burdens of the disease. More cooperation and collaboration between biophysical scientists and economists is also necessary for a clear understanding of economic impacts of malaria due to climate change. ACKNOWLEDGMENT Present study is funded and supported by the Dana Operasi Universiti Penyelidikan (Ref. No. UKM-OUP-PI-25-111/2009), Arus Perdana (Ref. No. UKM-AP-PI-18-2009/3) and Grant Universiti Penyelidikan (Ref. No. UKM-GUP-PI-08-35-083) in the Universiti Kebangsaan Malaysia (UKM), Malaysia.
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