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-rw-r--r--man/FOMC.solution.Rd99
1 files changed, 51 insertions, 48 deletions
diff --git a/man/FOMC.solution.Rd b/man/FOMC.solution.Rd
index 55d89709..54430dd1 100644
--- a/man/FOMC.solution.Rd
+++ b/man/FOMC.solution.Rd
@@ -1,48 +1,51 @@
-\name{FOMC.solution}
-\alias{FOMC.solution}
-\title{ First-Order Multi-Compartment kinetics }
-\description{
- Function describing exponential decline from a defined starting value, with
- a decreasing rate constant.
-
- The form given here differs slightly from the original reference by Gustafson
- and Holden (1990). The parameter \code{beta} corresponds to 1/beta in the
- original equation.
-}
-\usage{
-FOMC.solution(t, parent.0, alpha, beta)
-}
-\arguments{
- \item{t}{ Time. }
- \item{parent.0}{ Starting value for the response variable at time zero. }
- \item{alpha}{
- Shape parameter determined by coefficient of variation of rate constant
- values. }
- \item{beta}{
- Location parameter.
-}
-}
-\note{
- The solution of the FOMC kinetic model reduces to the
- \code{\link{SFO.solution}} for large values of \code{alpha} and
- \code{beta} with
- \eqn{k = \frac{\beta}{\alpha}}{k = beta/alpha}.
-}
-\value{
- The value of the response variable at time \code{t}.
-}
-\references{
- FOCUS (2006) \dQuote{Guidance Document on Estimating Persistence and
- Degradation Kinetics from Environmental Fate Studies on Pesticides in EU
- Registration} Report of the FOCUS Work Group on Degradation Kinetics,
- EC Document Reference Sanco/10058/2005 version 2.0, 434 pp,
- \url{http://esdac.jrc.ec.europa.eu/projects/degradation-kinetics}
-
- Gustafson DI and Holden LR (1990) Nonlinear pesticide dissipation in soil: A
- new model based on spatial variability. \emph{Environmental Science and
- Technology} \bold{24}, 1032-1038
-}
-\examples{
- plot(function(x) FOMC.solution(x, 100, 10, 2), 0, 2, ylim = c(0, 100))
-}
-\keyword{ manip }
+% Generated by roxygen2: do not edit by hand
+% Please edit documentation in R/FOMC.solution.R
+\name{FOMC.solution}
+\alias{FOMC.solution}
+\title{First-Order Multi-Compartment kinetics}
+\usage{
+FOMC.solution(t, parent.0, alpha, beta)
+}
+\arguments{
+\item{t}{Time.}
+
+\item{parent.0}{Starting value for the response variable at time zero.}
+
+\item{alpha}{Shape parameter determined by coefficient of variation of rate
+constant values.}
+
+\item{beta}{Location parameter.}
+}
+\value{
+The value of the response variable at time \code{t}.
+}
+\description{
+Function describing exponential decline from a defined starting value, with
+a decreasing rate constant.
+}
+\details{
+The form given here differs slightly from the original reference by
+Gustafson and Holden (1990). The parameter \code{beta} corresponds to 1/beta
+in the original equation.
+}
+\note{
+The solution of the FOMC kinetic model reduces to the
+ \code{\link{SFO.solution}} for large values of \code{alpha} and
+ \code{beta} with \eqn{k = \frac{\beta}{\alpha}}{k = beta/alpha}.
+}
+\examples{
+
+ plot(function(x) FOMC.solution(x, 100, 10, 2), 0, 2, ylim = c(0, 100))
+
+}
+\references{
+FOCUS (2006) \dQuote{Guidance Document on Estimating Persistence
+ and Degradation Kinetics from Environmental Fate Studies on Pesticides in
+ EU Registration} Report of the FOCUS Work Group on Degradation Kinetics,
+ EC Document Reference Sanco/10058/2005 version 2.0, 434 pp,
+ \url{http://esdac.jrc.ec.europa.eu/projects/degradation-kinetics}
+
+ Gustafson DI and Holden LR (1990) Nonlinear pesticide dissipation in soil:
+ A new model based on spatial variability. \emph{Environmental Science and
+ Technology} \bold{24}, 1032-1038
+}

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