|
APPENDIX B: SHOOTER ACCURACYThe four contributory parameters characterising shooter accuracy, as described in Part 1, the User Manual, are specified as standard deviations as follows (given with their units):
The 'Basic error' is converted to radians within the
program. The 'Basic error' and 'Swing error' are measures of
aim distribution about the mean. However 'Lead error' is a
measure of variability about the correct lead angle, given
as a percentage of the correct lead. Similarly, 'Range
error' is specified as a percentage of the actual range.
These are used in the following first-order approximations
to determine the contributions to total dispersion of aim.
The first three terms are considered independent, but the
where
Eleven sample datafiles are provided representing shooter ability. The parameter values for each category -poor, fair, good, very good, super - vary according to whether the target is a clay pigeon or a gamebird. The 'perfect' category is the same for either target: this equates to a target fixed in the centre of the pellet pattern. The sample datafile parameter values are listed below, together with bag/hit rates predicted by the program for typical conditions (program repetition = 5000 shots per range). The values are advised here as being representative of the shooter accuracy errors; specific values may be obtained by direct measurement or by fitting the program results to observations from well-controlled trials. Error Basic Swing Lead Range Bag rate* * Lead #6 (2.6mm) shot at 400m/s. Mallard underside, 15m/s. Long-ranging.1/2 choke. Shooter Characteristics versus Standard Clay Pigeon**
* Lead #71/2 (2.3mm) shot at 400m/s. Clay pigeon at 30°, 15m/s. Long-ranging. 1/2 choke These contributions to dispersion are then combined
where x and y are respectively parallel and perpendicular to the target path as seen by the shooter. These total dispersions of aim are then used to drive a random Gaussian generator, sampled to determine the aimpoint of every simulated firing. Published 22 December 1998 Return to Wildlife and Countryside Index Return to DEFRA Home Page |