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Outdoor Lighting and Crime - Amper

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crime.) Regardless of what the conversion factor might be between the satellite data <strong>and</strong> the<br />

actual mean city illuminances, the crime change represented by the slope of the regression<br />

line in Figure 13 seems improbably large to ascribe wholly to an effect of light over the<br />

lighting range covered. For theproportion of crime reduction in dark conditions to be<br />

realistic, the relatively steep slope could apply over less than one log unit of light reduction,<br />

<strong>and</strong> the observed curve would need to flatten out substantially at lower levels.<br />

Looking at the issue in another way, the upper <strong>and</strong> lower light energy loss values are 11.4 <strong>and</strong><br />

5.07. Eight successive lighting reduction treatments of 11.4/5.07 would reduce the ambient<br />

light by 2.8 log units. If the ambient light level is accepted as low enough to have crime<br />

reduce in the short term to say 25% of its initial value, this would require the crime rate to<br />

reduce by just 16% per treatment, about a quarter of the reduction observed. Possible<br />

explanations for the steep slope include:<br />

• the slope indicates a genuinely steep part of the underlying curve, which must be<br />

generally flatter elsewhere;<br />

• the slope has been exaggerated by some non-lighting factor that has affected the<br />

brighter <strong>and</strong> dimmer cities differentially;<br />

• observed crime levels have not stabilised after recent lighting changes, bearing in<br />

mind the substantial <strong>and</strong> discontinuous growth in outdoor lighting;<br />

• the lighting peaks at the centres of the brighter cities have been underestimated<br />

because of sensor saturation or insufficient spatial resolution; <strong>and</strong><br />

• the large range in light levels within individual cities is masked, possibly<br />

inappropriately, by the use of the arithmetic mean as a single quantity to characterise<br />

the lighting.<br />

There seems to be no way of testing for these possibilities with the information at h<strong>and</strong>. In<br />

the meantime, the lighting, commerce <strong>and</strong> crime hypothesis is supported by the direction of<br />

the result for English cities but the regression equation appears to be unreliably optimistic for<br />

predicting the magnitude of the crime reduction expected with reduced lighting at night.<br />

Regardless of the problems, the observed result is certainly of opposite sign to that implied by<br />

the results of the Farrington <strong>and</strong> Welsh (2002a,b) meta-analysis. This is further independent<br />

evidence that the meta-analysis result does not reflect the real-world relationship between<br />

lighting <strong>and</strong> crime.<br />

It remains to check the USA results. Here the ranges in light energy values are greater: a<br />

factor of 9.80 for Figures 9 <strong>and</strong> 10, or 25.0 if the data are not corrected to no-snow<br />

conditions. 69 Curve E is not readily applicable in the case of Figure 10 because the crime<br />

measure there is relative rather than absolute. Figure 9 is therefore tested instead.<br />

The reduction in crime for one light energy reduction of 9.8 along the regression line in<br />

Figure 9 is a factor of 0.595. Repeating this two more times would represent a lighting<br />

change of nearly three log units <strong>and</strong> a crime reduction to 21%. This does not appear to be an<br />

69 Compared with the light data range in Figure 13 for English cities, the greater range for<br />

USA city light data in Figure 9, although corrected to no-snow conditions, possibly results<br />

from factors such as having a larger sample number, a broader geographic extent, <strong>and</strong> greater<br />

autonomy for the US states in terms of how they light their cities.<br />

81

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