Monte Carlo Level III Probabilistic Calculation
Lognormal Distributions for the HalfLives Triangular Distributions for the HalfLives View Pesticide Emissions in the Great Lakes States View 2002 Great Lakes Toxic Air Emissions Inventory There are two choices when running the model in Monte Carlo mode: lognormal distributions for the halflives and triangular distributions. Biodegradation data collected for a limited number of pesticides suggest that the degradation profile is typically lognormally distributed and a mean halflife and standard deviation is required to develop the distribution function. In the absence of data, risk assessors often employ triangular distributions consisting of a minimum, maximum, and most likely value. The Henry's Law constant, log Kow, and vapor pressure are also treated as log normally distributed probabilistic input parameters; however, the coefficient of variation (CV) is fixed. We based the CV for each of these parameters on data obtained from SRC databases, published papers, estimation programs, and recommendations made in the CALTOX multimedia fate model. The CV for the Henry's Law constant and vapor pressure is assumed to be 1, while the standard deviation for the log Kow is assumed to be 0.5 log units. Lognormal distributions for the degradation halflife of several pesticides in soil are shown below. In general the coefficient of variation (ratio of standard deviation to the mean halflife) ranges from approximately 0.5 to 2.
View the fitted distribution functions for these chemicals. How can I estimate the input parameters?
The best method is to collect experimental data on the degradation profile of your chemical
and fit the data to a lognormal distribution function.
In the absence of any experimental data the model can estimate these
values for you based upon your chemical's structure. However, these values in water, soil,
and sediment are very approximate at best. Moreover, the halflife estimation in air only considers
degradation via atmospheric oxidants and does not take into account the possibility of direct photolysis.
Therefore, halflives may be underestimated for compounds that are susceptible to direct photolysis.

