This chapter shows how forest accounts have been implemented and used for policy analysis. Country experience at the national level is discussed in relation to how it addresses each of the main policy applications of forest accounts identified in Chapter 1:
A. Establish the true socio-economic value of forests in relation to the rest of the economy
What is the total economic contribution of forests and what are the benefits from sustainable forest management?
What is the distribution of forest benefits among different groups in society?
Is economic growth sustainable or is it based on the depletion of forests?
B. Evaluate the impact of non-forestry policies
What are the trade-offs among competing users and how can forest utilization be optimized?
What are the impacts of non-forestry policies on forest use?
National forest accounts assess the total economic value of forests and link forestry values to the use of other resources and to the broader economy, integrating forestry policy with national development and monitoring interactions and feedback across different industries. Thus, forest accounts can be useful for two sets of resource managers and stakeholders: forestry managers and stakeholders responsible for sustainable management of the forest sector, and managers and stakeholders concerned with the macroeconomy.
Forestry managers may already have information about the total economic value of forest resources, including the inputs provided to sectors not part of the traditional forestry sector. What they gain from forest accounts is the ability to put that information within the context of the national economy. This helps them to identify and address threats to forest resources that originate outside the forestry sector, which can improve their ability to protect this resource.
Policy-makers and other stakeholders outside the forestry sector benefit from forest accounts in several ways: more accurate GDP that reflects all the contributions of forests, better indicators of sustainable economic development that include forestry and forestland resources, a tool for comparing policies across different natural resources including the extent to which the ‘user pays’ principle is applied, but perhaps most importantly, a method to integrate forestry into macroeconomic policy and planning tools. By identifying the extent of other sectors’ dependence on forests, it is possible to build strategic alliances with stakeholders in other sectors, such as agriculture, tourism, electric power and water.
Sustainable economic development requires anticipating the interaction and feedback from one part of the economy to another, weighing alternative development strategies in a manner that anticipates the full (direct + indirect) costs and benefits incurred throughout the economy. In the past, sectoral policies may have been designed with relatively little emphasis on economy‑wide impacts. Agricultural policy, for example, may have been formulated with little concern for impact on forestry, even though it may have had a major indirect impact through changes in land use. Forest accounts provide a tool for coordinating policies across the economy, anticipating cross-sectoral policy impacts and designing more effective national development policies.
This chapter begins by listing the countries with formal forest accounting programmes and the components of forest accounts and related environmental accounts that they have constructed. Examples of the policy applications of forest accounts are drawn from a range of countries—beginning with Sweden, South Africa and Romania—to illustrate how forest accounts are implemented and applied under widely varying circumstances. Additional examples will be provided by accounts for other countries, such as Swaziland and Spain, as well as forest valuation case studies.
Table 2.1 shows countries that have constructed forest accounts and the type of forest goods and services included in the accounts. This table is limited to those countries with formal accounting programmes sponsored by government agencies or by non-governmental agencies in cooperation with governments. Forestry accounts are more common in developed than in developing countries. Eurostat has had an ongoing programme to develop forest resource accounts since 1995 and many of the participating countries have developed extensive accounts. There are also many additional academic studies and one-off studies by governments or international agencies that are not shown here; some of these will be discussed later in the section on policy analysis. For an exhaustive review of all forest accounting efforts through 1997, see Vincent and Hartwick, 1997.
Forest accounts for all countries include timber asset accounts in physical and monetary terms. Forests are disaggregated in different ways depending on the policy issues and characteristics of forests in each country. Virtually all forest accounts distinguish cultivated and natural forests, and disaggregate forests by major tree species. Many developing countries limit timber accounts to commercial timber production, but are beginning to add non-commercial timber production and use of non-wood products as data become available. Among the developing countries, only Swaziland has constructed supply and use tables (SUT). SUTs are only constructed for timber and wood products at this time.
The non-timber benefit most commonly included in forest resource
accounts is carbon storage. Virtually all developed countries include carbon
accounts. This practice is less widespread in developing countries but is
likely to increase with growing potential for markets in forest carbon mitigation.
There is limited treatment of environmental services such as water and soil
protection at the national level. This omission is due partly to the great
uncertainty about these services (discussed further in Part II) compounded
by the highly site-specific nature of the quantity of services provided and
their economic value. For these reasons, forest environmental services are
more commonly found in regional accounts or accounts for individual forests.
This issue will be discussed in more detail in Chapter 3.
Forest management, especially in developing countries, has often been based on a limited range of economic, mostly commercial, values. Decisions about forestland use, for example, often compare the value of land under commercial timber production and the value of land under commercial agriculture, omitting other forest benefits, especially the use of forest products by local communities. Better understanding of the full range of goods and services supplied by forests is essential for optimal utilization of forests, and may provide an economic rationale for sustainable forestry. This section uses data from Sweden, South Africa and Romania to show the importance of accounting for total forest values, and the share of forest values that are either wrongly attributed to other sectors or not counted at all in national economic accounts. Sweden and South Africa have constructed forest accounts.
|
FOREST ACCOUNTS |
FOREST-RELATED ACCOUNTS |
||||||
|
Timber |
Non-timber goods and services |
Land |
Energy |
Water |
Pollution and env. degradation |
||
|
Asset accounts |
Supply and use table |
Carbon storage |
Other goods and services |
||||
Developing countries
|
|
|||||||
Brazil |
X |
|
|
|
|
|
|
|
Chile |
X |
|
|
|
|
|
|
|
Costa Rica |
X |
|
|
|
|
|
|
|
Indonesia |
X |
|
X |
|
|
|
|
|
Mexico |
X |
|
|
|
X |
X |
|
X |
Philippines |
X |
|
X |
X |
X |
X |
|
X |
Thailand |
X |
|
|
|
|
|
|
|
South Africa |
X |
|
X |
X |
|
|
X |
|
Swaziland |
X |
X |
X |
X |
|
|
|
|
Developed countries |
|
|
|
|
|
|
||
Under Eurostat pilot programme: |
||||||||
Austria |
X |
X |
X |
X |
X |
X |
|
X |
Finland |
X |
X |
X |
X |
X |
X |
|
X |
Denmark |
X |
X |
X |
X |
X |
X |
X |
X |
France |
X |
X |
X |
X |
X |
X |
X |
X |
Norway |
X |
X |
X |
X |
X |
X |
|
X |
Sweden |
X |
X |
X |
X |
X |
X |
X |
X |
Spain |
X |
X |
X |
X |
X |
X |
|
X |
Germany |
X |
X |
X |
X |
X |
X |
X |
X |
Italy |
X |
X |
X |
X |
X |
X |
|
X |
Other developed countries |
||||||||
Canada |
X |
X |
X |
X |
X |
X |
X |
X |
Australia |
X |
X |
X |
X |
X |
X |
X |
X |
New Zealand |
X |
X |
X |
X |
X |
X |
|
X |
Note: Countries included here have ongoing accounting programmes by government agencies or by non‑governmental agencies in cooperation with governments. There have been many additional academic studies and one-time studies by governments or international agencies. See Vincent and Hartwick (1997) for a review of these studies.
Sweden’s forest accounts are part of a well established and comprehensive government programme of environmental accounting that includes all components of forest accounts, as well as many other resources including water, pollution, energy and detailed land and ecosystem accounts (Eurostat 2002a, 2002b; Norman et al., 2001). The asset accounts are disaggregated by the categories recommended in the Eurostat project, but flow accounts for forest goods and services are not disaggregated by type of forest. Swedish forest accounts are generally quite comprehensive, but do not attempt to include forest environmental services other than carbon storage
South Africa’s forest accounts are part of an environmental accounting initiative by Statistics South Africa with support from the University of Pretoria and other agencies (Hassan, 2002, 2003). In addition to forests, accounts have been constructed for water and minerals. South African forests are classified by three major types: cultivated forest plantations that provide most of the country’s commercial timber and tree products, natural forests and woodlands that are used by rural communities, and fynbos woodlands, which is a unique biome in South Africa, the Cape Floral Kingdom.
Complete stock and flow accounts have been constructed only for cultivated forests, including impact on hydrological flow services. Flow accounts for timber and non-timber goods have been constructed for natural forests and fynbos woodlands; this information is especially useful because many of these values are not included in the national accounts of South Africa. Indeed, a primary motivation for forest accounts was to provide a better estimate of the total economic value of forestry in the national economy. Forest environmental services are represented mainly by carbon storage.
There are two major gaps in the South African forest accounts: stock accounts for natural forests have not been constructed, and forest accounts for national parks and protected areas have not yet been included in the accounts. Most of the forest-based international and domestic tourism is based on the system of national parks. The omission of forests in national parks and protected areas results in a significant underestimation of the recreation and tourism value of South Africa’s forests.
Romania’s forest valuation study was undertaken by a research consortium as a review of forest management in cooperation with the World Bank (Fortech Dames and Moore, 1999). From 1948 until 1991, most of Romania’s forests were owned and managed by the state and forests were managed sustainably. In 1991 a policy of restitution to private owners was instituted but since that time 31 percent of privatized land was clearcut or seriously degraded. The government is considering returning more of state-owned forests to private owners. There is support for return of forests to private owners, but in a manner that encourages sustainable management. Accounting for the full economic value of forests is an important element in these policy discussions.
Forest values for Romania include timber stock and flows of non-timber forest products. There is also an estimate of the combined value of social and environmental services provided by forests. As described below, this value is more than an order of magnitude greater than all other forest values combined, but the methodologies and data used for this figure are not discussed in the report so it is not possible to evaluate it.
The structure of each country’s forest accounts is described in Table 2.2, which shows the classification of forests and the detailed NTFP and environmental services included in each country’s accounts. All countries provide physical and monetary accounts for timber, forestland, non-timber forest goods and carbon storage. Specific non-timber forest products vary by country. The countries differ in the forest services that are represented: recreational benefits are most often included, but for South Africa much of the tourism value is missing because of the omission of national parks from forest accounts. South Africa also includes services to agriculture, livestock grazing and pollination of commercial agriculture in the western part of the country.
In the Swedish and South African accounts, there is relatively little representation of protective environmental services provided by forests, other than carbon storage. South Africa includes an estimate of the (negative) impact of cultivated forest plantations on water flow. Sweden records the land area that provides protection from noise. The Romanian report covers a wide range of forest environmental services, but provides no explanation of how these were calculated.
The estimated forest values for Sweden, South Africa and Romania (Tables 2.3, 2.4, and 2.5) indicate that non-timber values can be greater than the value of commercial timber harvest. Both Sweden and Romania report values at the national level, not providing information about values by type of forest. South African forest accounts disaggregate values for three categories of forest: cultivated, natural and fynbos woodlands. A short time series of forest values is available for Sweden (1993-1999) and Romania (1994-1997) and only one year’s values are available for South Africa, so it is not possible to assess what may be happening to forest values over time.
Table 2.2: Structure of forest accounts for South Africa, Sweden and Romania1
|
South Africa |
Sweden |
Romania |
1. Asset accounts for standing timber and forestland |
|||
Standing timber (m3 and value) |
Timber cultivated forests classified by major species and age class.
Standing timber in natural forests is not estimated. |
Classified by type of forest (cultivated, natural, other), availability for wood supply, protection status, major species and age class. |
Classified by major species, site class and age class. |
Forestland |
Classified by three types of forest: cultivated, natural and fynbos woodlands
Land area (ha) only. |
Classified by type of forest (cultivated, natural, other). Availability for wood supply, protection status.
Land area and value. |
|
2. Flow accounts for forest products |
|||
Commercial timber and tree products (m3 and value)
|
Timber from cultivated forests by major species, rattan. |
Timber by species. |
Timber by species, wickerwork. |
Non-market timber (m3 and value)
|
Timber for construction, fuelwood, crafts, etc. |
Timber for fuelwood. |
NAV |
NTFP (volume and value) |
Wild plants, game, medicines, honey, tea, flowers.
|
Wild plants, game. |
Wild plants, game, honey, fish. |
Forest services |
Livestock grazing (livestock days, value).
Pollination services of wild bees (number of farms, value).
Recreation and tourism (value).
Carbon storage (tons C, value).
Impact on water flow from cultivated forests (volume, value). |
Recreation (number of visitors, value).
Carbon storage (tons C, value).
Biodiversity protection (land area, species count).
Noise protection services (land area and value). |
Single value for combined carbon storage, soil and water protection, and social value of forest. |
3. Expenditures for forest management and protection |
|||
|
NAV |
Costs of forest management and protection. |
Costs of forest management. |
4. Macroeconomic indicators |
|||
|
GDP adjusted for omitted non-market forest products.
Forest appreciation-depreciation/depletion. |
NDP, forest appreciation-depreciation/depletion. |
NAV |
1 Information for Romania is from a forest valuation study not forest accounts, but much of the information is compatible with forest accounts.
NAV: Not available
Sources: South Africa (Hassan, 2002, 2003); Sweden (Eurostat 2002a, 2002b; Norman et al., 2001); Romania (Fortech Dames and Moore, 1999)
There are similarities and differences among the forest values of these three countries, reflecting in part different forest uses and the different coverage of forest accounts. Notably absent from South Africa’s and Romania’s forest values are comprehensive figures for recreational services.
Recreational use of Swedish forests is the single most important forest value, greater than the value of timber harvest. The value of carbon storage is roughly half the value of timber[1]. Non‑timber goods are less than 5 percent of the total value of forests, and the forest protective services for soils and noise abatement are negligible. Of course, there are some forest services that could not be valued (see Table 2.2), but these accounts provide a reasonable estimate of the magnitude of non‑timber forest values.
Table 2.3: Value of forest goods and services in Sweden, 1993 to 1999 (millions of euros)
|
1993 |
1995 |
1999 |
|
Timber harvest |
2080 |
2540 |
2370 |
|
Non-timber goods |
273 |
233 |
225 |
|
Forest services |
|
|
|
|
|
Recreation* |
2370 |
2370 |
2370 |
|
Protection from noise |
20 |
20 |
20 |
|
Carbon storage |
1050 |
630 |
810 |
|
Subtotal |
3440 |
3020 |
3200 |
Total output of forests |
5793 |
5793 |
5795 |
*Recreational value was estimated for one year based on number of tourist-day visits to forest areas; the number of tourist-day visits is considered to have remained fairly stable over time.
Source: Norman et al. (2001).
In South Africa, commercial timber harvest accounts for less than a third of forest value. The largest single forest value is non-market goods from natural forests, which are used mainly by traditional rural communities. Combined with livestock grazing, the goods and services in natural forests account for over half of total forest value. In contrast to Sweden, recreational use of forests is very small and limited to fynbos woodlands; tourism in cultivated forests and natural woodlands is negligible. Natural forests provide also cultural and aesthetic values to traditional communities, but there has been no estimate of this value.
The recreational value of forests in national parks and protected
areas, which are major domestic and international tourism sites, have not
yet been included in forest accounts. Environmental damage, in the form of
a water abstraction externality by cultivated forests of alien species, accounts
for about 12 percent of the value of commercial timber harvest. In South Africa,
this externality is being treated quite seriously. The new South African water
policy has proposed charging forest plantations for this water abstraction
externality.
Table 2.4: Value of forest goods and services in South Africa, 1998 (millions of rands)
|
Cultivated forests |
Natural forests |
Fynbos woodlands |
Total |
|
Commercial timber harvest |
1856 |
NA |
NA |
1856 |
|
Non-market timber and non-timber goods |
NA |
2613 |
79 |
2692 |
|
Forest services |
|
|
|
|
|
|
Recreation |
NA |
NA |
29 |
29 |
|
Livestock grazing |
NA |
1021 |
NA |
1021 |
|
Pollination services |
NA |
NA |
786 |
786 |
|
Reduction of rainfall runoff |
-225 |
NA |
NA |
-225 |
|
Carbon storage |
120 |
360 |
NAV |
480 |
|
Subtotal |
-105 |
1381 |
815 |
2091 |
Total value of forests |
1751 |
3994 |
894 |
6639 |
NA: not applicable
NAV: not available
Source: (Hassan, 2002)
(millions of US$ in constant 1997 prices)
|
1994 |
1995 |
1996 |
1997 |
Timber production Wickerwork Forest fruits and mushrooms Hunting Fish and apiculture |
89.2 7.7 9.0 21.2 1.3 |
110.9 7.6 11.4 21.8 1.6 |
120.7 7.3 8.9 19.2 1.5 |
104.2 5.4 7.6 15.3 1.6 |
Tourism and recreation Total |
not valued 130.3 |
173.3 |
159.7 |
136.1 |
Forest environmental services (carbon storage, soil and water protection, etc.) |
Average annual value: 3,096.0 |
Source: Adapted from Fortech Dames and Moore, 1999.
The Romanian forest valuation study reports timber and non-timber products, recreational services and forest environmental services. Figures are not reported for different categories of forest. The underlying physical data and valuation methodologies are reported only for timber and non-timber products. Insufficient data were available for valuing recreational services. A single value is reported for environmental services that combine carbon storage, soil and water protection and social values, but no information about the value of each service and how this figure was obtained. The estimated value of environmental services is more than an order of magnitude greater than the total for timber and non-timber products. Without further documentation it is difficult to assess this value; in any case, it is likely that forest environmental services are substantial. An example of forest accounts that addresses the value of environmental protection services for water and soil will be discussed in Chapter 3.
With respect to the main objective of this policy application, providing a better understanding of the total economic value of forests than conventional national accounts provide, the benefit of accounts may be summarized in Table 2.6. In all countries, the values directly attributed to forests in national accounts greatly underestimate the true value of forests. The share attributed to forestry ranges from a high of 45 percent in Sweden to a low of 4 percent in Romania. A large part of forest services benefits other sectors and is attributed to these sectors, mainly recreation and agriculture, which account for 41 percent of forest output in Sweden and 24 percent in South Africa. Given the omission of many forest environmental services from forest accounts, these values should be considered a lower bound. It is not possible to determine the share of Romanian forest values wrongly attributed to other sectors and the share not counted at all.
Table 2.6: Forest values included in national accounts of Sweden, South Africa and Romania
|
Sweden, 1999 |
South Africa, 1998 |
Romania, 1997 |
|||
|
(million euros) |
% of total |
(million rands) |
% of total |
(million US$) |
% of total |
Included in national accounts as forest values |
2595 (timber, non-timber goods) |
45% |
1856 (commercial timber) |
28% |
136 |
4% |
Included but attributed to other sectors |
2370 (recreational services) |
41% |
1611 (grazing, recreation, pollination, reduced rainfall runoff) |
24% |
Part of 3,096 (forest environment services) |
Part of 96% |
Not included in national accounts |
830 (noise protection + carbon storage) |
14% |
3172 (non-market timber, non-timber forest goods, carbon storage) |
48% |
Part of 3096 (forest environment services) |
Part of 96% |
Total |
5795 |
100% |
6639 |
100% |
3235 |
100% |
The question of who benefits from forests is increasingly important for development policy. This issue has two dimensions, inter-generational and intra-generational. Inter‑generational equity concerns the forest wealth left to future generations - whether society is liquidating its natural capital to pay for current consumption or using it sustainably. This is discussed in section 2.4.
Intra-generational equity concerns the distribution of benefits among different social groups in the present generation. Forest accounts have not been used to address systematically the issues of equity and poverty, but this use of the accounts is likely to become important in future work (e.g. Lange and Hassan, 2002). Identifying the different social groups that benefit from forest goods and services is an essential first step in forestland use planning, infrastructure development and assessing trade-offs among competing forest uses.
There are several ways in which the distribution of forest benefits may be evaluated, each of which is useful for policy purposes. Some of the characteristics to consider include:
In identifying forest beneficiaries, it may be useful to combine two or more of these dimensions and to further disaggregate households by income class or other relevant characteristics. This section will address the first two approaches to evaluating the distribution of forest benefits, scale of forest use and distance from forest. Distribution by geographic distribution within a country will be discussed in Chapter 5, where the construction of accounts for regions or individual forests is addressed.
[1] Several methods were used to value carbon storage (see Chapter 7). The value reported here is one of the lower values and is the one preferred by the authors.