A WWF International Discussion Paper
Prunus Africana
Alternatives to the Unsustainable Exploitation of Wild Stocks in Africa and Madagascar
Anthony B. Cunningham
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Alan Hamilton
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Prunus Africana bark
Alternatives to the Unsustainable Exploitation of Wild Stocks
Introduction
This paper takes the Prunus africana bark trade as an example to
describe the path towards workable solutions in medicinal plants
conservation. Although this case study only deals with Prunus africana,
several issues raised are relevant to the exploitation of other
medicinal species which are in trade. These issues are:
1. the complexity of the medicinal plants trade from harvesters to final product;
2. the reluctance of industry to invest in "green production" despite the benefits of doing so;
3. underestimation of sustainable yields from wild populations;
4. inappropriate local tenure systems;
5. low prices to local harvesters which act as disincentives for growing
medicinal plants or trees to relieve harvesting pressure on wild
stocks.
Although these factors complicate monitoring and resource management,
the path towards workable solutions is more one of politics and people
management than one based uniquely on natural resource management. As
demand grows, cultivation of slower growing species such as Prunus
africana can be a viable proposition. However, industry is often
reluctant to commit resources to cultivation on a significant scale when
wild stocks are still available. Resource mining is preferred to
resource management despite the availability of information on volumes
and products traded, on the economics of tree production, on genotypic
variation within species, for developing on farm cultivation.
Three changes are considered important for shifting from unsustainable
wild harvest of Prunus africana to agroforestry or plantation scale
production. These are:
1. the application of "non-detriment" finding by CITES authorities with
regard to export and import permits; ( in fact a ban on export and
import of wild stocks);
2. wider awareness amongst the European and North American public and
the herbal products industry of the need for, and benefits of certified
or sustainable sourcing; and
3. the will to invest in the future and implement cultivation on a commercial scale.
Trade in Prunus Africana
Prunus africana is a tree species restricted to montane forests of
Africa and Madagascar. To local people, Prunus africana is a multiple
use species, used primarily for its bark (traditional medicines) and
hard timber (building poles, fuelwood, axe handles). Internationally,
Prunus africana bark extracts are used medicinally to treat prostate
gland hypertrophy and benign prostatic hyperplasia (BPH).
Trade in Prunus africana products takes place in several forms. Between 3
200 and 4 900 tons of bark are exploited annually for export, either as
dried bark or bark extract. All of this is taken from wild populations
from mountains forests in Cameroon (supplying 70% of world trade) and
Madagascar (18% of world trade) and to a lesser extent from Zaire,
Equatorial Guinea (the island Bioko) and Kenya. Bark extracts are also
exported and used to produce herbal preparations in brand-name capsules.
Twenty different European companies produce and sell herbal preparations
containing Prunus africana extract. Several sell Prunus africana
products under licensing agreement with Groupe Fournier (France) or
Indena Spa. /Inverni della Beffa (Italy). In the USA, marketing of
Prunus africana extract mixed with other ingredients (such as the fruit
extract Saw Palmetto, Serenoa repens and pumpkin seeds, Cucurbita pepo),
takes place by mail order and through the Internet. The retail cost of
Prunus africana herbal preparations is high and the over-the-counter
retail value of the trade is an estimated US$220 million/yr.
In the 1970's and early 1980's, most bark was dried in source countries
of Africa and Madagascar before export for processing in Europe. Since
then, there has been a major shift in the two major exporting countries
(Cameroon and Madagascar) away from export of unprocessed dried bark to
export of locally produced bark extract. These two countries export some
14.6 tons of extract annually to France and Italy. Bark extract yields
are 5kg of extract per ton of air-dry bark (or two tons of fresh bark).
By contrast, yields of bark extract from black wattle (Acacia mearnsii),
which is commercially cultivated for tannin, are 330kg per ton of wet
bark. The low yields of Prunus africana bark extract are compensated for
by its high value. In late 1996, its price was FrF4934 per kg
(US$966/kg) compared to FrF1643 per kg (US$321) for Serenoa repens
extract.
Environmental effects
Trade in Prunus africana bark is a significant source of foreign
exchange for Cameroon and Madagascar. However, it has had a devastating
effect on the wild populations of this unique resource. Distribution is
limited to Afromontane forest "islands" which are generally above 1500 -
2000m altitude. The size of these "islands" has been greatly reduced by
agricultural clearing, the major threat to Afromontane forests. It is
these remaining Afromontane forests that are the current focus of Prunus
africana bark exploitation.
Although sustainable bark harvest is theoretically possible, tree or
tree-crown die-off is common while felling to strip bark is frequent in
Madagascar. Bark exploitation to meet the highest volumes of export
demand even takes place inside "protected" forests and national parks.
In Cameroon, commercial harvesting of bark has affected the habitat of
three most important forests for bird conservation. (Mount Oku, Mount
Cameroon and Mount Kupe). Cultivation in plantations or agroforestry
systems within Africa is therefore the way forward to meet demand.
However, international awareness of the destructive effects of this
trade on wild populations should be further raised in order to promote a
shift from wild populations harvesting to cultivated sources. This
should take place before there is more extensive marketing of herbal
extracts from Prunus africana in North America, which is considered to
be the major potential market for Prunus africana herbal products in the
future.
Environmental sourcing
The international trade in wild collected plant material to supply a
thriving trade in dietary supplements and herbal products has grown
rapidly over the past two decades. To increase market shares, companies
are keen to produce quality products that are safe and effective.
However, companies based in North America and Europe need to take the
lead in developing a system of "environmental accounting" so that
quality of herbal products and dietary supplements also encompass
sustainable harvest and production. At present, there is not sufficient
pressure on companies for developing methods of environmental sourcing.
It is well recognised that far too many large companies (the main
importer) leave issues such as origin of raw material and cultivation
methods to local exporters and harvesters, and are therefore unaware of
the destructive effects of their products on certain wild plant
populations and habitats. Continuation of this practice will ultimately
lead to the loss of the supply source for industry as habitat is damaged
or selectively depleted of species. Local people will also lose out as
their local self-sufficiency is eroded through overexploitation of
popular plant species which they use as effective medicine.
One way of achieving "environmental sourcing" is to give particular
attention to slower growing, habitat specific medicinal plant species
used in international trade. A growing number of these have been listed
by CITES due to conservation concerns about overexploitation. Examples
include American ginseng (Panax quinquefolius), Goldenseal (Hydrastis
canadensis), African cherry (Prunus africana), jatamansi (Nardostchys
jatamansi) and kukti (Picrorhiza kurrooa)
Legislation and Resource Management
All source countries (Uganda, Kenya, Madagascar, Zaire and Cameroon) are
signatories to CITES. It is a requirement of CITES legislation that a
Management Authority is established which would be responsible for
national CITES control, administration and licences. This is not always
the case.
Prunus africana harvesting in Cameroon and Madagascar is allowed under
permit systems issued by the national Departments of Forestry. The
systems of exploitation that have been implemented are very different.
In Madagascar, trees are routinely felled and stripped of their bark.
Bark harvesters are supposed to leave 2 trees/ha undamaged as a source
of seedlings in the future. These are supposed to be chosen by staff of
the Forest Department. No felling is allowed within 10 m of a
watercourse. Permits are issued for a duration of two years, and no
limit is placed on the quantity of bark each person may collect.
In Cameroon, sustainable bark harvesting was attempted between 1972 and
1987, when the company "Plantecam Medicam" had a monopoly on bark
exploitation. This was carried out by trained teams of harvesters who
removed opposing quarters of the trunk bark up to the first branch
rather than girdling the trees. The intention was to return after 4-5
years to remove the undamaged trunk bark and after another 4-5 years,
the regrowth. Although crown die-back occurred in some trees and bark
regrowth was poor on trees located in open, dry sites, this practice had
the advantage to reduce tree die-off due to bark damage. A real effort
was made by Plantecam to ensure that all the bark harvesters employed
were shown the collecting procedure of removing bark "quarters" from
opposing sides of the tree trunk. Workers caught removing all bark from
the trees also faced dismissal.
Despite the commendable efforts of Plantecam at sustainable bark
harvesting, there are many cases where this has not been achieved,
particularly in north-west Cameroon. This is because the loss of
monopoly control of Prunus Africana exploitation by Plantecam resulted
in an opportunistic scramble for wild stocks by licensed entrepreneurs.
In addition, the felling and/or complete stripping of Prunus africana
trees by some bark harvesters has significantly reduced wild stocks.
Concern about the effects of this over-harvesting resulted in
recommendations leading to the partial ban on bark extraction in 1991.
Cunningham and Mbenkum (1993) have shown that the ban may have had the
opposite effect, as during 1991, over 3898 metric tons of bark, over
twice the annual average, were processed.
Concerning exploitation fees, all Special Permit holders in Cameroon,
including Plantecam, pay a "Regeneration Tax" (2% of the value of the
raw material) and a "Transformation Tax" to the Forestry Department.
These are supposed to cover forest regeneration costs. These taxes have
not been particularly effective in meeting their goals, and enrichment
planting and regeneration schemes are limited. A similar regeneration
tax system has been proposed for Madagascar.
What Needs to be Done
Meeting demand from cultivated sources
To provide an alternative supply source and improve self-sufficiency of
traditional medical practitioners, Prunus africana plants would need to
be produced cheaply and in large quantity. In addition, bark prices and
bark extract from "on farm" cultivation would have to be high enough to
provide the necessary incentives for sustainable harvesting. In all
cases where cultivation has taken place, (in Europe, Asia or Africa),
plants have been grown for profit or for a high level of resource
returns (eg: multiple use species for fruits, and medicinal properties).
Relatively low Prunus africana bark prices, coupled with farmer's
uncertainty concerning guaranteed entry to foreign markets, are
disincentives which hamper cultivation. If small farmers are to become
involved in Prunus africana cultivation, there needs to be a guaranteed
market for the bark they produce at a price that makes production
profitable.
From an horticultural point of view, meeting commercial and domestic
demands of the bark can be achieved relatively easily. The total volume
of medicinal plant material is relatively small compared to food or
timber products; therefore commercial demands can be met from relatively
a small cultivated area. For example, the total Australian domestic
demand of 200 - 300 tonnes of Aloe vera gel is met by 10-15 ha of Aloe
barbadensis plantation. It is also estimated that 70 ha would be
required to meet the regional demand of 300, 000 bulbs /yr of Scilla
natalensis (Liliaceae), which is used in traditional medicine in
KwaZulu/Natal, South Africa.
In good growing conditions, bark production rates of Prunus africana are
similar to Acacia mearnsii plantations, which produce 28 tons/bark/yr
from 12 yr old stands with a mean density of 1 363 trees/ha. Before
manufacture of the capsules, the bark extract of Prunus africana is
standardised to contain 13% phytosterols. Twelve year old trees have
about 50% of the phytosterol content, so twice the current tonnage would
presumably be required. This suggests that the total annual world
demand of 3200 - 4900 tonnes of Prunus africana bark could be produced
from a total plantation area of 2743 - 4200 ha or a 12 year rotation of a
total of 230 - 350 ha of trees felled and totally stripped of bark each
year. Based on studies of Prunus africana bark production rates and
prices, this can be an economic proposition
Cultivation by small farmers
As a relatively fast growing indigenous tree, Prunus africana also has
great potential for reafforestation and agroforestry systems in
deforested areas around forest remnants in Cameroon, Madagascar, Kenya,
Uganda and Zaire. Several recent reports have drawn attention to
conservation problems in these countries and suggested cultivation as a
possible solution in order to take harvesting pressure off wild stocks.
In Kenya, it is estimated that that there are 153 ha of Prunus africana
plantations, nearly half of which are over 40 years old.
The commercial importance of Prunus africana in north-west Cameroon has
been an important stimulus for rural farmers to start growing this tree
from seed, and some farmers in this area started planting as early as
1977. Most cultivation has however taken place since 1990 with support
from local and international non-governmental organisations.
An investigation, conducted by the author, on bark production and growth
rates in Cameroon, found a statistically significant correlation
between bark thickness, diameter at breast height (dbh) and tree height.
This suggests that Prunus africana showed rapid growth. Trees with the
fastest growth rates reached 14m high and 37cm dbh in 18yr. The study
also compared the economics of cultivating Prunus africana and
Eucalyptus camaldulensis (a popular introduced species in montane
Africa), and showed that while Eucalyptus camaldulensis cultivation is
30% more profitable than Prunus africana production, there are reasons
(such as the negative effects of Eucalyptus on crop yields) why farmers
might rather invest in Prunus africana than in Eucalyptus trees. The
3500 farmers already planting Prunus africana in northwest Cameroon are
evidence of this. To encourage further cultivation, steps need to be
taken within exporting countries and internationally for the legal
recognition of legitimate growers. If it is economically viable, small
holder farmers should therefore play a greater role in Prunus africana
cultivation, including agroforestry systems.
Large scale cultivation
Cultivation by small farmers is nowhere near the scale of planting
required to reduce harvesting pressure on overexploited wild stocks.
Herbal products companies with a high stake in Prunus africana should
take direct responsibility for large scale cultivation. As argued in
this paper, large scale cultivation to meet demand can be economically
viable. Five options are suggested for cultivation on a large scale:
1. cultivation done directly by the company, as Schwabe does with Gingko
biloba in France. Similarly, the German company Boehringer Ingelheim in
Australia produces about 40% of its requirements of Duboisia for
production of scopalamine;
2. research and cultivation through production contracts with selected
farmers who then market their product to the company involved. An
African example is the cultivation of Xysmalobium undulatum
(Asclepiaceae), for a German and an Australian company.
3. cultivation (and possibly on-farm research) by farmers who do not
have access to a guaranteed market. This can be a high risk strategy
(rather than a shared risk as in (2) above). A good example of this is
the initial boom and bust experienced by Aloe vera (Aloe barbadensis)
production in Australia during the mid-1980's when the market collapsed
for many growers when prices plunged.
4. research and cultivation by the State. Research that is publicly
funded by the State can play an important role. A good example is the
development of improved genetic material of Duboisia for plantation
production of scopalamine in Australia. Large state owned plantations of
timber trees provide a good example, although this option is unlikely
for slower growing species. National governments, particularly in
developing countries, are also reluctant to embark on such ventures.
5. A combination of several of the above. If some of the different
approaches are to be implemented, contracts between providers and buyer
companies would have to be developed to get around the secretive
approach which herbal product companies often take. Without this,
production and marketing become fragmented and there is little
co-operation between producers and industry.
Lessons learned
Traded internationally and harvested from the wild, Prunus africana is
hardly a "minor forest product". Between 3200 - 4900 tonnes of bark are
exploited annually for export to Europe. This represents the largest
volume of any African medicinal plant in international trade. Neither
the uncontrolled harvesting of wild Prunus africana populations, nor
tree cultivation as one alternative to wild harvest are easy problems to
resolve.
Five lessons which have wide policy implications for plants in trade are
put forward. Taking them into consideration could lead to a better
balance between medicinal bark harvesting, forest conservation and local
economic development.
* Although sustainable harvest from wild populations was planned, this has unfortunately not occurred for a number of reasons.
Local people have lost local self-sufficiency in an important
traditional medicine; the Cameroon and Madagascar Forest Departments are
concerned about the loss of foreign earnings; and international
conservation organisations are worried about the effects on forest
structure and biodiversity. Government regulations in Cameroon for a
partial ban on harvest; for encouraging tree cultivation by the export
company; or in Madagascar, the retention of two trees/hectare for seed
production, have not been effective. Ironically, the loss of monopoly
harvest-control by Plantecam in Cameroon and the partial ban on export,
in fact led to a higher level of destructive harvest and volume of bark
harvested than ever before.
* A certain degree of control on the production and marketing of Prunus
africana appears to be necessary to stop disorderly exploitation.
Monopoly control on bark harvest in Cameroon had benefits for
sustainable resource extraction, limiting tree felling or death from
total debarking until 1978, when bark harvesting licences were granted
to 50 Cameroonian entrepreneurs. Monopoly control on bark exports also
had disadvantages for bark prices paid to harvesters, and consequently,
reduced the incentive to cultivate trees. In 1994, illegal bark
exploitation, fuelled by the higher price offered by an Italian company
to three Cameroonian entrepreneurs resulted in extensive damage to
Prunus africana trees on Mt Cameroon.
* Overexploitation of wild Prunus africana populations has serious implication for conservation and cultivation.
The location of isolated Prunus africana populations on montane
"islands" dotted over virtually the entire length of sub-Saharan Africa
and a few isolated mountains in Madagascar has probably been a key
factor in genotypic and chemical differences between populations.
Chemical analysis has shown, for example, that it is possible to
distinguish between the bark extracts from different localities in
Africa and Madagascar. These differences offer wider scope for selection
of plant characteristics for the purposes of domestication and genetic
improvement. It is also a point of concern that already isolated
populations on montane islands are becoming further isolated due to the
destruction of almost all large, reproductively mature trees from
intervening "islands". The worst affected are also the most unusual -
the Madagascan Prunus africana populations.
* There is a need to change national forestry policy which prevents farmers selling Prunus africana bark.
The rationale behind this regulation was to reduce uncontrolled
exploitation of what was considered a national natural resource.
However, it is a further disincentive for on-farm cultivation under
rising scarcity of large Prunus africana trees.
* It is encouraging to see that despite the lack of support from
government, coupled with the disincentives of low bark prices and weak
property rights, at least 3 500 small-scale farmers are already planting
Prunus africana in agroforestry systems in north-west Cameroon.
As a relatively fast growing indigenous tree, Prunus africana has great
potential for reafforestation and agroforestry systems in deforested
areas around forest remnants.
References
Cunningham, A B and F T Mbenkum. 1993. Sustainability of harvesting
Prunus africana bark in Cameroon : a medicinal plant in international
trade. People and Plants Working Paper 2. Paris, UNESCO.
Cunningham, A B; E Ayuk, S Franzel, B Duguma and C Asanga. in press. An
economic evaluation of medicinal tree cultivation : Prunus africana in
Cameroon. Working Paper no. 6, WWF/UNESCO/Kew People and Plants
Initiative.
Cunningham, M, A B Cunningham and U Schippmann. 1997. Trade in Prunus
africana and the implementation of CITES. Bundesamt fur Naturshutz,
Germany.
Davis, S D, V H Heywood and A C Hamilton. 1994. Centres of plant
diversity : a guide and strategy for their conservation. IUCN
Publications Unit, Cambridge, UK.
Ewusi, B N, T Tanyi Charles, J Nyambi and J Acworth. 1996. Bark
extraction : current situation and sustainable cropping of Prunus
africana on Mount Cameroon. Unpublished paper, Mount Cameroon Project,
Limbe, Cameroon.
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