Mapping
Access to Benefits in Cameroon using Commodity Chain Analysis:
A Case Study of the Azobé Timber Chain
Wynet Smith, Department of Geography, University of Cambridge,
UK. Email: wvs20@cam.ac.uk
Introduction
In Southwest Cameroon, a farmer bemoans the damage to his farm
resulting from the activities of a company logging in his village’s
community forest. The company cut through peoples’ farms
in their attempt to open a road into the steep forests of the
Bakossi Mountains. Meanwhile, the chiefs of nearby villages, who
contest the community forest and claim such activities are illegal,
discuss how to disrupt the logging operations and ensure that
their forest is not destroyed. The trees being logged –
including a highly valued, very resistant hardwood named Lophira
alata or azobé – are being loaded on trucks and taken
to Douala. This wood, as well as azobé coming from other
logging sites, is mostly bound for Europe, where it ends up being
used in projects such as a boardwalk in Nieuwport, Belgium. At
the European end of the commodity chain, the use of tropical wood
from sites such as the one in Southwest Cameroon generates considerable
controversy. In July 2004, for example, a coalition of environmental
non-governmental organizations (NGOs) criticized the construction
of the Belgium boardwalk, claiming that such projects are helping
to destroy tropical forests through illegal and unsustainable
logging. The NGOs are demanding, amongst other things, that local,
provincial and national authorities in Europe institute more coherent
and rigorous buying policies for tropical wood (Forum illegale
houtkap, 2004).
As
the above anecdote illustrates, the commodity or supply chain
linking the farmer and the surrounding forest with the environmentalists
and the boardwalk in Belgium is a highly complex and contested
system, with the material flow of timber but a small aspect of
the overall chain. One tool for mapping this complex system is
commodity chain analysis, which can help identify the institutions,
mechanisms and actors that govern access to the resource and mediate
the distribution of profits. It can also assist in deconstructing
the interactions between political discourse and the functioning
of the market. In this article, I illustrate the potential of
commodity chain analysis by presenting a summary of the timber
commodity chain in Southwest Cameroon and the links between Cameroonian
activities and international political discourse in Europe
.
The
article begins with an introduction to commodity chain analysis
and the selection of Cameroon as a case study. Discussion then
moves on to highlight the means by which the Cameroonian Government
controls access to the forest resource and the specific case of
the azobé timber chain in the country’s Southwest
Province. The next section discusses the issue of illegality in
the chain, whilst the penultimate section brings together the
local and global levels of the chain and how political discourse
in Europe acts both as a backdrop to and as a factor that influences
the market itself. The article concludes by arguing how commodity
chain analysis is a useful tool for interrogating these types
of local-global linkages and how environmental policy discourse
can affect outcomes in producer countries such as Cameroon as
well as in Europe.
The
Power of Commodity Chain Analysis
A growing body of literature within geography and other disciplines
explores the concept of commodity chains and networks. Variations
can be found in terminology, theoretical bases, and thematic areas.
In their review article, Leslie and Reimer (1999) define three
general categories of commodity chain literature: global commodity
chain analysis, systems of provision literature and commodity
circuits. Other studies use either the term filière or
value chains. For the purposes of this article, I use the definition
of commodity chains as a “series of interlinked exchanges
through which a commodity and its constituents pass from extraction
or harvesting through production to end use” (Ribot 1998:307-308).
The embedded nature of power relations in the chain (Kaplinsky
and Morris 2001: 8) and “who controls global trade and industry”
are key questions in commodity chain studies (Gibbon 2001:346).
Governance arrangements are important and can be either centralized
or decentralized, buyer-driven or producer-driven (Gereffi 1994).
Tracing networks provides a means of examining “the ongoing
division and integration of labor processes and … the constant
development and transformation of the world-economy’s production
system” (Hopkins and Wallerstein 1994:17).
The
creation of these chains is complex. The networks linking households,
states and companies are “situationally specific, socially
constructed, and locally integrated, underscoring the social embeddedness
of economic organization” (Gereffi, Korzeniewicz and Korzeniewicz
1994:2). Le Billon (1999) notes that chains are embedded in much
wider networks of social actors and practices than the production
of the commodity itself. In turn, the commodity shapes these networks
and social institutions. From this perspective, “markets
are not only regulated by economic rationality, government policies
and legal mechanisms but are both constrained and enabled by a
vast array of social relations and institutions such as, for example,
kinship or religious institutions” (Barber 1995, cited in
Le Billon 1999). The concept of social embeddedness emphasizes
the role and construction of power in the commodification process.
Hartwick (1998:425) argues that it is important not just to concentrate
on identifying actors and distribution of benefits but that commodity
chain analysis also needs to address “the most politically
sensitive sites along commodity chains.”
Two commodity chain studies on forest resource use are of particular
interest to this article. In the first study, Ribot (1998) explores
how the control and maintenance of commercial forest access occurs
at different levels of the charcoal commodity chain in Senegal.
He uses commodity chain analysis as a tool to examine how, and
for whom, markets operate and for understanding the patterns of
benefit distribution. Ribot reveals a complex series of structures,
mechanisms, and relations used by the various actors in Senegal
to maintain their access to profits (Ribot 1998:308). In the second
study, Le Billon (1999; 2000) examines timber commodity chains
in Cambodia, focusing not only on the actors in the chain, but
also on the meanings constructed through forestry discourse in
the country and as influenced by external agents. He deconstructs
the ideal model of forest management that is implicit in the recommendations
of donor agencies, and how this actually results in more exclusionary
forms of forest management. The ideal model of forest management
did not make sense in Cambodia, where the shift from ‘anarchy’
to ‘order’ failed to benefit either local people or
local forests (Le Billon 2000).
Cameroon
as a Case Study
Situated at the junction of West and Central Africa, Cameroon
is an exceptional country for exploring the material and discursive
construction of timber commodity chains. It has rich forest resources
and a complex colonial history that has resulted in lingering
political, economic and social challenges. Humid moist forest
covers approximately 23.9 million hectares, or almost 50 percent
of Cameroon’s territory (FAO 2001), much of it located in
the five southern-most provinces (see Figure 1). Cameroon’s
forests form part of what is today referred to as the Congo Basin
forests, which span seven countries and cover almost 200 million
hectares - the second largest contiguous block of tropical rainforest
in the world (Laporte et al. 1998). The area is the subject of
considerable international attention, with an announcement at
the Johannesburg Summit of the Congo Basin Forest Partnership
and US$53 million dollars of funding for numerous conservation
initiatives (U.S. State Department 2002).
Figure
1: Cameroon’s forest distribution

The
volume of total industrial roundwood production in Cameroon has
been increasing significantly over the last 40 years and a large
proportion of the country’s forests are now managed for
commercial timber purposes (Global Forest Watch Cameroon 2000).
Cameroon is one of the top six tropical timber exporters in the
world: it exported over 2.8 million cubic meters of industrial
roundwood equivalent in 1997 (ITTO 2001). This increase in exports,
combined with a decline in oil revenues, means the timber industry
now provides a significant proportion of Cameroon’s foreign
export earnings. In 1996-1998, the forest sector contributed approximately
230 million USD per year, or almost 20 percent, of the total value
of exports (Eba'a Atyi 1998)
Access
to the Forest Resource in Cameroon
As noted by Goldman (1998:2), whoever “controls property
rights controls the processes of resource extraction and environmental
change.” In terms of commercial forest resources in Southwest
Cameroon, a number of factors, including the institutional context,
are important determinants of access. The main legal means for
governing access to forest resources, however, is the revised
Forestry Law of 1994
.
Existing literature considers this legislation the most progressive
in Central Africa as there are provisions for community benefits
and processes for transparency in the administration of rights
(Ekoko 2000; Silva et al. 2002)
.
The law carves up Cameroon’s forests into two main categories,
permanent and non-permanent forest. The permanent forest estate
consists of both State and Council forests and covers thirty percent
of the national territory
.
State forests include both areas for wildlife protection and forest
reserves
.
Council forests are areas given as private property to a municipal
or rural council
.
The non-permanent forest is further divided into communal, community,
and private forests. The community forests are intended to provide
communities with the right to own and manage up to 5,000 hectares
.
Table
1: Commercial timber exploitation rights outlined in
Cameroon’s 1994 Forestry Law and Decree No. 95/531/PM (dated
August 23, 1995).
|
Forest
Exploitation Right
|
Notes
|
Amount
(area or volume)
|
Period
|
|
Forest
Management Unit (FMU)
|
An
agreement to provide a long-term supply of wood.
|
Up
to 200,000 hectares per company
|
15
years, renewable. 3 years initially.
|
|
Sale
of standing volume (SSV)
|
Permanent
domain forest for Cameroon nationals only
|
Specified
volume
|
1
year, non-renewable
|
|
Non-permanent
domain forest
|
2,500
hectare, specified volume
|
3
years, non-renewable
|
|
Exploitation
permits
|
Small-scale commercial
|
500
m3
|
1
year, non-renewable
|
|
Timber
Recover Special Authorization (TRSA)
|
For
salvage of abandoned timber on the coast and roads
|
Not
specified in law
|
Less
than one year
|
|
Timber
Recovery Permit (TRP)
|
Felling
trees for road-building and other infrastructure
|
1,000
hectares
|
Not
specified
|
The law also sets out the categories and means of forest exploitation
rights (see Table 1). The major categories of commercial exploitation
are forest management units (FMU) and sales of standing volume
(SSV). FMU are large-scale logging areas that are restricted to
State production forests while SSV can be located either in permanent
forest areas of state production or council forests, or in non-permanent
forests
.
FMU are initially for 15 years and are renewable. The conditions
for SSV depend on the forest category but are basically short-term
exploitation licenses for relatively small areas (2,500 hectares).
An exploitation permit that provides up to 500 cubic meters of
wood was also included in the law but has been suspended since
1999
.
Companies can also obtain timber through short-term special authorizations
for timber removal (TRSA), for infrastructure purposes such as
road building, and timber salvage or recover permits (TRP). These
are not intended, however, to provide a steady supply of wood
.
Additionally, companies can work with community forests or with
councils that have a council forest
.
Access
to any of the commercial rights requires that a company or individual
be registered as an approved timber exploiter with the government
.
The registered timber exploiters are then entitled to participate
in the bidding processes for FMU and SSV, with a final decision
made by an inter-ministerial commission and monitored by an independent
observer. Access to any of these exploitation rights requires,
by law, financial resources and technical capacity or training.
Although not required by law, political connections are also often
needed to obtain logging rights
.
A wide-range of links thus exists between local communities and
companies, between elites and companies, and between small-scale
Cameroonian and multinational companies. The next section examines
the implications of these factors in the case of the azobé
timber chain in Southwest Province.
The
Azobé Chain in the Southwest Province
Cameroon’s Southwest Province is densely populated and agriculture
plays a significant role in the local economy. The region is fairly
mountainous and the forests are located within the Guinean forests,
which are known for their high levels of biodiversity and species
endemism (Diangha 2001; Oates and Bergle 2001)
.
The region includes a number of important conservation areas,
including Banyang-Mbo Wildlife Sanctuary and the proposed Bakossi
National Park.
Commercial
timber exploitation has been occurring in the Southwest Province
since at least the 1940s, with logging increasing in the late
1950s (Government of the Southern Cameroons 1960; cf. Sharpe 2005)
.
There is currently one active FMU and another that is not yet
attributed. These concessions border on the boundaries of Korup
National Park in one case, and the Banyang-Mbo Wildlife Sanctuary
in the other (see Figure 3). Additionally, there have been a number
of SSV over the past ten years. The most recent public auction
for SSV was in September 2003 and included three in Southwest
Province
.
There is also the Ndecuda community forest in Ndisse-Ekep, where
logging has been taking place on and off since 2002.
An
analysis of the various logging rights handed out in recent years
indicates a very specialized and vertically integrated timber
commodity chain (see Table 2)
.
Timber from the various logging rights appears to flow predominantly
to three international companies: Wijma; Transformation Reef Cameroon
(TRC); and Compagnie Industrielle & Commerciale des Bois Exotiques
(CIBEC), all of which are Dutch or have strong Dutch connections.
In those cases where these companies are not directly involved
in owning the logging rights or carrying out the timber harvesting,
they have been the partners or purchasers of the wood cut by Cameroonian
companies who are the legal rights-holders. Most of the wood goes
to the first two companies with the third being a smaller player.
Table
2: Preliminary list of recent and current logging rights
in Southwest Province.
|
Year
|
Logging
Right
|
Department
|
Division
|
Winner
|
Partner/
Purchaser
|
| 2002 |
FMU
11-002
|
Manyu
|
Upper
Banyang
|
Wijma
|
|
| 2003 |
SSV
11-06-16
|
Ndian
and Meme
|
Mbongue
& Ekondo Titi
|
TRC
|
|
| 2003 |
SSV
11-06-17
|
Kupe-Manenguba
|
Nguti
|
TRC
|
|
| 2003 |
SSV
11-06-18
|
Kupe-Manenguba
|
Nguti
|
CAFECO*
|
Wijma
|
| 2001 |
SSV
11-06-13
|
Meme
|
Konye
|
PMF-Wood
|
TRC
|
| 2001 |
SSV
11-03-14
|
Kupe-Manenguba
|
Tombel
|
PMF-Wood
|
TRC
|
| 2001 |
SSV
11-03-15
|
Kupe-Manenguba
|
Tombel
|
|
|
| 2000 |
SSV
11-06-12
|
Meme
|
Kumba
|
SEPFCO
|
TRC
|
| 1999 |
SSV
11-05-04
|
Kupe-Manenguba
|
Nguti
|
Zangem
Albert
|
TRC
|
| 1997 |
SSV
11-05-01
|
Kupe-Manenguba
|
|
SSCTM
|
No
information
|
| 1997 |
SSV
11-03-05
|
|
|
Enoumedi
|
No
information
|
| 2001 |
TRSA
2252
|
Kupe-Manenguba
|
Nguti
|
Zangem
Albert
|
TRC
|
| 2002 |
Community
Forest
|
Kupe-Manenguba
|
Tombel
|
Ndecuda
Community Development Association
|
Complexe
Helena Bois and CIBEC
|
Source:
Compiled from Government notices, legal documents, Global Witness
reports, Greenpeace reports, interviews and direct observation.
Further analysis of the commodity chain shows that despite the
rich array of species in the forests of Southwest Cameroon, azobé
accounts for a significant proportion of the trees logged in this
region. Azobé is used for heavy marine construction, including
locks, as well as for railway cross-ties and heavy-duty flooring
(Chudnoff 1984). The wood’s resistant properties mean that
it does not need to be treated with preservatives. Because of
its hardness, azobé tends to be processed by a specialized
group of companies. Of Cameroon’s azobé exports,
the bulk is sent to Europe with the Netherlands receiving the
vast majority. In 2003, some 80 percent of imported azobé
ended up there, with Belgium and France each receiving just over
five percent while the UK and the USA imported approximately three
percent and three and a half percent respectively (SEPBC 2004).
.
In
terms of the big three Dutch companies, Wijma, or GWZ, is a logging
and trading company that specializes in highly durable timber
for marine engineering projects. They have been active in Africa
and Cameroon for over thirty years. They acquired FMU 11-002 in
the Southwest in 2002. They constructed a new sawmill in Nguti,
which opened in January 2004
.
They work with various species of tree in Nguti, although azobé
accounts for 80 to 90 percent of total production. They export
80 to 90 percent of their entire azobé production to Europe,
although they were also producing ties for the Cameroonian railway
in June 2004. At that time, they were processing wood coming from
the FMU and were soon to begin doing the same to timber from SSV
11-06-18, awarded to Cafeco, a Cameroonian company
.
The
second company, TRC, is a subdivision of Reef, a Dutch company
that specializes in wood for marine construction. Reef has an
outstanding environmental reputation in Europe and 30% of the
wood sold by Reef in 2001 was Forest Stewardship Council (FSC)
certified (Greenpeace, Monitor and CED 2003). TRC did not possess
a FMU until 2004 and have usually obtained their timber from SSV
attributed to Cameroonian companies (Global Witness 2002c; 2003b;
Greenpeace, Monitor and CED, 2003). In December 2003, they obtained
two SSV in Southwest Province, SSV 11-06-16 and SSV 11-06-17
.
TRC owns a sawmill in Douala, as well as a sawmill in Kumba, which
they purchased in 2002
.
CIBEC,
the third company, was controlled by Dutch businessman Jacco Ravenhorst,
and began activities in Cameroon in 1998 (Greenpeace and CED 2003).
They had a sawmill in the Bonabéri section of Douala and
focused on species such as azobé and doussié (Carret
1999). Most of their wood came from TRC although they also began
to source wood from the Ndecuda community forest in the Bakossi
Mountains in Southwest Province in 2002. They conducted this exploitation
in partnership with Complex Helena Bois, a Cameroonian company
based in Douala. This timber source was disrupted for various
reasons including a provincial court injunction (Wild et al. 2004)
and the company apparently later filed for bankruptcy (Anonymous
source 2004).
Illegality
in the Timber Chain
Implementation of the law and its various regulations is problematic
on a number of levels in Cameroon and at different points within
the commodity chain. There have been on-going problems concerning
illegal logging and a number of cases of irregular attribution
and irregular relocation of exploitation rights. This section
describes the means by which government officials, elites and
companies manipulate the system in order to access or control
the resource, focusing on the attribution of SSV and community
forests as an example.
As
noted earlier, both SSV and community forests can be placed in
the non-permanent forest domain. In December 2002, MINEF issued
an order that fixed the procedures for a “preemption right”
that would enable communities to refuse a SSV and instead pursue
community forestry activities in the same area of forest
.
Thus, prior to issuing tenders for SSV, the Government has a responsibility
to inform communities. In practice, however, this right does not
appear to have been applied on a transparent or consistent basis.
For example, all six chiefs interviewed in the villages around
SSV 11-06-17 stated that the first they knew of the SSV was when
TRC arrived in their village with a government order showing they
had the right to log. Members of two villages erected a barricade
to protest against the logging because: As one chief explained:
They
just surprised us when they came. As a result of that, there
was a blockade set up at the road leading into the forest because,
traditionally, the custodians are supposed to be aware of (problems)
before ever the forest is tampered with.
Another
chief complained that although he had been told that logging would
only begin after a regional meeting, TRC started to log before
this meeting ever took place. Additionally, neither the Nguti
Mayor nor the chiefs appeared to be aware that SSV 11-06-18 would
soon be in operation
.
A number of other SSV in the Southwest have involved illegal activities
or social conflicts, as evident in Table 3 (Global Witness 2002c;
2003a; 2003b; Greenpeace, Monitor and CED 2003). A major concern
revolves around the relocation of SSV areas after the bidding
and allocation process is complete but before the issuance of
documents, which requires the active participation of public officials
(Global Witness 2003b; 2004). This practice effectively removes
the community’s preemption right as well as depriving other
companies of the opportunity to bid on that particular patch of
forest. Additionally, there have been numerous cases of companies
actually logging outside of their approved area, resulting in
significant losses of royalties to the state (Global Witness 2002a;
2002b; 2003b; Greenpeace, Monitor and CED 2003).
Table
3: Examples of documented problems in some exploitation
rights in Southwest Province.
|
Right
|
Company
|
Notes
|
|
SSV
11-06-16
|
TRC
|
SSV
granted to TRC is different in the final authorization compared
to the area opened for public bidding in the September 2003
Public Notice. Allegations of wrongdoing have been made in
the press. |
|
SSV
11-06-17
|
TRC
|
This
SSV was not included in the original Planning document that
is used to notify communities about their right of refusal. |
|
SSV11-06-18
|
CAFECO
|
The
area of the map does not match legal description. |
|
SSV
11-06-12
|
SEPFCO
|
Inaccurate
position of SSV on the ground. Evidence of logging 7.5 km
outside of SSV boundaries. Illegal road network. |
|
SSV
11-06-13
|
PMF
Wood
|
The
boundaries of this SSV were moved 20 km away from legal location
advertised the June 2000 public bid. Illegal logging outside
of boundaries. Conflict with local community. |
|
SSV
11-05-14 and TRSA 2252
|
Zangem
Albert
|
Issuance
and dates of use appear irregular. Logging outside of dates
and outside of approved boundaries. |
|
FMU
11-002
|
Wijma
|
Irregular
use of log books (DF-10). |
|
Ndecuda
Community Forest
|
Complexe
Helena Bois-CIBEC
|
On-going
conflict with local communities. Authorization to exploit
the forest by industrial means. |
Sources:
Various Global Witness and Greenpeace reports and newspaper articles.
There
are also allegations of manipulation of the community forest regime
in Cameroon. In many cases, local elites and economic operators
have used community forests to gain access rights to the forest
and the associated economic benefits. This situation appears to
hold true in terms of the Ndecuda community forest, where logging
was initiated by two local elites who live elsewhere. The villages
of Ndisse and Ekep obtained the rights to the forest in 2002,
despite protests from nearby villages. The surrounding villages
took the case to court, alleging that the community forestry process
was not followed and a consultation meeting had never taken place.
The independent monitor, Global Witness, investigated some issues
in 2002 and found the forest had never been demarcated on the
ground (Global Witness 2002c). The other villages lost the case,
however, in 2003 after considerable social conflict and violent
incidents involving the army and local government officials. One
village chief stated that this was possible in Cameroon because:
Here,
it is the survival of the fittest … those who have the
money can fight and win a legal battle. I am not afraid to say
it. Even if it was the Governor who was there or the President
himself. Let me die. Cameroon is Cameroon.
Some
residents of Ndisse now express concern and dismay about the situation
and how their community had been misled. One young man stated:
A
road from Ndisse to Ekep. Electricity. Employment for the youths.
See? She [Helena Complexe] promised these things but nothing
has been done since the creation of the community forest. She
puts more attention on the production of timber.
While
promises are made to the village members to obtain their consent,
these often amount to nothing. Reasons for manipulating access
are at least in part due to a desire to garner the benefits from
this high value commodity. The distribution of benefits along
the chain is far from equitable, despite widespread rhetoric of
poverty alleviation and the like (see Table 4 for a simple expression
of the numbers). Value at the local level (forest level) remains
low. In the Ndecuda community forest, for example, Ndisse and
Ekep’s contract with Complex Helena Bois pays them 1,000
FCFA
per cubic meter of wood of any species, including azobé.
In SSV 11-07-17, the villagers received 1,000 FCFA/m
for wood directly from TRC
.
Royalties are paid separately to the government, with forty percent
intended for the municipal council and ten percent for the affected
communities
.
The export value set by the government for tax purposes is currently
84,000 FCFA for azobé. Initial data gathered from companies
in Europe indicate that this wood (in end product form) can be
sold for between 450 and 1,100 Euros/m
,
or approximately 700,000 FCFA/m
.
The distribution of earnings / profits in Cameroon is related
to one’s ability to mediate access, something which increases
the further you move away from the forest and higher up in the
commodity chain. Elites from Ndisse, for example, now have their
own cars, while the resident villagers both here and in the isolated
settlement of Ekep, continue to live without electricity and the
road they so desperately wanted.
Table
4: Value of azobé along the commodity chain.
|
Location
|
Value
(FCFA/m3)
|
Equivalent
(Euro/ m3)
|
| Villages |
1,000
– 5,000
|
1.50
to 8.00
|
| Port
(Cameroon government FOB) |
85,000
|
125
|
| FOB
prices (log price) as of February 2005 |
|
145
|
| Europe
retail price |
700,000
|
1,100.00
|
Source:
Interviews, Government documents, ITTO Market Study Reports.
Contesting
Central African Forest Spaces: Influencing the Market through
Political Discourse
Issues of illegality, coercion and manipulation of the legal regime
become even more problematic in the global context and have significant
ramifications for the international trade in timber from the Southwest
and other parts of Cameroon. This is partly because tropical forests
are “highly contested spaces”, both on the ground
and in social theory (Doornbos, Saith and White 2000). On the
one hand, tropical timber is a high-value commodity that provides
significant revenues for many Third World countries
.
On the other hand, tropical humid forests
are a high priority on the international environmental agenda
(Adger et al. 2001; Humphreys 1996), with various actors expressing
concern about the on-going loss of these biodiversity hotspots
(Bowles and Prickett 2001). The demand for timber is identified
as an important cause of forest degradation globally (Dudley,
Jeanrenaud and Sullivan 1998), whilst its impacts on biodiversity
are poorly understood (Matthews et al. 2000). Logging is considered
the most significant threat to remaining frontier forest in many
global regions, including Africa (Bryant, Nielsen and Tangley
1997). As a result of these findings, highly politicized struggles
to control access to and use of the forest play out on the international
as well as national and local stages.
This
struggle is nowhere more apparent than in the battle over timber
from Cameroon and other Central African forest nations, which
is being fought both in Europe and on the ground in Cameroon.
At the European end of the commodity chain, actors have developed
various strategies to address the problem of declining forest
cover. Many groups, from NGOs to multilateral and bilateral agencies,
have championed market-based approaches, including certification
and labeling. The underlying assumptions are that since forest
use and logging is inevitable, there should be an attempt to ensure
that such use is managed sustainably. This approach, often based
within first-world contexts, recognizes the power of the consumer
and the market, and attempts to use that market to influence change.
As a result, part of the current discourse focuses on improving
the logging industry’s operating practices and reducing
the impact of demand.
The
concept of supply chains is an explicit part of international
forestry discourse. Many NGOs are currently expending considerable
effort on tracing the links between development activities in
remaining forest areas and the governments, retailers and other
consumers who buy the wood. As mentioned briefly in the introduction,
a coalition of European NGOs released a report that criticized
the construction of a boardwalk in Belgium because of its use
of Cameroon timber. This move by Greenpeace and others is part
of a larger campaign targeting tropical timber supply chains that
rely on illegally and unsustainably harvested wood. For example,
in 2002, Greenpeace took public action against the United Kingdom
government, storming Whitehall during renovations to replace windows
and doors that they claimed were made of illegally and unsustainably
harvested wood from Cameroon.
They
have also consistently targeted companies in an attempt to influence
the timber commodity markets. They have attacked a number of companies,
including Wijma, Reef and CIBEC, based on their records in Cameroon
(Greenpeace 2003; Greenpeace and CED 2003; Greenpeace, Monitor
and CED 2003). In one report, the caption for a picture of Wijma
sawn timber in a Dutch port reads:
Is
this timber legally produced? Once Wijma’s sawn timber arrives
on the European market, it is impossible for the customer to verify
its legality. Logs from legal and illegal sources are easily mixed
and could be processed together in Wijma’s sawmills in Cameroon
or in Europe (Greenpeace 2003).
They
have challenged timber traders, such as Hupkes in the Netherlands,
to audit their own suppliers and ensure they are not marketing
illegally harvested timber (Greenpeace and CED, 2003). They are
questioning the validity of the entire chain, not just the illegal
aspects. Their objective is to pressure companies into changing
their practices and governments to reform legislation and purchasing
policies.
Partly
in response to such pressure, European governments including those
of the United Kingdom, Denmark, the Netherlands, and the European
Union (EU) itself, are developing policies focused on reducing
the importation of illegally harvested and traded tropical timber.
For example, the EU has just developed an action plan focused
on reducing the importation of illegally harvested and traded
tropical timber (European Commission 2003) and the UK government
has a procurement policy on tropical hardwood (Meecher 2000).
The G8 is addressing the issue of illegal logging in 2005, although
their Environment and Development Ministers refrained from endorsing
any legislative language in their March 2005 statement.
These
new policies and developments are in turn beginning to affect
the functioning of related markets. Companies are now turning
to certification and other processes in an attempt to ensure they
do not lose their access to markets in Europe. Eight companies,
including Reef, sent an open letter to the G8 Ministers, calling
upon them to take action and develop legislation
.
This would have seemed impossible five years ago. In turn, these
developments in Europe are affecting operations on the ground,
with some companies at least attempting to implement timber-tracking
systems as part of their Cameroonian operations. Thus, change
does seem to be underway, although it is still too early to assess
the overall impacts and meaning of these changes.
Conclusion
Tropical timber is a high-value commodity that links villagers
and timber-producers in forest-rich countries with traders, retailers
and consumers in countries around the world and provides significant
revenues for many Third World countries. The political nature
of the timber trade and the broader forestry discourse raises
questions, however, about the nature of power relations in political
economic structures and knowledge construction surrounding timber
commodity chains. Commodity chain analysis is a tool that enables
the deconstruction of the networks, discourses and power dynamics
present in these chains. Following the network of actors, processes
and institutions, as well as the distribution of access to benefits
and profits highlights the socially embedded nature of the timber
chain and how there are complex linkages between the different
processes taking place at global, regional and local levels. It
also reveals that northern environmental pressures can bring about
conditions that affect the functioning of the market. The discourses
on the conservation and development of tropical rain forests are
targeting timber commodity chains linking places such as Cameroon’s
Southwest Province with international markets in Belgium and the
United Kingdom. In response, market players and consumers are
beginning to react and even, in some cases, becoming proactive
in terms of developing their own strategies and visions for change.
Progress is slow, however, and only time will tell whether these
different initiatives will have an impact on levels of illegally
logged timber.
Acknowledgements
I would like to thank the Canadian Social Sciences and Humanities
Research Council and the Cambridge Political Economy Society Trust
for their doctoral scholarships. Fieldwork funding was obtained
from the World Resources Institute (WRI), an International Tropical
Timber Organization fellowship, Cambridge University’s Smuts
Memorial and UAC Nigeria Funds, and the Department of Geography’s
Philip Lake II Fund. I would like to extend a special thank you
to Jesse Ribot of WRI for his on-going support and for providing
fieldwork funding. I would like to thank the staff at the Center
for International Forestry Research (CIFOR) and the various people
whom assisted me along the way through interviews and discussions.
I would also like to thank Bill Adams, my Ph.D. supervisor, for
his advice and support and the organizers of the IASCP 2004 conference
and the Christensen Fund for the travel award to attend the conference.
References
Adger,
W.N., T.A. Benjaminsen, K. Brown and H. Svarstad. 2001. Advancing
a political ecology of global environmental discourses. Development
and Change 32:681-715.
Bowles, I.A. and G.T. Prickett (eds.). 2001. Footprints in the
Jungle: Natural Resource Industries, Infrastructure and Biodiversity
Conservation. Oxford University Press, Oxford, UK.
Bryant, D., D. Nielsen and L. Tangley. 1997. The Last Frontier
Forests: Ecosystems and Economies on the Edge. World Resources
Institute, Washington, D.C.
CARPE. 2005. The Forests of the Congo Basin: A Preliminary Assessment.
Central African Regional Program for the Environment, Washington,
D.C.
Carret, J.-C. 1999. Monographies par Usine. Ministere camerounaise
de l'Environnement et des Forets, Yaounde, Cameroon.
Chudnoff, M. 1984. Tropical Timbers of the World. United States
Department of Agriculture Forest Service, Washington, D.C.
Diangha, M.N. 2001. Botanical Inventory of the Banyang-Mbo Wildlife
Sanctuary, Southwest Province, Cameroon. The Wildlife Conservation
Society, Yaounde, Cameroon.
Doornbos, M., A. Saith and B. White. 2000. "Forest lives
and struggles: An introduction" in Doornbos, M., A. Saith
and B. White (eds.), Forests: Nature, People, Power. Blackwell
Publishers, Oxford, UK. 1-10 pp.
Dudley, N., J.P. Jeanrenaud and F. Sullivan. 1998. The timber
trade and global forest loss. Ambio 27:248-250.
Eba'a Atyi, R. 1998. Cameroon's Logging Industry: Structure, Economic
Importance and Effects of Devaluation. Center for International
Forestry Research and Tropenbos. No. 14., Bogor, Indonesia.
Ekoko, F. 2000. "Balancing politics, economics and conservation:
the case of the Cameroon forestry law reform" in Doornbos,
M., A. Saith and B. White (eds.), Forests: Nature, People, Power.
Blackwell Publishers, Oxford, UK. 129-152 pp.
European Commission. 2003. Forest Law Enforcement, Governance
and Trade (FLEGT): Proposal for an EU action plan. European Commission,
Brussels.
FAO. 2001. State of the World's Forests 2001. Food and Agricultural
Organization, Rome, Italy.
Forum illegale houtkap. 2004. Balada a Nieuwport, pillage au Cameroun.
Forum illegale houtkap.
Gereffi, G. 1994. "The organization of buyer-driven global
commodity chains: How US retailers shape overseas production networks"
in Gereffi, G. and M. Korzeniewicz (eds.), Commodity Chains and
Global Capitalism. Routledge, London, UK. 95-122 pp.
Gereffi, G., M. Korzeniewicz and R. P. Korzeniewicz. 1994. "Introduction:
Global Commodity Chains" in Gereffi, G. and M. Korzeniewicz
(eds.), Commodity Chains and Global Capitalism. Routledge, London,
UK. 1-14 pp.
Gibbon, P. 2001. Agro-commodity chains: An introduction. IDS Bulletin
32:60. Institute of Development Studies (IDS), Brighton, UK.
Global Forest Watch Cameroon. 2000. An Overview of Logging in
Cameroon. World Resources Institute, Washington, D.C.
Global Forest Watch Cameroon. 2005. Interactive Forestry Atlas
of Cameroon (Version 1.0): An Overview. World Resources Institute,
Washington, D.C.
Global Witness. 2002a. Report No. 12. Global Witness, Yaounde,
Cameroon.
Global Witness. 2002b. Report No. 028En. Global Witness, Yaounde,
Cameroon.
Global Witness. 2002c. Report No. 029En. Global Witness, Yaounde,
Cameroon.
Global Witness. 2003a. Report of the Independent Observer No.
58En. Global Witness, Yaounde, Cameroon.
Global Witness. 2003b. Report of the Independent Observer No.
65En. Global Witness, Yaounde, Cameroon.
Global Witness. 2004. Report 89En. Global Witness, Yaounde, Cameroon.
Goldman, M. 1998. "Introduction: The political resurgence
of the commons" in Goldman, M. (ed.), Privatizing Nature:
Political Struggles for the Global Commons. Pluto
Press, London, UK. 1-19 pp.
Government of the Southern Cameroons. 1960. Introducing the Southern
Cameroons: A Symposium on the Southern Portion of the Mandated
Territory of the Cameroons under United Kingdom Administration.
UK Federal Information Service, Lagos, Nigeria.
Greenpeace. 2003. Chainsaw Criminal Wijma. Greenpeace, Amsterdam,
Netherlands.
Greenpeace and CED. 2003. Chainsaw Criminal CIBEC. Greenpeace,
Amsterdam, Netherlands.
Greenpeace, F. Monitor and CED. 2003. Chainsaw Criminal Reef.
Greenpeace, Amsterdam, Netherlands.
Hartwick, E. 1998. Geographies of consumption: a commodity-chain
approach. Environment and Planning D-Society & Space 16:423-437.
Hopkins, T. K. and I. Wallerstein. 1994. "Commodity chains
in the capitalist world-economy prior to 1800" in Gereffi,
G. and M. Korzeniewicz (eds.), Commodity Chains and Global Capitalism.
Routledge, London, United Kingdom. 17-20 pp.
Humphreys, D. 1996. Forest Politics: The Evolution of International
Cooperation. Earthscan Publications, London, UK.
International Tropical Timber Organization (ITTO). 2003. Annual
Review and Assessment of the World Timber Situation, 2002. International
Tropical Timber Organization (ITTO), Yokohama, Japan.
ITTO. 2001. Annual Review and Assessment of the World Timber Situation,
2000. International Tropical Timber Organization, Yokohama, Japan.
Kaplinsky, R. and M. Morris. 2001. A Manual for Value Chain Research.
Institute of Development Studies (IDS), Brighton, UK.
Karsenty, A. 1999. Vers la fin de l'etat forestier? Politique
Africaine 75:147-161.
Laporte, N.T., S.J. Goetz, C.O. Justice and M. Heinicke. 1998.
A new land cover map of central Africa derived from multi- resolution,
multi-temporal AVHRR data. International Journal of Remote Sensing
19:3537-3550.
Le Billon, P. 1999. Power is Consuming the Forest: The Political
Ecology of Conflict and Reconstruction in Cambodia. University
of Oxford Press, Oxford, United Kingdom.
Le Billon, P. 2000. The political ecology of transition in Cambodia
1989-1999: War, peace and forest exploitation. Development and
Change 31:785-805.
Leslie, D. and S. Reimer. 1999. Spatializing commodity chains.
Progress in Human Geography 23:401-420.
Matthews, E., R. Payne, M. Rohweder and S. Murray. 2000. Pilot
Assessment of Forest Ecosystems. World Resources Institute, Washington,
D.C.
Meecher, M.R.H. 2000. The UK Government Procurement Policy on
Tropical Hardwood: Statement to Parliament. United Kingdom Government,
London, United Kingdom.
Myers, N. 1994. "Tropical deforestation: rates and patterns"
in Pearce, D.W. and K. Brown (eds.), The Causes of Tropical Deforestation:
The Economic and Statistical Analysis of Factors Giving Rise to
the Loss of Tropical Forests. UCL Press, London, United Kingdom.
27-40 pp.
Oates, J.F. and R.A. Bergle. 2001. Biodiversity Patterns and Conservation
in the Gulf of Guinea Forests. Conservation International and
The Wildlife Conservation Society, Washington, D.C. and New York.
Olson, D.M. and E. Dinerstein. 2002. The Global 200: Priority
ecoregions for global conservation. Annals of the Missouri Botanical
Garden 89:199-224.
Olson, D.M., E. Dinerstein, R.A. Abell, T. Allnutt, C. Carpenter,
L.M. McClenachan, J. D'Amico, P. Hurley, K. Kassem, H. Strand, M. Taye and M. Thieme.
2000. The Global 200: A Representation Approach to Conserving
the Earth's Distinctive Ecoregions. World Wildlife Fund-US, Washington,
D.C.
Oyono, P.R. 2004. Green and Black Gold in Rural Cameroon: Local
Governance, Justice and Sustainability. World Resources Institute,
Washington, D.C.
Reid, W.V. and K. Miller. 1989. Keeping Options Alive: The Scientific
Basis for Conserving Biodiversity. World Resources Institute,
Washington, D.C.
Ribot, J.C. 1998. Theorizing access: Forest profits along Senegal's
charcoal commodity chain. Development and Change 29:307-341.
SEPBC. 2004. Log and Sawntimber Export Statistics from Cameroon.
La Lettre de l'ATIBT,
Sharpe, B. 2005. "Understanding institutional contexts to
define research questions" in Homewood, K. (ed.), Rural Resources
and Local Livelihoods in Africa. James Currey, Oxford, United
Kingdom. 157-176 pp.
Silva, E., D. Kaimowitz, A. Bojanic, F. Ekoko, T. Manurung and
I. Pavez. 2002. Making the law of the jungle: The reform of forest
legislation in Bolivia, Cameroon, Costa Rica, and Indonesia. Global
Environmental Politics 2:63-96.
U.S. Department of State. 2002. Press Release: Congo Basin Forest
Partnership.
Wild, C., C. Ekobo, B. Fosso and A. Ntok. 2004. The Protected
Area System. Yaounde, Cameroon.
NOTES
This
analysis draws upon a much broader study of the timber commodity
chains linking Cameroon and Europe, and how these are embedded
in environmental politics, that the author conducted in Cameroon
during 2003-2004 as part of his PhD research. He conducted extensive
informal and semi-formal interviews with key actors in the chain
from Cameroon to Europe, as well as direct observation of activities
at various points in the chain.
It
is debatable, of course, how much these export earnings translate
either into real contributions to development or direct benefits
for local communities.
Law No. 94-1 to lay down forestry wildlife and fisheries regulations.
The
development of the Law, however, was shrouded in considerable
controversy (Ekoko, 2000) and its’ implementation is variable
with regards to a number of aspects including community forests
and commercial forest concessions.
Law 94-1, Section
21 and 22.
Law 94-1, Section
24.
Law 94-1, Section
30.
Law 94-1, Section
37
According to some sources, it appears that SSV are now supposed
to be limited solely to non-permanent domain forests. There are
cases, however, where recent SSV are at least partially within
the permanent forest domain and even overlapping with proposed
national parks, such as the case of the proposed Ebo National
Park and SSV 07-02-32 in Littoral Province.
The
suspension of these permits was purportedly to cut down on abuse.
One side effect, however, is that most small scale operators are
now left no option but to log illegally.
TRP
have been suspended since 1999 by Decision No. 0944/0/MINEF/DF
of 30 July, 1999.
To
date, only one communal forest in Cameroon has been classified
and exploitation has only recently begun so companies have not
yet been able to readily access wood through this route (Oyono
2004).
Law
94-1, Section 41.
One
forestry company employee said to the author, in April 2004, that
“Cameroonians have the opportunity, but not the means. My
boss has the means. He is the son of the President.”
According
to the World Wide Fund for Nature’s Global 200 Ecoregions,
this area can be classed into two major ecoregions:
the Congolian Coastal Forests and the Cameroon Highland Forests
(Olson and Dinerstein 2002; Olson et al. 2000). They are subsumed
into the Congo Basin forest term in most contemporary usage (CARPE
2005).
Companies were operating in Tombel in the 1940s and in Southern
Bakossi in the 1950s through 1960s (Wild et al. 2004). In the
Nguti area, there has been logging since at least the 1960s (Diangha
2001).
This
sale included 20 SSV reserved for nationals and forty in a general
category. Anyone applying under the national category would not,
however, be able to apply for the any SSV in the general category.
The
list is based on a compilation of documentation the author accessed
while in Cameroon. There may be other rights that have been authorised
but which could not be accessed or which are not available in
the most recent listing of rights. A recent atlas released by
Global Forest Watch Cameroon (2005), and compiled directly from
Government-supplied data, is missing information on 179 out of
311allocated SSV.
They
also own a sawmill and FMU in South Province, where azobé
is also found.
Cafeco
are sub-contractors in the Wijma FMU; they carry out the actual
harvesting activity, though they use equipment leased from Wijma.
Cafeco will also harvest the timber in their SSV but then sell
the logs to Wijma.
Decision
No 00158/D/MINEF/CABA of December 30, 2003. They also obtained
two other SSV in Littoral and Centre Provinces.
The
sawmill has been in operation since 1973 and owned by a number
of companies, including STIK, affiliated with Wijma (Carret 1999).
Arrêté 518/MINEF/CAB du 21 Décembre 2002.
In
general in Cameroon, a significant proportion of the SSV allocated
appear to be larger than the 2,500 hectares allowed by law (Global
Forest Watch Cameroon 2005:10).
Pound Sterling is equivalent to approximately 950 Central African
Francs (FCFA). One Euro is worth about 670 FCFA.
The
1,000 FCFA/m3 appears to have been created as a mechanism to provide
benefits to the communities as an incentive to allow logging (Karsenty
1999).
There
are significant problems with the distribution and spending of
the forest royalties in Cameroon.
For example, producer countries of the International Tropical
Timber Organization (ITTO) exported nearly 8.3 billion USD in
2000 and 7.4 billion USD in 2001 of tropical timber products (ITTO
2003).
Tropical
moist forest are “evergreen or partly evergreen forests,
in areas receiving not less than 100 mm of precipitation in any
month for two out of three years, with mean annual temperature
of 24-plus degrees C and essentially frost-free”. (Myers
1980, cited in Myers 1994:27). These forests are rich in biodiversity:
closed tropical forests are estimated to hold between 50 and 90
percent of the world’s terrestrial biodiversity (Reid and
Miller 1989).
“Our
pledge on forestry products”, Thursday 17/03/05, The Guardian.
Available online at: http://www.guardian.co.uk/letters/story/0,,1439523,00.html.