Laserfiche WebLink
David Stavarek, R.G. <br /> June 29, 1998 <br /> Page 4 <br /> assessment should be interpreted as to be limited to the area within facility boundary. Health <br /> risks among off-site receptors associated with exposure pathways such as soil dust <br /> originating from the contaminated site, may be assessed only to estimate the magnitude of the <br /> partial contribution to the overall health risk. <br /> 3. Pooling of data. The Workplan proposes the use of the most recent 12-months of on-and <br /> off-site concentration data averaged both temporal and spatially. An average value is not <br /> sufficient to show that concentrations are increasing or decreasing as a function of time. It is <br /> suggested that data analysis of concentration of contaminants in groundwater include or be <br /> preceded by a trend analysis over time(a simple tabular or graphical form would be <br /> sufficient). If there is no evidence of trend over time, in particular of increasing <br /> concentrations, then the pooling of the data seems reasonable. Also, if results from <br /> groundwater sampling and analysis are not equally distributed among wells, but rather <br /> indicate one or more contaminated groundwater wells,then describe the procedure to be used <br /> to develop a representative concentration for the deterministic risk assessment. <br /> 4. Replacement value for censored data. The Workplan proposes the use of one-half the <br /> minimum detection limit value as a replacement for all censored data(page 16). This <br /> approach is not correct. Quantitation detection limits (QDLs) normally vary across <br /> analytical runs. Occasionally,values of QDLs are higher than the values of positively <br /> detected analytes in other analytical runs. The overall uncertainty of the data set for a <br /> particular contaminant,therefore, is affected by the results generated from the runs with the <br /> highest detection limit. It is recommended that each censored data be replaced with half of <br /> their respective QDLs for the chosen analytical run and method. <br /> 5. Definitions. In the equation for the 95%UCL of the mean (page 17) of normally distributed <br /> data, the following changes must be made: <br /> - in"mean of the traR&feffaed-data" delete the word transformed, <br /> - in"s= standard deviation of the#Fin.44med data" delete the word transformed; <br /> - it is suggested to use different symbols for the arithmetic mean and the mean of <br /> lognormally distributed data. <br /> 6. The statement in the last paragraph in page 17, that". . . datasets that are neither normal nor <br /> lognormal . . . are non-parametric' is not correct. Revise the concept, as there are many other <br /> parametric functions that are non-parametric. <br /> 7. Central tendency estimates from non-parametric data. The explanation of the method (pages <br /> 17-18) seems irrelevant. No data set in this project will be analyzed with a non-parametric <br /> statistical method. Please identify the data set if this is the case, and if so, it is sufficient with <br /> referencing the statistical method of analysis. <br />