Outdoor Lighting and Crime - Amper
Outdoor Lighting and Crime - Amper
Outdoor Lighting and Crime - Amper
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On the assumption that roads <strong>and</strong> paths had been cleared of snow <strong>and</strong> that the snow was<br />
contaminated by vehicle exhaust particles, the effective terrain reflectance was estimated to be<br />
0.7 for Minneapolis <strong>and</strong> 0.6 for St Louis. The light energy loss values were divided by 2.56<br />
<strong>and</strong> 2.04 respectively (from Table 4) to give values more likely to be representative of nosnow<br />
conditions. In the case of Buffalo, Denver <strong>and</strong> Kansas City, the effective terrain<br />
reflectance was thought more likely to be about 0.3 at the time of measurement. The factor<br />
for light energy loss correction to no-snow conditions for these three cities was therefore 1.52.<br />
The corrected data points were closer to the notional trend line of Figure 8, but still to its right<br />
(brighter) side. The corrected light energy losses for Minneapolis, St Louis, Buffalo, Denver<br />
<strong>and</strong> Kansas City are shown in parentheses in Tables 5 <strong>and</strong> 6.<br />
The linear regression analysis was repeated for the plot values of Figure 7 after the corrections<br />
to give no-snow conditions were applied to the five cities. The slope became negative <strong>and</strong><br />
larger, -0.102, but was still not significantly different from zero (r 2 = 0.052, t = 1.016, 19 df).<br />
Neither Figure 7 nor its version corrected to no-snow conditions (not shown) represents a<br />
year’s results accurately, as snow was present only for part of the year. Presumably they do<br />
represent their respective parts of the year well enough, <strong>and</strong> the whole year’s results would be<br />
an appropriate mix of the two parts, weighted according to the fraction of days with snow<br />
cover. Clearly, the regression line slope for a combined result would still not be significantly<br />
different from zero.<br />
The sample size for Figure 7 is the maximum set by the available source of light energy loss<br />
data. The choice of crime data is less constrained, <strong>and</strong> may have a large effect on the<br />
results. 61 Although the 1997 UCR report is still available (FBI 1997), it was not used as it has<br />
no data for Buffalo, Kansas City, Las Vegas, Philadelphia <strong>and</strong> St Louis. These five cities<br />
were in the eight brightest of the 21 <strong>and</strong> their absence would have biased <strong>and</strong> degraded the<br />
results. Given the nature of the hypothesis, it seems quite reasonable to use crime data for a<br />
year (1998) that started ten or eleven months after the satellite measurements of light energy<br />
loss.<br />
61 Other variables may also have an effect. For example, the latitude effect on crime<br />
mentioned in Section 2.4 applies between countries, with countries having a smaller mean<br />
latitude tending to have a higher victimisation percentage V, given by V = 40.7 – 0.4 L, where<br />
L is the mean latitude in degrees (Walker, Wilson, Chappell <strong>and</strong> Weatherburn 1990). During<br />
an initial attempt at Figure 7, a 60% larger but non-significant within-country latitude-effect<br />
regression line slope was found for 1999 UCR data for US Metropolitan Statistical Areas. No<br />
latitude effect was apparent using the 1998 UCR city data obtained subsequently as more<br />
appropriate for Figure 7. Walker et al. related between-country effects in general to the<br />
amount of time individuals spent outdoors in the evening, <strong>and</strong> the latitude effect to an<br />
informal curfew imposed by cold <strong>and</strong> wet conditions at higher latitudes. A present extension<br />
of these reasons is that the degree of encouragement for individuals to be outdoors at night<br />
would presumably also be increased by the extent of artificial lighting, thereby increasing<br />
opportunities for crime.<br />
68