Promoting Rainwater Harvesting in Caribbean Small Island Developing States Water Availability Mapping for Grenada Preliminary findings

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Promoting Rainwater Harvesting in Caribbean Small Island Developing States Water Availability Mapping for Grenada Preliminary findings National Workshop Pilot Project funded by The United Nations Environment Programme Executed by The February 2006 Tropicana Hotel, Grenada

Procedural outline Objective: map areas on mainland Grenada subjected to moisture deficit Based on simplified water balance Determine the depth of runoff from water catchment areas (areas upstream of NAWASA intakes) Three analytical steps 1. Determine spatial variability in monthly rainfall 2. Determine spatial variability in evapotranspiration (ET) 3. Determine spatial variability in water deficit Catchments with low yield/runoff (during dry months) downstream communities expected to experience shortfalls

Most catchments located at high elevations; high rainfall Water yield is function of catchment area and effective rainfall (balance after ET) Water intake locations denoted as blue squares; catchments are blue shaded areas

Procedure Water balance partitioning of components of the hydrological cycle P = R + ET + S (simplified) P = rainfall ET = evapotranspiration S = storage In small island environments the storage component is negligible (relative to other components) Hence, after estimating losses to ET; remainder from precipitation input is runoff; available for use

Procedure STEP1: Rainfall spatial variability estimation Interpolation method; means of extrapolating rainfall estimates over unsampled areas In GIS, is automated procedure as alternative to conventional isohyetal (manual) method Limitation: Does not account for elevational influences at unsampled locations; with conventional method one can approximate influence of elevated terrain

Procedure STEP2: Evapotranspiration spatial variability estimation The FAO Penman-Monteith combination equation FAO guidelines for computing crop water requirements (Allen et al., 1998) Method recommended as the sole method for predicting ET o ; most closely estimates ET o where data parameters are missing (FAO Irrigation and Drainage Paper 56) Estimate for potential evapotranspiration is referenced from a well-watered grass surface

Procedure FAO Penman-Monteith combination equation ET o 0. 408 900 T 273 1 034. u R G u e e n 2 s a ET o = reference evapotranspiration (mm/day) R n = net radiation at crop surface (MJ/m 2 /day) G = heat flux density to the soil (MJ/m 2 /day) T = air temperature at 2 m height ( o C) u 2 = wind speed at 2 m height (m/s) e s = saturated vapor pressure (kpa) e a = actual vapour pressure (kpa) e s -e a = saturation vapour pressure deficit (kpa) = slope of vapour pressure curve (kpa/ o C) = psychrometric constant (kpa/ o C) 2

Assumptions Estimating ET Temperature (mean daily min, max) data across island not available; values derived from GIS map source. Adiabatic lapse rate to account for decrease in temps with elevation used Windspeed data across island not available; assumed at 2 m/s over island surface (FAO, 1998)

Procedure STEP 3: Estimating water deficit Simply the difference between rainfall input and ET losses Also referred to as effective rainfall Water available for abstraction potable (domestic) water; irrigation, livestock watering Rainfall/ET deficit surplus J F M A M J J A S O N D ET

Data quality Monthly rainfall data observations Interpolation revealed inconsistencies in rainfall monthly observations Vendome WTP station consistent under-reporting for all months Nianganfoix station - large deviation for September (excess of 800 mm!) Vendome WTP station excluded from analysis; Nianganfoix station excluded from September analysis only Interpolation with original data Adjusted interpolation suspect stations excluded

RESULTS: Spatial variation in mean monthly rainfall Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

RESULTS: Spatial variation in monthly evapotranspiration December (minimum) April August (maximum) ET is primarily a function of temperature (seasonal variation and elevation)

Rainfall March Water deficit Rainfall - ET Evapotranspiration

RESULTS: Spatial variation in mean rainfall deficit Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec

Vulnerable Catchments (runoff depth) Mount Nesbit -7.4 mm Birch Grove -7.5 mm Belle Vue -4.4 mm Minich -12.3 mm Mamma Cannes 1.5 mm Pomme Rose -8.1 mm By extension, communities exclusively dependent on these sources will be relatively vulnerable to water stress during dry months. Water supply augmentation strategies highly recommended (NOTE: there may be other abstraction sources not analyzed at this time; verification needed) March rainfall deficit

Target communities for RWH investment

Number consecutive months where mean rainfall < ET Year-round surplus Implications for rain-fed agriculture More dry months; shorter growing season; limits rain-fed production. Areas with high land capability (good land qualities) but severe deficit (high number consecutive dry months) are good candidate areas for investment in water augmentation measures (RWH and irrigation)

Planning Process permits objective spatial allocation (zoning) of resource distribution Investment in water abstraction and distribution systems Agriculture production zoning (crops, livestock) Build on previous FAO-supported initiative

Considerations Analysis is based on mean rainfall data observations May be wide variation around the mean. Should be further investigated in context of frequency analysis ET analysis may be improved with better parameter estimation Feedback from stakeholders on whether methodology is a suitable guide Are communities identified using methodology really at risk?

Thank You! The Morne, PO Box 1111, Castries, St. Lucia