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```
#scripts to compute traditional measures of sprinkler uniformity
# see IA "Irrigation" text and others
###function to calculate CU, Christiansen's uniformity coefficient
"CU" = function(x)
{
x<-na.exclude(x)
((mean(x) - (sum(abs(x - mean(x)))/length(x)))/mean(x)) * 100
}
#function to to distribution uniformity
#of low-quarter
"DU"=function(x)
{
x<-na.exclude(x) # guard against padded data e.g., for created square/rectangular region from irregular area
#get subarray of low quarter
x<-sort(x)
end<-round(length(x)/4,digits=0)
mean(x[1:end])/mean(x)*100
}
#function to compute Distribution uniformity of low half
"DU.lh"=function(x)
{
x<-na.exclude(x)
x<-sort(x)
end<-round(length(x)/2,digits=0)
mean(x[1:end])/mean(x)*100
}
# find percentile of area receiving target depth or more (by area covered assuming equal area per catch can)
# x is array of catch can data, target is target application depth. If target is soil moisture
# deficit, then similar concept as PELQ, except catch rather than application rate is used.
# to be analogous to PELQ or AELQ, a target equal to a percentile of 87.5 (mid of low quartile or 25%) for adequacy assuming a normal
# distribution, would be returned. With a small standard deviation, however, the percentile could "look bad" but a good AELQ
# could result since this is based on averages of low quartile and overall average rather than percentile.
# Best use of percentile would be for application efficiency with a target equal to SMD, so that anything greater than SMD
# would in theory not be held in the root zone so would be inefficient. Otherwise, depending upon application uniformity, it may be
# a poor measure of system performance. In short it is a measure of efficiency relative to a target (keep application less
# than or equal to target) rather than uniformity. The larger the target amount, the greater the efficiency,
# assuming that less than target with stay in root zone, but a lower adequacy will result.
# Use consistent units (SI, or US custom)
"adper"=function(x,target,plot=TRUE)
{
out<-ecdf(x) (target)
adeq<-1-out # frame as receiving target or more versus target as a percentile of catches
ae<-out # percentile <= target amount. If target is SMD, then percentile of area
# receiving less or equal to SMD.
d<-density(x,n=512,cut=3)
xx=d$x;yy=d$y;dx <- xx[2L] - xx[1L];C <- sum(yy) * dx ## sum(yy * dx)
adeq.unscaled <- sum(yy[xx >= target]) * dx;adeq.scaled <- adeq.unscaled / C # estimate of adequacy from density plot
eff.unscaled<-sum(yy[xx <= target]) * dx;eff.scaled<-eff.unscaled/C # estimate of efficiency (at or below target)
if(plot)
{
plot(d,main="Density Plot of Catch Data", xlab="catch depth")
abline(v=target,col=2)
text(target,0.0,"target depth",srt=90,adj=c(0,1))
#print(xx);print(yy);print(2L);print(1L);print(C)
xl<-c(min(x),max(x))
plot(ecdf(x),verticals=TRUE,main="cumulative distribution",ylab="cum. prob.",xlab="depth applied (caught)",xlim=xl)
abline(v=target,col=2)
text(target,0.5,"target depth",srt=90,adj=c(0,1))
}
return(list("adequacy.density=",adeq.scaled,"eff.density=",eff.scaled,"adequacy.ecdf=",adeq,"eff.ecdf=",ae))
}
"eff"=function(x,target){
# unlike adper, this function needs to quantify total volumes of water applied,
# and volume below target depth (e.g., SMD or that below root zone) that is inefficient
# and volume of under-irrigation (inadequate). These volumes can be visualized in 2 dimensions
# as a cumulative distribution plot of applied amounts assuming an unbiased sampling across the
# irrigated area (even catch can distribution). So it must be more than areas under a density plot, and
# must include the applied depth (x-axis) in the computations of efficiency and adequacy (by volume) if using
# a density plot. This can be acheived by weighting the density (relative # observations)
# by mutiplying by applied depth, e.g. yy*dx*xx Alternative would be to accumulate the density plot
# and operate on that smoothed ecdf curve.
# use values of x (catch depth) with density to get areas above target and below target
# sum(yy) for those values of xx less than or greater than target
# adequacy just looks at land area receiving equal to or more than the target, i.e., no credit for areas
# receiving more than target amount. As target depth decreases relative to the mean applied depth
# appeff decreases and appadeq increases (and vice-versa)
d<-density(x,n=512,cut=3)
xx=d$x;yy=d$y;dx <- xx[2L] - xx[1L];C <- sum(yy) * dx ## sum(yy)* dx (total area). This is just area
#under curve and does not account for magnitude of depth difference from target
total<-sum(yy*xx)*dx # total area weighted by depth - this will equal the mean (or very close)
above.x<-xx[xx>target];above.x<-above.x-target# array of x - target for above target, i.e., excess irrigation
# i.e., horizontal lines from right side of curve to target
above.y<-yy[xx > target] # pull all y values (density or relative occurrences) to right of target
excess<-sum(above.y*above.x)*dx # weighted area greater (to right of) target depth (inefficient)
eff<-1-excess/total # CC is total area weighted by depth
below.x<-xx[xx<=target];below.x<-target-below.x# array of target-x for each x below target, i.e., array of 1D deficits
below.y<-yy[xx <= target];deficit<-sum(below.y*below.x)*dx #weighted area under curve to left of target (inadequate)
target.area<-sum(yy*target)*dx # target area (target depth * all entries*dx)
#print(total);print(deficit);print(excess);print(target.area)
adeq<-1-(deficit/target.area) # 1- deficit area/(area of target and less * target)
return(list("appeff"=eff,"appadeq"=adeq))
}
```

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