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Soil metal/metalloid concentrations in the Clyde Basin, Scotland, UK: implications for land quality – CORRIGENDUM

Published online by Cambridge University Press:  08 July 2019

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Abstract

Type
Corrigendum
Copyright
Copyright © The Royal Society of Edinburgh 2019 

In the above article (Fordyce, F., Everett, P., Bearcock, J., & Lister, T. (Reference Fordyce, Everett, Bearcock and Lister2019)), Figure 7 was not published in its entirety. The correct figure should be as follows:

Figure 7 Box and whisker plots showing the 10th, 25th, 50th, 75th and 90th percentiles of parameter distributions in topsoil over various land-use types. Abbreviations: AGRI=agriculture (n1303); DL=derelict land (n124); IND=industry (n236); MIN=mining (n33); MOOR=moorland (n151); PARK=recreational (n656); RES=residential open space (n347); RESG=garden/allotment (n254); ROAD=road/rail (n579); SCH=school (n72); WOOD=woodland (n189).

Figure 7 Continued

References

Fordyce, F., Everett, P., Bearcock, J., & Lister, T. (2019). Soil metal/metalloid concentrations in the Clyde Basin, Scotland, UK: Implications for land quality. Earth and Environmental Science Transactions of the Royal Society of Edinburgh, 108(2–3), 191216. doi:10.1017/S1755691018000282Google Scholar
Figure 0

Figure 7Figure 7 Box and whisker plots showing the 10th, 25th, 50th, 75th and 90th percentiles of parameter distributions in topsoil over various land-use types. Abbreviations: AGRI=agriculture (n1303); DL=derelict land (n124); IND=industry (n236); MIN=mining (n33); MOOR=moorland (n151); PARK=recreational (n656); RES=residential open space (n347); RESG=garden/allotment (n254); ROAD=road/rail (n579); SCH=school (n72); WOOD=woodland (n189).

Figure 1

Figure 7Figure 7 Continued