Questions? Call 888-624-8373

PAPERBACK + PDF
your price: $53.00
add to cart

PAPERBACK
list:$45.00
Web:$40.50
add to cart

PDF BOOK
your price: $34.50
add to cart

PDF CHAPTERS
your price: $4.40
select

Rights & Permissions

topleft topright

Valuing Ecosystem Services: Toward Better Environmental Decision-Making (2004)
Water Science and Technology Board (WSTB)

Page
83
bottomleft bottomright

The following HTML text is provided to enhance online readability. Many aspects of typography translate only awkwardly to HTML. Please use the page image as the authoritative form to ensure accuracy.


Valuing Ecosystem Services: Toward Better Environmental Decision–Making

Functions

Ecosystem Processes and Components

Goods and Services

Cultural and artistic

Variety in natural features with cultural and artistic value

Inspiration for creative activities

Spiritual and historic

Variety in natural features with spiritual and historic value

Use of nature for religious or historic purposes

Science and education

Variety in nature with scientific and educational value

Use of nature for education and research

 

SOURCE: Adapted from de Groot et al. (2002).

ISSUES AFFECTING IDENTIFICATION OF GOODS AND SERVICES

Ecosystems vary in time and space. As ecologists extend their analyses of ecosystem structure and function to include potential goods and services, the uncertainty affecting assessments increases across both time and space. The interaction of ecological and social systems makes extrapolation of observations and prediction of future conditions exceptionally complex (Berkes et al., 2003; Gunderson and Holling, 2002; Gunderson and Pritchard, 2002). The challenges arise from the heterogeneity of ecosystems and values across space which complicates aggregation for assessment at larger scales, and from nonlinear system behavior that confounds forecasting. Recognition of the thresholds of change in both space and time is one of the principal challenges in ecological research.

Scale

It may be argued that almost all ecosystem functions can be performed by aquatic ecosystems at any scale. Indeed, Limburg et al. (2002) found that scaling rules describing production and delivery of ecosystem services are yet to be formulated and quantified (as noted in the preceding sections). However, there are clearly thresholds in the level of their relative importance. For example, individual wetlands in a watershed may each have the capacity to slow the flow of waters moving through them, but this function becomes important only when there are a sufficient number of wetlands in a watershed to significantly alter the flow of floodwaters downstream.

The complication in assessment of ecosystem goods and services arises because the scale at which functions become important is not always the same.

Page
83