43 C.F.R. § 11.83
(a) General.
(2)
(3) The authorized official shall determine that the following criteria have been met when choosing among the cost estimating and valuation methodologies. The authorized official shall document this determination in the Report of the Assessment. Only those methodologies shall be chosen:
(4) Factors that may be considered by trustees to evaluate the feasibility and reliability of methodologies can include:
(b) Costs of restoration, rehabilitation, replacement, and/or acquisition of equivalent resources.
(1) Costs for restoration, rehabilitation, replacement, and/or acquisition of equivalent resources are the amount of money determined by the authorized official as necessary to complete all actions identified in the selected alternative for restoration, rehabilitation, replacement, and/or acquisition of equivalent resources, as selected in the Restoration and Compensation Determination Plan of § 11.81 of this part. Such costs shall include direct and indirect costs, consistent with the provisions of this section.
(2) Cost estimating methodologies. The authorized official may choose among the cost estimating methodologies listed in this section or may choose other methodologies that meet the acceptance criterion in paragraph (b)(3) of this section. Nothing in this section precludes the use of a combination of cost estimating methodologies so long as the authorized official does not double count or uses techniques that allow any double counting to be estimated and eliminated in the final damage calculation.
(c) Compensable value.
(1) Compensable value is the amount of money required to compensate the public for the loss in services provided by the injured resources between the time of the discharge or release and the time the resources are fully returned to their baseline conditions, or until the resources are replaced and/or equivalent natural resources are acquired. The compensable value can include the economic value of lost services provided by the injured resources, including both public use and nonuse values such as existence and bequest values. Economic value can be measured by changes in consumer surplus, economic rent, and any fees or other payments collectible by a Federal or State agency or an Indian tribe for a private party's use of the natural resources; and any economic rent accruing to a private party because the Federal or State agency or Indian tribe does not charge a fee or price for the use of the resources. Alternatively, compensable value can be determined utilizing a restoration cost approach, which measures the cost of implementing a project or projects that restore, replace, or acquire the equivalent of natural resource services lost pending restoration to baseline.
(2) Valuation methodologies. The authorized official may choose among the valuation methodologies listed in this section to estimate appropriate compensation for lost services or may choose other methodologies provided that the methodology can satisfy the acceptance criterion in paragraph (c)(3) of this section. Nothing in this section precludes the use of a combination of valuation methodologies so long as the authorized official does not double count or uses techniques that allow any double counting to be estimated and eliminated in the final damage calculation.
| Type of Methodology | Description |
|---|---|
| (i) Market price | The authorized official may determine the compensable value of the injured resources using the diminution in the market price of the injured resources or the lost services. May be used only if: |
| (A) The natural resources are traded in the market; and | |
| (B) The authorized official determines that the market for the resources, or the services provided by the resources, is reasonably competitive. | |
| (ii) Appraisal | The measure of compensable value is the difference between the with- and without-injury appraisal value determined by the comparable sales approach as described in the Uniform Appraisal Standards. Must measure compensable value, to the extent possible, in accordance with the “Uniform Appraisal Standards for Federal Land Acquisition,” Interagency Land Acquisition Conference, Washington, DC, 1973 (incorporated by reference, see § 11.18). |
| (iii) Factor income (sometimes referred to as the “reverse value added” methodology) | May be used only if the injured resources are inputs to a production process, which has as an output a product with a well-defined market price. May be used to determine: (A) The economic rent associated with the use of resources in the production process; and (B) The in-place value of the resources. |
| (iv) Travel cost | May be used to determine a value for the use of a specific area. Uses an individual's incremental travel costs to an area to model the economic value of the services of that area. Compensable value of the area to the traveler is the difference between the value of the area with and without a discharge or release. Regional travel cost models may be used, if appropriate. |
| (v) Hedonic pricing | May be used to determine the value of nonmarketed resources by an analysis of private market choices. The demand for nonmarketed natural resources is thereby estimated indirectly by an analysis of commodities that are traded in a market. |
| (vi) Unit value/benefits transfer | Unit values are preassigned dollar values for various types of nonmarketed recreational or other experiences by the public. Where feasible, unit values in the region of the affected resources and unit values that closely resemble the recreational or other experience lost with the affected resources may be used. |
| (vii) Contingent valuation | Includes all techniques that set up hypothetical markets to directly elicit an individual's economic valuation of a natural resource. Can determine: |
| (A) Use values and explicitly determine option and existence values; and | |
| (B) Lost use values of injured natural resources. | |
| (viii) Conjoint Analysis | Like contingent valuation, conjoint analysis is a stated preference method. However, instead of seeking to value natural resource service losses in strictly economic terms, conjoint analysis compares natural resource service losses that arise from injury to natural resource service gains produced by restoration projects. |
| (ix) Habitat Equivalency Analysis | May be used to compare the natural resource services produced by habitat or resource-based restoration actions to natural resource service losses. |
| (x) Resource Equivalency Analysis | Similar to habitat equivalency analysis. This methodology may be used to compare the effects of restoration actions on specifically identified resources that are injured or destroyed. |
| (xi) Random Utility Model | Can be used to: (A) Compare restoration actions on the basis of equivalent resource services provided; and (B) Calculate the monetary value of lost recreational services to the public. |
[51 FR 27725, Aug. 1, 1986, as amended at 53 FR 5175, Feb. 22, 1988; 59 FR 14285, Mar. 25, 1994; 73 FR 57266, Oct. 2, 2008]