Abstract
The assessment of management effectiveness in protected areas, i.e., the evaluation of whether management strategies are actually helping to achieve stated goals, is becoming a priority. In any such evaluation, accurate information concerning the dynamics of the managed system is required—information that is gathered through monitoring. Few protected areas, however, have well-developed monitoring plans, and reserve managers are faced with a shortage of protocols for their design. This paper proposes a methodology, applicable to a wide range of situations, for designing such plans. The process begins with the precise definition of the aims of the monitoring plan, followed by the identification of key ecological processes and management objectives for the area, and finally the selection of a reduced set of indicators. These indicators are represented at three levels of growing complexity, allowing the plan to be followed in a modular fashion and in agreement with available resources.
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Acknowledgments
This work is the result of collaboration between the Diputación General de Aragón and EUROPARC-España, via the Fundación Fernando González Bernáldez. Joaquín Guerrero, Director of the Natural Reserve, and Carme Pedrol provided the data from monitoring.
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Appendix: List of indicators selected for the monitoring plan
Appendix: List of indicators selected for the monitoring plan
LEVEL I | LEVEL II | |||
---|---|---|---|---|
PROGRAM | Variable | Units | Variable | Units |
Meteorology | Mean monthly temp. | °C | T max | °C |
Relative humidity | % | T min | °C | |
Accumulated rainfall | mm | Wind speed | m/sec | |
Maximum rainfall | mm | Wind direction | ° | |
Sunshine | hours/month | |||
Hydro-geology | Depth of water table | m | Depth of water table | m |
Fluvial dynamics | Mean discharge of Ebro | m3/sec | Floodable area | Ha |
Max. discharge of Ebro | m3/sec | Area flooded per year | Ha | |
Frequency of floods | year−1 | Sedimentation rate | cm/year | |
Maximum flood level | m | |||
Discharge (irrigation ditches) | m3/sec | |||
Depth (galachos) | cm | |||
Number of defense works | ||||
Length of defense works | m | |||
Water quality | Water temperature | °C | Cations Ca, Na, K, Mg, | mg/I |
pH | Anions (Cl, SO4) | mg/I | ||
Conductivity at 20°C | microS/c | Alkalinity | mg/I | |
m | CO3Ca | |||
Dissolved oxygen | mg/l O2 | Hardness Ca | mg/I CaCO3 | |
Turbidity | FTU | Hardness Mg | mg/I MgCO3 | |
Nitrites | mg/I NO2 | |||
Nitrates | mg/I NO3 | |||
Total ammonia | mg/I NH4 | |||
Phosphates | mg/I PO4 | |||
Total dissolved solids | mg/I | |||
Total suspended solids | mg/I | |||
Organic matter in suspension | mg/I O2 | |||
Dissolved organic material | mg/l O2 | |||
BOD5 | mg/I O2 | |||
COD | mg/I O2 | |||
Metals (As, Bo, Cd, Cr, Fe, Hg, Mn, Pb, Zn) | mg/I | |||
Total coliforms at 37°C | NMP/100 mI | |||
Pesticides | microg/I | |||
BMWP’ | ||||
Species | Richness in birds | N° spp | Species richness | ind/sp |
Bird diversity | Bit | Species diversity | bits/sp | |
Species density | Ind / ha | Threatened species | ||
Reproductive success | chicks/pair | |||
Population size | n° ind | |||
Exotic species | ||||
Reproductive success | chicks/pair | |||
Population size | n° ind | |||
Habitats / ecosystems | Cover of vegetation types | Ha | Richness of understory | n sp |
Coverage in habitats of community interest | Ha | Diversity of understory | bits | |
N° of Ha restored | Ha / habitat | Richness of tree layer | n sp | |
Diversity of tree layer | bits | |||
Mortality / sp | ind/sp | |||
Replacements / sp | ind/sp | |||
% survival | % | |||
Landscape | Landcover types | Ha | Landcover richness | n |
Lancover change | Ha/year | Landcover diversity | Bit | |
Landcover evenness | ||||
Number of patches | ||||
Mean distance among patches | km | |||
Human activities | Land ownership | Ha/category | Crops: | |
Urban planning | Ha/category | N°. of farms | ||
Agricultural area | Ha | Size of farms | Ha | |
Mean agric. yield | Tm/ha | Yield per variety | Tm/ha | |
Head of stock | Varieties | |||
Forested area | Ha | Stock: | ||
Forestry production (wood) | Tm/ha | N°. of farms | ||
Industrial use | Ha | Size of farms | Ha | |
Hunting | ind/sp | Stocking rate | head/ha | |
Gravel pits | Ha | Breeds | ||
Landfills | Ha | Forestry | ||
N°. exploitations | ||||
Size of exploitations | Ha | |||
Yield per species | Tm/ha | |||
Varieties | ||||
Recreation | N° visitors | N° ind | Frequency per zone | Ind |
N°. groups | N° groups | Origin of visitors | % | |
Size of groups | N° ind/group | Activities performed |
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Mezquida, J.A.A., De Fernández, J.V.L. & Yangüas, M.A.M. A Framework for Designing Ecological Monitoring Programs for Protected Areas: A Case Study of the Galachos del Ebro Nature Reserve (Spain). Environmental Management 35, 20–33 (2005). https://doi.org/10.1007/s00267-003-0051-0
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DOI: https://doi.org/10.1007/s00267-003-0051-0