European Journal of Social Sciences Studies
ISSN: 2501-8590
ISSN-L: 2501-8590
Available on-line at: www.oapub.org/soc
Volume 2 │ Issue 2 │ 2017
doi: 10.5281/zenodo.438079
INCREASE IN DEFORESTATION: A KEY CHALLENGE TO
HOUSEHOLD CHARCOAL SUPPLY –
A CASE OF TANGA URBAN, TANZANIA
Rahma Mohamed Msoffei
The Open University of Tanzania,
Dar es Salaam, Tanzania
Abstract:
This study investigated an increase in deforestation and its impact in charcoal supply
for households in Tanga district (urban). Tanga district was chosen because it has high
urban population as compared to her neighbor Districts of Muheza and Mkinga. The
district was also chosen because it is so close to natural and reserved forests in both
Muheza and Mkinga districts in which effect of deforestation on charcoal supply can be
clearly seen and determined. The study involved 61 respondents including
(households, charcoal venders and forest officer). Questionnaire survey, interview and
documentary review methods were employed in data collection. A quantitative data
were analyzed using Statistical Package for Social Sciences (SPSS 20th version). While
qualitative information was analyzed using content analysis. The study findings show
that majority 56 (92%) of the respondents reported that there is high rate of
deforestation which was mainly contributed by charcoal production in the study area.
The study further revealed that the observed high rate of deforestation affect the
availability and supply of charcoal for domestic use. The scarcity of charcoal coupled
with high and fluctuating price give the evidence on presence domestic energy crisis in
the study area. Along with other recommendations, the study recommends that the
Government Regulator (Energy and Water Utilities Regulatory Authorities - EWURA)
should consider reducing tariff on other sources of energy particularly gas and
electricity to allow many people afford and resorting to alternative energies for their
domestic use and hence reduce the extent of deforestation.
Keywords: deforestation, household charcoal consumption, fuel wood crisis
Copyright © The Author(s). All Rights Reserved.
© 2015 – 2017 Open Access Publishing Group
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INCREASE IN DEFORESTATION: A KEY CHALLENGE TO HOUSEHOLD CHARCOAL SUPPLY –
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JEL: Q23, Q21, R23
1. Introduction
Historically, forests have played a major role to influence patterns of economic
development, supporting livelihoods, helping structure economic change, and
promoting sustainable growth (UN, 2013). Forests are more than trees, are fundamental
for food security, and improved livelihoods (FAO, 2016). The forests of the future will
increase the resilience of communities by: providing food, wood energy, shelter, fodder
and fiber; generating income and employment to allow communities and societies to
prosper; and harboring biodiversity (Ibid). They will support sustainable agriculture
and human well-being by stabilizing soils and climate, and regulating water flows
(FAO, 2016). Forests also provide substantial levels of employment whereas more than
13 million people are employed in forest formal and informal sector (UN, 2013). Forests
are also very potential in reduction of total greenhouse gas emissions produced from
other sectors of economy (Ibid).
Forests cover almost third of the earth’s land surface FAO, 2010). In Africa
forests currently cover about 23% of the land, however about 75% of hectors of
forestland converted to other uses between 1990 and 2010 (FAO, 2012). Tanzania has
about 48 million ha of forest cover which is approximately 55% of her forest, woodland
cover provides people with various benefits, and services (Malimbwi, 2014) cited in
Kessy et al (2016).
However, there is significant change in ability of forests to provide important
goods and service including employment, wood products, non-wood forest products
and services (FAO, 2016). It was indicated that, natural forest area is decreasing, the
global annual net loss of natural forests decreased from some 10.6 million ha in the
1990s to 6.5 million ha between 2010 and 2015 (Ibid).
Indirectly deforestation has been influenced by Population growth, while
agriculture, logging, mining, oil extraction, urbanization, wood fuel production and
acidic rain being the direct cause (FAO, 2007). According to the United Nations
Framework Convention on Climate Change (UNFCCC), about 80% of deforestation is
resulted from need of agricultural land (Goldstein, 2016). In Democratic Republic of
Congo for example, agriculture appears to be the main driver of deforestation and its
impact will likely increase as the population grow (Tchatchou et al, 2015).
Operationally, logging can interact with other drivers of deforestation, in many
instances logging creates partially cleared areas, which become accessible by logging
roads, and can therefore be more easily converted to agriculture, preventing the forest
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INCREASE IN DEFORESTATION: A KEY CHALLENGE TO HOUSEHOLD CHARCOAL SUPPLY –
A CASE OF TANGA URBAN, TANZANIA
from growing back (Boucher et al, 2011). Illegal logging on the other hand increase the
extent of deforestation as it undermines governmental regulations and hence destroys
large parts of the forest, because, unlike the legal logging, it is hardly ever paired with
reforestation efforts (Goldstein, 2016). Therefore, the paper set out to examine the
relationship between deforestation and wood fuel (charcoal) crisis in Tanga DistrictTanzania.
3. Overview of the Study
3.1 Extent and Rate of Deforestation
Definitions of deforestation vary, because deforestation is not official until tree cover
has fallen below the national thresholds for forest (WRI, 2000). Deforestation can be
defined as the conversion of forested areas to non-forest land through cutting, clearing,
and removal of rainforest or related ecosystems into less bio diverse ecosystems such as
pasture, cropland, or plantations, urban use, logged area, or wasteland (Kricher, 1997)
Cited in (Mahbub, 2008). Deforestation can also be defined broadly to include not only
conversion to non-forest, but also degradation that reduces forest quality, the density
and structure of the trees, the ecological services supplied, the biomass of plants and
animals, the species diversity and the genetic diversity (Mahbub, 2008).
Deforestation and forest degradation therefore are undoubtedly part of the
largest environmental problems facing the world today, of which the 16 million square
kilometers of forest that once covered the earth’s surface only . million remain up to
date, 2.3 million have been destroyed between 2000 and 2012 (Goldstein,2016). Statistics
show that there is net annual loss of 56.3 million hectares of forest cover all over the
world (FAO, 2003; WRI, 2000). Study by CIFOR, (2001), show that tropical forests are
being destroyed in an alarming rate all over the world. Estimates show that more than 5
million hectares are being converted into poorly managed secondary vegetation and it
was projected that forest cover will continue to be depleted at more or less rates in the
year 2020 (FOSA, 2003). If the current rate of deforestation continues, the world's rain
forests will vanish within 100 years causing unknown effects on global climate and
eliminating the majority of plant and animal species on the planet (Ibid).
Although developed countries in Europe also suffer deforestation resulting from
acidic rain caused by industrial pollution, they are highly concerned with
environmental management and conservation leaving deforestation problem to be a
major challenge to development of developing countries than developed (FAO, 1982).
In western Europe for example, deforestation rates declined as a result of several
factors, such as improvements in the productivity of existing agricultural land; an
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A CASE OF TANGA URBAN, TANZANIA
increase in timber imports from other parts of the world; and the replacement of wood
fuel by coal as the main source of fuel (FAO, 2016).
In third world countries, more than 11 million hectares of forest are cleared
annually (WRI, 2000). At regional level, South America suffered the largest net loss of
forests between 2000 and 2010 whereas about 4.0 million hectares of forest cleared per
year, followed by Africa, which lost 3.4 million hectares annually (FAO, 2010). Country
wise, Burundi reported to be the second largest country with high deforestation rate in
the world, followed by Togo and Mauritania (Rademaekers et al, 2010). Other country
with high deforestation rate in Africa includes: Ivory Coast with 5% per year and
Nigeria with 6% per year (WRI, 2000).
Tanzania has about 48 million ha of forest cover which is approximately 55% of
her forest and woodland cover, however, this amount of forests cover expected to be
reduced to 28.4 million hectares by the year 2020 ( FAO, 2003; Malimbwi, 2014).
Although the rate of deforestation is increasing yearly, the precise extent cannot
accurately be measured due to the remoteness of many areas from which the forest is
removed. National forest inventories are frequently outdated and non-comparable;
many forest conversions go unrecorded or are illegal (WRI, 2000). In Tanzania for
example, there is an agreement that the country is deforested but there is no agreement
on the extent of depletion as there is a wide variation in data explaining the extent of
forest depletion (Ministry of Land Natural Resources and Tourism, 1989). Despite the
disagreement on the extent of deforestation, various studies show that there is
widespread loss of trees in most parts of the country (Nkonoki, 1983; Kikula, 1988;
Reeds, 1996, Malimbwi, 2014; Lusambo; 2016).
3.2 Situation of Charcoal Consumption
Traditional sources of energy in the form of firewood and charcoal account for over 80%
of the total energy use in sub-Saharan Africa (Belward et al, 2011). Charcoal meets most
of the gap and more than 95% of the urban demand (Ibid). Global production of wood
charcoal was estimated to be 47 million metric tons in 2011(FAO 2013). Since 2003,
global production of charcoal has increased by 11% whereas more than 80% of this
wood-based energy is used for domestic purposes; due to population growth coupled
with increasing urbanization (Ibid).
Recently, there is decline in wood fuel consumption in developed countries due
to increase in use of fossils fuel (FAO 2014). Thus, wood fuel remains the important
source of energy for developing countries particularly for poor people (Ibid). Statistics
show that global charcoal consumption is 45% million ton/year, with a great variation
across the region whereas Africa consume 27% million ton/year, Latin America and the
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A CASE OF TANGA URBAN, TANZANIA
Caribbean 17%, Asia and Oceania 5% ton/year, (FAO, 2014). It was indicated that Africa
has higher household biomass energy consumption than other developing regions due
to presence of higher share of fuel wood and other biomass as compared to Asia and
South America (UN, 1999). In SADC Region, it was indicated that more than 60 million
people rely upon biomass in form of charcoal and firewood for their household use
(Munslow et al, 1988). About 91% of Ugandans both household and public institutions
use wood -based energy for cooking, lighting and baking (Alvarez et al, 2014).
In Tanzania, fire wood and charcoal accounts for 91% of total domestic use
(Nkonoki, 1983; Mnzava, 1984; Alvarez et al, 2014; Lusambo, 2016). Tanzanian energy
balance is dominated by biomass-based fuels, particularly firewood and charcoal which
account for more than 90% of primary energy supply (Lusambo, 2016). It was estimated
that with the rapid population growth, urbanization and the increase in cost of
alternative fuels, the demand for charcoal is expected to double in Africa by 2030
(Arnold et al. 2006; GiZ, 2009). The status of energy consumption in Tanzania as other
developing countries is highly characterized by low per capital income that indicating
presence of wood fuel crisis (Nkonoki, 1983; Kjellstrom, 1992).
3.3 Wood fuel crisis
The wood fuel crisis appeared to be a classic case of rising energy demand outstripping
supply. Although the resources in this case were renewable, unlike oil, gas and coal
they were apparently being over-used at unsustainable rates (Mearns and Leach, 1989).
The dynamics of the fuel wood situation in Africa represent a growing crisis, whereas
population pressure coupled with increased in rate of deforestation has created acute
wood-fuel shortages in most of Sub Saharan African Countries (Schandorf, 1990). Africa
has the highest birth -rate of any continent and also the world’s highest urbanization
rates with an average urban growth rate of 4% per year (Belward et al, 2011). The
growth in urban population is directly linked to a growth in charcoal demand. Every
1% increase in the level of urbanization is estimated to result in a 14% increase in the
consumption of charcoal (ibid).
Statistics show that in 1980, 55 million people in Sub- Saharan Africa lived in
areas where there was acute fuel wood scarcity and another 146 million lived in areas
with an increasing deficit, it is estimated that by the year 2000 about 535 million people
will experience a critical fuel wood deficit if exploitation of forest continues at the
current rate (Schandorf, 1990).
Evidence of fuel wood crisis in Tanzania is shown by annual fuel wood deficit of
18 million cubic meters in 1983 which forecasted to reach 25 cubic meters in 1985
(Nkonoki, 1983). The wood deficit was expected to continue to grow at a rate of 19.5m 3
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A CASE OF TANGA URBAN, TANZANIA
in 2012 and will continue to increase to 47.2 million m3 in year 2030 (Ishengoma, 2015).
Commercialization of fuel wood is increasingly entering the commercial sector in the
big towns and other small rural based township where most of household rely on
charcoal/fire wood for their domestic use (Nkonoki, 1983; Kaale, 1985). In Zambia for
example, Ministry of Tourism, Environment and Natural Resources (2007) indicates
that extended droughts and an increasing prospect of forest fires threaten the country’s
forests and could reduce the availability of biomass as a local energy source, directly
affecting low income families that depend on biomass for cooking and lighting.
Despite the increase in demand of fuel wood in Tanzania there is no plan to
sustain the supply. The situation that lead to fuel wood crisis (Mwandosya and
Luhanga, 1983; Mnzava, 1984). The overview of Tanzania energy policy (1992), show
that fuel wood as non-commercial energy is not given much attention despite the fact
that it is a dominant source of domestic energy for more than 90% of the population in
the country (Kjellstrom, et al, 1992). Dewees (1989), argue that fuel wood scarcity could
result into increased deforestation, changes in cooking and eating habits, and the
emergence of fuel wood markets. This is particular true from the study area where
various charcoal market centers have been established in Tanga Urban. Jones, (2015)
commented that large charcoal markets for example, have evolved across Liberia, leads
to the increase in transportation of charcoal from the interior to the coastal urban center
for shipment to neighboring countries.
The scarcity of wood fuel and the rapidly growing population has encouraged an
alarming rate of deforestation that manifested itself in wood fuel (charcoal/ fire wood)
crisis. The situation will in turn jeopardize livelihood of many people in developing
countries especially in Sub-Saharan due to the fact that over 80 percent of households
are still heavily rely on traditional fuels (IEA 2010). Mearns and Leach, (1989) claimed
that, in rural areas, the distance and time to collect wood fuels is commonly used as the
yardstick of scarcity and the need for remedies. For urban centers, it is commonly
assumed that wood fuel prices will rise as forest stocks are depleted and the transport
distance from the city to its main wood fuel resources lengthens.
4. Methodology
4.1 Study design
The study used case study research design. Miles and Huberman (1994) define a case
study as the investigation of a phenomenon occurring within a specific context.
Furthermore, Gall, Gall & Borg (2007), Case study has been chosen so as to save time
and obtain in depth information about the increase in deforestation a key challenge in
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household charcoal supply. Both qualitative and quantitative research approach were
used.
4.2 Study area
The study was conducted in Tanga urban district, one of the districts in Tanga Region.
The District has been chosen because of the researcher’s familiarity, high population
compared to other districts and numerous forests in the neighbor districts (Muheza and
Mkinga).
4.3 Study population
Population is defined as the total number of subjects or the total elements of interest to
researcher (Kothari, 2004). In this study, the target population was both men and
women from the selected household randomly. The choice of both genders is due to the
fact that the group has more chance of making decision as far as domestic energy
consumption concerned. The study also involved charcoal venders from Tanga Urban
and forest officer who had enough knowledge and experience concerned forest and
charcoal production.
4.4 Sample size and sampling procedures
In this paper, simple random sampling procedure was used in selecting the required
number of household members form the study area. In other hand Purposive sampling
procedure used in obtaining key informants such as forest officer (Tanga district) and
charcoal venders from the study area, because they were considered by researcher to be
more knowledgeable about the cultural arena of the study area.
4.5 Data collection methods
In this paper questionnaire survey, interview and documentary review methods were
used in data collection. For example survey method was used in capturing information
of 61 household members (including men and women) relaying in charcoal use.
Interview was used in capturing data like extent of charcoal production in
deforestation, the price of charcoal and the current situation of charcoal availability that
could not captured through questionnaire. Data obtained through household
questionnaire analyzed quantitatively while information captured through interview
analyzed qualitatively.
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5. Results and Discussion
The findings on deforestation a key challenge to household charcoal supply were
discussed as follows.
The respondents were asked whether charcoal production contribute to
deforestation or not. The findings revealed that 56 (92%) of the respondents agreed that
charcoal making contribute largely to the loss of forests compared to 5(8%) who
disagreed with the statement (Figure 1). Equally, in Paraguay the production of
charcoal and the harvesting of firewood are considered as the key drivers of
degradation and devastation of forests after agricultural expansion (Alvarez et al,
(2014).
Probably it attributed by the increase of charcoal demand in urban household for
domestic use including cooking, boiling water and ironing clothes. Contrary to this
study, Jones (2015) suggested that, charcoal production is not an initial driver of
deforestation, but it follows timber harvesting. Similarly, Regional studies by WRI
(2000) indicated that two thirds of wood fuel (charcoal) worldwide comes from nonforest sources that includes alternative sources for collecting fuel wood; from logging,
wood industries residues and from agroindustry plantations.
Figure 1: The contribution of charcoal making in deforestation
Source: Field data, 2017
5.1 The extent to which charcoal production cause deforestation
The respondents were further asked to state the extent to which charcoal production
leads deforestation. The study observed that, 28 (45.9%) of the respondents reported
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A CASE OF TANGA URBAN, TANZANIA
that charcoal production in large extent cause deforestation (Figure2). This implies that
the increase in demand of charcoal for urban dwellers associated with deforestation in
rural areas. Similarly, the study by Sedano et al (2016) in Mozambique revealed that, in
areas where charcoal produced in large extent the rate of deforestation is highly
contributed by charcoal production rather than agricultural expansion.
Figure 2: The extent to which charcoal making degrade environment
Source: Field data, 2017
5.2 Types of energy used in the study area
The study also was investigated the types of domestic energy often preferred in the
study area. The result indicated that many respondents 45 (73.8%) rely on charcoal, 10
(16.4%) gas, kerosene 3 (4.9%), firewood 2 (3.3%) while 1 (1.6%) of the respondent use
Electricity (Table 1). Equally, the study by Kambewa et al (2007) in Malawi shows that,
larger cities consume about 6.08 million standard bags of charcoal per year. CHAPOSA
(2002) reported that in Lusaka (Zambia), 65% of the households used charcoal as the
only energy source while the rest of the households used charcoal in combination with
firewood (23%), kerosene (17%) and electricity (1%). As for Dar es Salaam, 86% of the
households used charcoal as their first choice fuel for cooking. But, most of the
households (88%) combine two or more types of fuels (Ishengoma and Ngaga, 2000).
Contrary to this in developed countries (Western Europe and North America) there is
decrease in per capita household wood (charcoal /firewood) consumption due to
increase in use of fossils fuel (FAO, 2013).
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Table 1: Types of Energy used in the study area
Energy types
Frequency
Percentage
Charcoal
45
73.8
Fire wood
2
3.3
Kerosene
3
4.9
10
16.4
1
1.6
61
100
Gas
Electricity
Total
Source: Field data, 2017
5.3 The charcoal availability
The increase of charcoal consumption in urban areas tends to affect natural and
artificial forest in Tanzania and Tanga specific where the study was conducted. The
study investigated the current availability of charcoal. The respondents were asked
whether charcoal is more available or not. The study findings revealed that 53 (86.9%)
of the respondents reported that currently there are difficult in obtaining charcoal for
domestic use (Figure 3). Equally, during interview, the charcoal venders made a
statement that reflects the real situation of charcoal availability in the study area. They
had this to say:
It is difficult in obtaining charcoal for selling due to loss of trees that impacted to the
increase in distance from where charcoal produced
Figure 3: Charcoal Availability
Source: Field data, 2017
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5.4 Factors influencing charcoal scarcity
The respondents were asked to mention the factors for difficultness in obtaining
charcoal for domestic use. The following factors: deforestation, poor technology and
exportation of charcoal to neighbor countries were outlined (Table 2).
5.4.1 Deforestation
The study findings revealed that deforestation is a key driver to the fuel wood
(charcoal) crisis in the study area where as 57 (93.4%) of the respondents reported that
forest depletion affects charcoal availability. The study by Dewees (1989) and Heltberg
et al. (2000), revealed the same that, deforestation has created a situation of fuel wood
scarcity to the point that an impending fuel wood crisis as observed in many areas
where charcoal is the source of domestic energy.
5.4.2 Poor Charcoal Making Technology
The study observed that 2 (3.3%) of the respondents commented that lack of modern
tools and the use of traditional method of charcoal making results into shortage of
charcoal in the market. The study by Girard, (2002), observed the same that traditional
methods of charcoal production that are still persist today in many developing
countries, are often produce very low yields (typically 1 kg of charcoal from 8 to 12 kg
or more of wood), with low quality of charcoal product because it is difficult to
maintain uniform carbonization.
Table 2: Reasons for difficulties in obtaining charcoal
Reasons
Frequency
Deforestation
Percentage
57
93.4
Poor technology
2
3.3
Exportation of charcoal to neighbor countries
1
1.6
None
1
1.6
Total
61
100
Source: field data, 2017
5.5 Status of charcoal price in the study area
This study revealed that the price of charcoal is highly determined by climatic condition
and distance from which the charcoal is being produced. The study findings show 54%
of respondents admitted that currently the price of Charcoal is very high as compared
to the previous time, while 41% claimed that the price of charcoal is fairly moderate but
fluctuating seasonally (Figure, 4). The findings correspond to what has been raised
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during Interview with charcoal venders. The charcoal vender made the following
statement that reflects the price of charcoal in Tanga urban City:
…..the price of charcoal varies from 30,000 to 50,000/bag, but the price can change
seasonally, ie during rainy season the price become a bit higher when compared with dry
season
This trend was equally shown by Schaafsma et al (2012), that the price of charcoal
varies from TSH 4000 to TSH 45,000 per 60 kg bag across the study area (Dar es Salaam,
Arusha, Morogoro and Tanga) with a mean price of TSH 30,088 (USD 21) per bag in Dar
es Salaam and TSH 16,584 (USD 12) elsewhere. Likewise, observation of the charcoal
price in Maputo (Mozambique) and Kwazulu (South Africa) support the findings of this
study as 1 ton of charcoal sold around 400 USD in Maputo and 732 USD per ton in
(KwaZulu-Natal (GiZ, 2009). The study also found that there was price fluctuation in
the study area that occurs when charcoal production hampered by rainy season. The
study further noted that despite the increase in charcoal price in the study area many
household (73.8%) still rely on it as the price of other sources energy are extremely high
when compared to charcoal. This was equally observed by GiZ, (2009), that most of
household in the cities of Africa, prefer charcoal for their domestic use because the price
of charcoal is often lower when compared with other types of energy and can be
purchased in small quantities for very little money on a daily.
Figure 4: The current price of charcoal
Source: Field data, 2017
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5.6 Household Charcoal Consumption per Month
Charcoal is the main energy source for Tanzania’s urban population regardless the
household economic status, although electricity and gas are the principal energy
sources among wealthier households, these households still use considerable quantities
of charcoal (World Bank, 2009). The findings of this study show that 52.5% of
respondents consume 1 bag of charcoal per month while 34.4% claimed to consume less
than 1 bag per month. Probably this trend of charcoal consumption resulted from the
observed high and fluctuating price of charcoal coupled with the difficultness in
obtaining charcoal from production site. Contrary to this study World Bank (2009),
shows that there is an increase in consumption of charcoal in Dar es Salaam city from
1,500 tons per day. This figure estimated to rise to 3,300 tons per day by 2030.
Figure 6: Charcoal consumption per month
Source: Field data, 2017
5.7 The influence of deforestation in charcoal production
The respondents were further asked to state how deforestation affects charcoal
production. The study findings revealed that 56 (50%) of the respondents
acknowledged that deforestation contribute largely to the decrease in raw materials for
charcoal production, while 29 (25.9%) reported that deforestation leads to fluctuation of
charcoal price and 27 (24.1%) admitted that deforestation contribute to the decrease in
charcoal business (Table 3). This signifies that forest depletion is the main source of
insufficient household charcoal supply in the study area. Contrary, Fontodji et al (2011)
observed that, in Togo, charcoal production is greatly concentrated in the Plateaus,
Central, and Savanna. It is in those regions that there is still enough vegetation, mostly
in the Plateaus Region because of its forests.
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Table 3: The effect of deforestation in charcoal production
Variables
Responses
Frequency
Percentage
Decrease in raw materials for charcoal production
56
50
Fluctuation of charcoal price
29
25.9
Decrease in charcoal dealers
27
24.1
112
100
Total
Source: Field data, 2017
5.8 Other Deforestation environmental effects:
The findings of this study noted that deforestation is not only the main cause of fuel
wood crisis but also is responsible for other environmental effects including
drought/floods, global warming, loss of biodiversity and indirectly hunger and
starvation (Table 4). The study was equally supported by Gervert, (2007) who
acknowledged that deforestation is not only convert forestland to non-forest, but also
degradation that reduces forest quality, the density and structure of trees, the ecological
services supplied, the biomass of plants and animals, the species diversity and the
genetic diversity.
Table 4: Other effect of deforestation in environment
Responses
Frequency
Percentage
Drought/Floods
56
40.9
Global warming
31
22.6
Hunger and starvation
26
19
Loss of biodiversity
24
17.5
Total
137
100
Source: Field data, 2017
6. Conclusion and Recommendation
6.1 Conclusion
Deforestation becomes a key challenge in charcoal supply in urban households. The
scarcity of charcoal that caused by depletion of forest resources affect lower income
earners who depend largely in charcoal for domestic use including cooking, boiling
water for drinking and ironing clothes. The study found that majority of the
respondents reported that currently there is scarcity of charcoal for domestic use. The
main factor associated with charcoal scarcity includes depletion of forest that influence
an increase in distance through which charcoal produced, as
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difficult in obtaining charcoal and price. Thus, more work is still needed to be done in
this area.
6.2 Recommendations
There is a need of integrating forest and energy polices in order to achieve the
benefits that forest can offer and hence contribute in solving the problem of
charcoal crisis.
them to plant and care tree seedling for sustainable forest conservation.
The Government should provide subsidies to charcoal makers in order to enable
There is a need to raise awareness to the community on the importance of using
other biomass energy such as animal dung and crop residue wherever they are
available.
Improve the efficient of wood production and use. These efforts include not only
promotion of efficient wood stoves but also development of more modern
energy production systems such as the use of wood and sisal waste for electricity
production.
The energy policy should consider the use of modern stoves in terms of supply
and price so that local community can afford, this will reduce the amount of
charcoal required for cooking.
affordable price.
The Government should speed process of gas production and supply with
The Government should put in place series of interventions aiming at improving
economic status of rural and urban poor, so as to enable charcoal dealers to
resort in other income generating activities.
Improve agricultural production through re-introduction of agricultural
subsidies and ensure market for the obtained product. This will reduce the
number of charcoal dealers (Charcoal produces and traders) who normal resort
to charcoal business when agricultural production failed.
6.3 Areas for further studies
The study recommends the following area to be researched: Integrated strategies for
sustainable forest conservation and charcoal production
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INCREASE IN DEFORESTATION: A KEY CHALLENGE TO HOUSEHOLD CHARCOAL SUPPLY –
A CASE OF TANGA URBAN, TANZANIA
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