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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

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