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Figure 4.2.1<br />

Assessment of the components of total wealth<br />

Intangible<br />

capital<br />

Protected areas,<br />

alternative<br />

cost method<br />

Forest resources, NPV<br />

Land assets, NPV<br />

Agricultural land, NPV<br />

Wealth<br />

measured<br />

using<br />

the NPV<br />

method<br />

Natural<br />

capital<br />

Residual value of<br />

structures and<br />

equipment<br />

Value of urban<br />

land assessed<br />

indirectly<br />

Residual value of<br />

structures and<br />

equipment<br />

Produced<br />

capital<br />

Produced<br />

capital<br />

Step 1 Step 2 Step 3 Step 4 Step 5<br />

Structures and equipment Urban land Natural capital Total wealth Intangible capital<br />

Source: Where is the Wealth of Nations? Measuring Capital for the 21st Century, 22<br />

The value of sub-soil assets is assessed during the period<br />

of use, based upon the net present value of the net profit<br />

earned during the (future) period of use. 5<br />

In the case of forest resources, the value is the<br />

present value of the resource rent for timber. In order to<br />

do the calculations, data is required about timber production,<br />

the unit price of products made from timber, and<br />

the period of use of the forest. The product value is relatively<br />

simple to calculate, using the average or prevalent<br />

global market prices. The assessment of the resource rents<br />

is more difficult. Theoretically, the present value of the<br />

forest should be equal to the net value of the forest owner’s<br />

future stump fees, from which the costs of growing<br />

the forest, throughout the maturation period, have been<br />

deducted. Generally, the exact figures reflecting the revenues<br />

and costs of forest owners are not available in many<br />

states, and therefore, various average prices for timber<br />

products, as well as the calculated regional resource rents<br />

(price – cost/price) were used in the study. 6<br />

In the case of agriculture land, assumptions were<br />

made concerning the average revenue from resource rent<br />

for ten cultures; the invariability of the agriculture land;<br />

as well as the average growth of 0.97% of agricultural production,<br />

per year, in the developed states, and a growth<br />

of 1.94% in the developing states. If the calculation year<br />

is t (based on the last assessment for 2005), the projected<br />

revenues for the period are t+24. 7<br />

In the case of protected areas, the best theoretical<br />

point of departure is the willingness of the consumers to<br />

pay for the existence of protected areas. The evaluation<br />

method based on the willingness to pay is implemented<br />

in the case of natural sites that do not directly produce<br />

revenues, but which are valuable for many other reasons.<br />

These sites may be unusual natural phenomena, like the<br />

Jägala Cascade, or red sandstone outcropping on the Ahja<br />

River in Taevaskoda. Since these natural wonders do not<br />

have a price, the following method is used to determine<br />

their value — people are asked how much they would be<br />

willing to pay to preserve these natural wonders. In this<br />

case, the survey depends on the sample of respondents.<br />

The same principles are applied to summarise the result<br />

as are used for determining the support for various political<br />

parties. Since the evaluation of natural wonders in<br />

this way is related primarily to individual examples, in<br />

order to apply this way of thinking more generally, and<br />

ensure comparability on an international scale, an evaluation<br />

method utilising quasi-alternative costs was used,<br />

which was based on the average productivity of crop land<br />

5 t+T–1<br />

The value Vt is calculated with the following formula: in which p i is a unit of rent income; q i the production volume; r<br />

V t = ∑ p i q i / (1 + r)i–t<br />

i=t<br />

the social discount rate and T the life span of the resource (depletion time). Although generally, assessments exist for<br />

the various sub-soil resources and possible depletion periods, actually, the assessment of the reserves and possible future production volumes<br />

are uncertain. In the calculations, the value T=20 is used for all sub-soil assets, or in other words, it is assumed that the sub-soil assets will be<br />

depleted in 20 years.<br />

6 To calculate the present value of forests, a timing value factor of 4%, and a time horizon of 25 years, is used. If the harvest exceeded the<br />

natural growth, the quotient of the difference between the forest reserve and the natural growth was used for the temporal assessment of the<br />

depletion of the forest reserves. If, based on this calculation, the depletion period for the forest reserves turned out to be less than 25 years,<br />

the appropriate shorter time period was used to calculate the value of the forest. When dealing with production reserves, the existence of<br />

infrastructure is also considered, which would ensure the accessibility of the timber, and the timber that is located more tan 50 km from the<br />

corresponding infrastructure is assessed as production reserves. Taking this fact into consideration means that only the forest which can be<br />

harvested and transported at a reasonable cost, due to the existence of the infrastructure, is taken into account.<br />

7 4% was used as the timed factor (The Changing Wealth of Nations, 2011, 149). In the case of pasture land, the general assumptions were the<br />

same; the global prices for beef and lamb, as well as milk and wool, were used to calculate the rent value; and the growth tempo was assessed<br />

at 0.89% annually, in the developed states, and 2.95% in the developing states (The Changing Wealth of Nations, 2011, 149).<br />

160<br />

Estonian Human Development Report 2012/2013

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