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Indicators for Monitoring Biodiversity: A Hierarchical Approach

REED F. NOSS

US. Environmental Protection Agency, Environmental Research Laboratory, Corvallis, OR 97333, U.S.A.

Current address is 925 NW. 31st Street, Corvallis, OR 47330Search for more papers by this author
First published: December 1990
Cited by: 1218

Abstract

en

Abstract: Biodiversity is presently a minor consideration in environmental policy. It has been regarded as too broad and vague a concept to be applied to real‐world regulatory and management problems. This problem can be corrected if biodiversity is recognized as an end in itself, and if measurable indicators can be selected to assess the status of biodiversity over time. Biodiversity, as presently understood, encompasses multiple levels of biological organization. In this paper, I expand the three primary attributes of biodiversity recognized by Jerry Franklin — composition, structure, and function—into a nested hierarchy that incorporates elements of each attribute at four levels of organization: regional landscape, community‐ecosystem, population‐species, and genetic. Indicators of each attribute in terrestrial ecosystems, at the four levels of organization, are identified for environmental monitoring purposes. Projects to monitor biodiversity will benefit from a direct linkage to long‐term ecological research and a commitment to test hypotheses relevant to biodiversity conservation. A general guideline is to proceed from the top down, beginning with a coarse‐scale inventory of landscape pattern, vegetation, habitat structure, and species distributions, then overlaying data on stress levels to identify biologically significant areas at high risk of impoverishment. Intensive research and monitoring can be directed to high‐risk ecosystems and elements of biodiversity, while less intensive monitoring is directed to the total landscape (or samples thereof). In any monitoring program, particular attention should be paid to specifying the questions that monitoring is intended to answer and validating the relationships between indicators and the components of biodiversity they represent.

Abstract

es

Resumen: La biodiversidad es hasta ahora una consid‐eración menor en lapolitica ambiental. Se ha visto como un concepto demasiado amplio y vago para ser aplicado en las regulaciones y el manejo de los problemas del mundo real. Este problema se puede corregir si la biodiversidad es reconocida como unfinporsi misma, y si se pueden seleccionar indicadores cuantificables para determinar el estado de la biodiversidad a través del tiempo. La biodiversidad, como se entiende actualmente comprende múltiples niveles de organización biológica En esta disertación, extiendo los tres atributos primarios de la biodiversidad reconocidos por Jerry Franklin — composición, estructura y función — dentro de unajerarquia que encaja a incorpora los elementos de cada uno de los atributos en cuatro niveles de organización: paisaje regional, ecosistemas de las comunidades, población de especies y genética Los indicadores de cada atributo en los ecosistemas terrestres, en los cuatro niveles de organización, son identificados para propósitos de monitoreo ambiental. Los proyectos para el monitoreo de la biodiversidad se beneficiarian de una unión directa con la investigación ecológica a laqo plazo y de un compromiso paraprobar hipótesis relevantes a la consmacidn de la biodiversidact. Un lineamiento general es proceder de arriba para abajo, empezando con una escala‐burda de inventario de los patrones del paisaje, de la vegetación, de la estructura del hábitat y de la distribución de ls especies, después super‐poner los datos sobre niveles de presión para identificar las areas da alto riezgo y de empobrecimiento. La investigación intensive y el monitorio peude ser dirigido a los ecosistemas de alto riezgo y a los elementos de la biodiversidad, mientras que un monitoreo ménos intenso se puede dirigir a1 total del paisaje (O a muestras del mismo). En cualquier programa de monitoreo, se debe de poner atención especial a1 estar espe‐cificando las preguntas que el monitoreo pretende resolver y al estar validando las relaciones entre los indicadores y los componentes de la biodiversidad que representen.

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  • , EDITOR'S CHOICE: Enhancing gardens as habitats for flower‐visiting aerial insects (pollinators): should we plant native or exotic species?, Journal of Applied Ecology, 52, 5, (1156-1164), (2015).
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  • , Assessing significant harm to terrestrial ecosystems from contaminated land, Soil Use and Management, 21, (527-540), (2006).
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  • , Diversity of dung and carrion beetles in a disturbed Mexican tropical montane cloud forest and on shade coffee plantations, Biodiversity and Conservation, 14, 3, (601), (2005).
  • , Ecological and social evaluation of landscape in a rural area with terraced paddies in southwestern Japan, Landscape and Urban Planning, 70, 3-4, (301), (2005).
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  • , Biodiversity in Urban Governance and Planning: Examples from Swedish Cities, Planning Theory & Practice, 6, 3, (283), (2005).
  • , Measuring conditions and trends in ecosystem services at multiple scales: the Southern African Millennium Ecosystem Assessment (SAfMA) experience, Philosophical Transactions of the Royal Society B: Biological Sciences, 360, 1454, (425), (2005).
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  • , An analysis of central Alpine capercaillie spring habitat at the forest stand scale, Forest Ecology and Management, 215, 1-3, (307), (2005).
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  • , Conservation Status as a Biodiversity Trend Indicator: Recommendations from a Decade of Listing Species at Risk in British Columbia, Conservation Biology, 19, 4, (1306-1311), (2005).
  • , Testing the Value of Six Taxonomic Groups as Biodiversity Indicators at a Local Scale, Conservation Biology, 18, 3, (667-675), (2004).
  • , Characteristics of Australia's rangelands and key design issues for monitoring biodiversity, Austral Ecology, 29, 1, (3-15), (2004).
  • , Monitoring rangeland biodiversity: Plants as indicators, Austral Ecology, 29, 1, (59-77), (2004).
  • , Selecting areas to protect the biodiversity of aquatic ecosystems in a semiarid Mediterranean region using water beetles, Aquatic Conservation: Marine and Freshwater Ecosystems, 14, 5, (465-479), (2004).
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  • , Preliminary assessment of the flagship species concept at a small scale, Animal Conservation, 7, 1, (63-70), (2006).
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  • , Diversity and distribution of sedges on multivariate environmental gradients, African Journal of Ecology, 42, (21-33), (2004).
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  • , Beyond Species Richness: Community Similarity as a Measure of Cross‐Taxon Congruence for Coarse‐Filter Conservation, Conservation Biology, 18, 1, (167-173), (2004).
  • , The Threat of Transformation: Quantifying the Vulnerability of Grasslands in South Africa, Conservation Biology, 18, 2, (466-477), (2004).
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