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Data <strong>an</strong>alysis techniques<br />

We syn<strong>the</strong>sized all data from <strong>the</strong> 8 iButton temperature loggers on <strong>the</strong> western slope, <strong>the</strong> HOBO<br />

wea<strong>the</strong>r station, <strong>an</strong>d <strong>the</strong> precipitation logger into hourly values to create 24-day periods during <strong>the</strong><br />

2005 dry, 17 June to 11 July, <strong>an</strong>d wet, 7 to 31 December, se<strong>as</strong>ons. These sample periods were<br />

chosen b<strong>as</strong>ed on data availability <strong>an</strong>d central proximity to <strong>the</strong> dry <strong>an</strong>d wet se<strong>as</strong>ons. We created<br />

composite averages of 24 hourly me<strong>as</strong>urements for all 24 days making up <strong>the</strong> wet <strong>an</strong>d dry<br />

periods—<strong>the</strong> diurnal cycle. Hence, composites are averages for each hour over <strong>the</strong> 24-day periods.<br />

The vector components of wind speed were calculated to create composite averages of speed <strong>an</strong>d<br />

direction. Because we were interested in microscale variability, particularly elevation effects, we<br />

concentrated on <strong>an</strong>alyzing <strong>an</strong>d comparing <strong>the</strong> composite diurnal cycles of meteorological<br />

components for <strong>the</strong> wet <strong>an</strong>d dry periods.<br />

Estimating Evapotr<strong>an</strong>spiration<br />

It is difficult to me<strong>as</strong>ure ET accurately, particularly in remote mountainous regions with steep<br />

topography; most me<strong>as</strong>urements require expensive equipment <strong>an</strong>d frequent mainten<strong>an</strong>ce (refs).<br />

Consequently, <strong>the</strong>re are a multitude of methods for estimating ET, most of which require site<br />

specific parameters <strong>an</strong>d b<strong>as</strong>ic meteorological me<strong>as</strong>urements. Evaporation rates, ignoring<br />

tr<strong>an</strong>spiration, are commonly estimated by energy bal<strong>an</strong>ce, aerodynamic, <strong>an</strong>d a combination of both<br />

methods, such <strong>as</strong> Penm<strong>an</strong> (1945; 1963) <strong>an</strong>d Penm<strong>an</strong>-Monteith. Xu <strong>an</strong>d Singh (1998; 2002) report<br />

on meteorological forcing of <strong>an</strong>d compares methods of estimating ET b<strong>as</strong>ed on input data from<br />

Ch<strong>an</strong>gines station in Switzerl<strong>an</strong>d. We used a similar modeling approach <strong>an</strong>d applied it to <strong>the</strong><br />

Ll<strong>an</strong>g<strong>an</strong>uco valley. Allen et al. (1989) reports on <strong>the</strong> FAO methods for estimating potential ET<br />

(ET0) b<strong>as</strong>ed on Penm<strong>an</strong> combination equations for reference surfaces, such <strong>as</strong> uniform 120 mm<br />

tall gr<strong>as</strong>s used herein. Because of it’s inclusion of several commonly used models for estimating<br />

ET0, we elected to use <strong>the</strong> REF-ET software developed by Allen et al. (1998) <strong>an</strong>d selected <strong>the</strong><br />

Penm<strong>an</strong>-Monteith FAO method for estimating hourly ET0 during <strong>the</strong> dry <strong>an</strong>d wet periods. This<br />

will serve <strong>as</strong> a b<strong>as</strong>e-line for comparison to a more realistic physics-b<strong>as</strong>ed model for ET. The<br />

equations for <strong>the</strong> FAO methods are explained in detail by Allen et al. (1998).<br />

We selected <strong>the</strong> BROOK90 (v.4.4e) model (Federer et al., 2003; Federer, 1995) to estimate <strong>the</strong><br />

actual ET during <strong>the</strong> dry <strong>an</strong>d wet se<strong>as</strong>on composite days. BROOK90 includes strong physicallyb<strong>as</strong>ed<br />

determination of ET, a graphic user interface, <strong>an</strong>d <strong>the</strong> visual b<strong>as</strong>ic code is available for<br />

modification. The model simulates deposition <strong>an</strong>d sublimation of frozen water <strong>an</strong>d <strong>as</strong>sumes<br />

snowfall for near-surface air temperature below –1.5°C. The model meteorological input includes<br />

solar radiation, air temperature, vapor pressure, wind speed, <strong>an</strong>d precipitation. Soil <strong>an</strong>d vegetation<br />

parameters were me<strong>as</strong>ured in <strong>the</strong> field. Additional parameters were taken from <strong>the</strong> literature <strong>as</strong><br />

reported by Federer et al. (2003). Model output includes hydrological bal<strong>an</strong>ce components of <strong>the</strong><br />

vegetation c<strong>an</strong>opy <strong>an</strong>d soil surface; we here report on <strong>the</strong> ET components.<br />

BROOK90 simulates evaporation <strong>an</strong>d soil-water movement using a process-oriented approach<br />

for sparse c<strong>an</strong>opies at a single location within a watershed. The model estimates interception <strong>an</strong>d<br />

tr<strong>an</strong>spiration from a single-layer pl<strong>an</strong>t c<strong>an</strong>opy, soil <strong>an</strong>d snow evaporation/sublimation, snow<br />

accumulation <strong>an</strong>d melt, <strong>an</strong>d soil water movement through multiple soil layers. Potential<br />

evaporation rates are obtained using <strong>the</strong> Shuttleworth <strong>an</strong>d Wallace (1985) modification of <strong>the</strong><br />

Penm<strong>an</strong>-Monteith combination equation.<br />

Actual tr<strong>an</strong>spiration is <strong>the</strong> lesser of potential tr<strong>an</strong>spiration <strong>an</strong>d a soil water supply rate<br />

determined by <strong>the</strong> resist<strong>an</strong>ce to liquid water flow in <strong>the</strong> pl<strong>an</strong>ts <strong>an</strong>d on root distribution <strong>an</strong>d soil<br />

water potential in <strong>the</strong> soil layers (Federer, 1979). For potential tr<strong>an</strong>spiration, c<strong>an</strong>opy resist<strong>an</strong>ce<br />

depends on maximum leaf conduct<strong>an</strong>ce, reduced for humidity, temperature, <strong>an</strong>d light penetration.<br />

Each soil layer <strong>an</strong>d <strong>the</strong> roots of vegetation have a resist<strong>an</strong>ce to water flow b<strong>as</strong>ed on field<br />

observations <strong>an</strong>d published results. Aerodynamic resist<strong>an</strong>ces are modified from Shuttleworth <strong>an</strong>d<br />

Gurney (1990); <strong>the</strong>y depend on leaf area index (LAI), which c<strong>an</strong> vary se<strong>as</strong>onally, <strong>an</strong>d on c<strong>an</strong>opy<br />

height, which determines stem area index (SAI). Potential tr<strong>an</strong>spiration or potential interception<br />

are obtained using <strong>the</strong> actual or existing soil surface wetness in <strong>the</strong> Shuttleworth-Wallace<br />

equations. The equations <strong>the</strong>n provide <strong>the</strong> total soil or ground evaporation. The total ET is <strong>the</strong> sum<br />

of precipitation evaporated from <strong>the</strong> c<strong>an</strong>opy, soil evaporation, <strong>an</strong>d tr<strong>an</strong>spiration from <strong>the</strong> c<strong>an</strong>opy.<br />

269

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