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Skin cancers are a significant public health problem in New Zealand (NZ). In 2009, cutaneous malignant melanoma (melanoma) was the fourth most commonly registered cancer and resulted in 326 deaths.1There are significant sex differences with the male age-standardised registration rate 27% higher than the female rate, and the male death rate more than twice that recorded for females (7.2:3.3 per 100,000).1Non-melanoma skin cancers, estimated to exceed 67,000 cases per annum2 and resulting in 97 reported deaths in 2009,1 are not required to be notified to the New Zealand Cancer Registry, but place a substantial burden on the health system and society.2,3Most skin cancers are potentially preventable through the avoidance of excessive, harmful exposure to ultraviolet radiation (UVR),4 with sunburn associated with increased risk.5For these reasons, national and regional SunSmart health promotion programs have been initiated in NZ since 1988, aimed at increasing public awareness of skin cancer, particularly melanoma, and reducing excessive UVR exposure.6As it was important to evaluate these efforts, the Cancer Society of New Zealand Inc. (CSNZ) and the Health Sponsorship Council (HSC) - now the Health Promotion Agency (HPA), commissioned the Triennial Sun Protection Survey (Sun Survey) series.From 1994 to 2006, cross-sectional surveys were carried out every three years among the NZ urban population. Data collected included sociodemographic information, outdoor sun exposure time, associated activity types and sunburn experience.To date, two peer-reviewed publications have reported descriptive Sun Survey data: one focused on respondents, 15-69 years, in 1994,7 and the other on the youngest age group, 12-17 years, in 1997.8The aim of the present paper is to extend the knowledge gained from these two reports by including data for three additional summers (1999/00, 2002/03 and 2005/06). As previously, outdoor sun exposure (activity type and duration) and sunburn experience for the recall weekends will be described, by sex, age group and skin type.Method Sample selection Respondents, 15-69 years inclusive, were residents of five surveyed metropolitan areas (Auckland, Wellington, Hamilton, Christchurch, and Dunedin) which represented approximately 55% of the total NZ population in the 2006 Census. Data were collected during summer, based on procedures used for a survey administered in Victoria, Australia.9 Participants were recruited either from randomly selected households using random digit dialling in the predetermined areas (1994 and 1997), or through telematching from electoral rolls, 1999-2006. Overall, data usable for analysis were obtained from 6,195 respondents with the breakdown by year as follows: 1994 n=1,243, 1997 n=1,188, 1999/00 n=1,250, 2002/03 n=1,250, and 2005/06 n=1,264. Given a primary prevention focus, interview protocols prioritised younger household members, but a quota system ensured approximately equal numbers by sex and city of residence. Procedures and instrument Data were obtained from computer-assisted telephone interviews (CATI), usually conducted on either the Monday or Tuesday evening, following selected survey weekends. Meteorological data were used to select appropriate survey weekends, with the main criterion being that the weather had been fine enough for potentially harmful sun exposure to have occurred.7 TNS was the contracted data collection agency in 2006, 2003 (then known as NFO New Zealand), and 2000 (then known as CM Research). The MRL Research group (1997) and Roy Morgan Research (1994) were contracted for previous survey years. The surveys used much common questionnaire content to facilitate comparisons across time. Sociodemographic information sought included sex, age and self-defined ethnicity (prioritised according to Level 1, the highest, of the NZ Ministry of Health ethnicity and data protocols).10 Self-reported skin type was based on a modified Fitzpatrick classification of skin sun-reaction: Type I (always burn, never tan), Type II (usually burn, tan with difficulty), Type III (sometimes burn, tan moderately), Type IV (rarely burn, tan easily).11 The exposure days selected varied by year. Data for both Saturdays and Sundays were recorded in 1994, however, due to possible respondent fatigue from survey length and cost issues, Sunday was preferentially selected in 1997 (unless the respondent was only outdoors and sunburnt on Saturday) so 1994 data were treated equivalently. Thereafter the recall day was selected using a standardised procedure.12 Information on sunburn (defined as any amount of reddening of the skin after being in the sun) and the body areas affected were recorded. Those who had spent longer than 15 minutes outdoors on the exposure day, 11am-4pm during daylight savings time (NZ Standard Time +1 hour), provided information on the type and duration of outdoor activities. Activities were classified slightly differently in 1994,7 therefore it was necessary to reclassify and collapse categories, to permit comparisons by year. The six activity categories formed were active recreation (e.g. sports), passive recreation (e.g. reading), water-based recreation (e.g. swimming), paid work, unpaid work (e.g. gardening), or unspecified recreation. The duration of the main outdoor activity (in minutes) was collected from respondents estimates. Analyses Chi-squared tests for association were used to identify significant between-group differences in sunburn patterns, including between years, sexes, age groups, skin sensitivities, and activities. Linear regression models were used to examine associations with duration outdoors. All data were analysed without sampling or post-stratification weights and using SAS 9.1.313 and Stata v12.1 software,14 with two-tailed tests used for the regression models. Statistical significance was determined by p<0.05 in all cases. Ethical approval Participation was taken as informed consent. Participants had previously been notified of the survey by mail from the commissioned market research agency. The proposed project analyses, reported here, were reviewed and ethical approval granted at the Departmental level, following University of Otago Human Ethics Committee procedures. Results Respondent characteristics Overall, 68.8% (n=4,264/6,195) of respondents reported meeting the outdoor status criterion (\u226515 minutes outdoors, 10am-4pm on recall weekend) (Table 1). Table 1. Respondent characteristics by outdoor status, 1994-2006 inclusive Variable All respondents n=6,195 Outdoor respondents n=4,264 P value n % n % of all outdoors % within category outdoors Sex Male Female 3,084 3,111 49.8 50.2 2,273 1,991 53.3 46.7 73.7 64.0 <0.001 Age group (years) 15-19 20-29 30-39 40-49 50-59 60-69 756 1,270 1,416 1,109 999 645 12.2 20.5 22.9 17.9 16.1 10.4 551 907 1,002 748 658 398 12.9 21.3 23.5 17.5 15.4 9.3 72.9 71.4 70.8 67.4 65.9 61.7 <0.001 Skin type* I II III IV Missing data 1,494 3,432 1,109 84 76 24.4 56.1 18.1 1.4 1,014 2,404 773 41 32 23.8 56.4 18.1 1.0 67.9 70.0 69.7 48.8 <0.001 City Auckland Hamilton Wellington Christchurch Dunedin 1,254 1,237 1,230 1,242 1,232 20.2 20.0 19.9 20.1 19.9 891 876 857 808 832 20.9 20.5 20.1 19.0 19.5 71.1 70.8 69.7 65.1 67.5 0.005 Priority ethnicity NZ European M\u0101ori Pacific Asian All other Missing data 5,326 405 123 231 55 55 86.7 6.6 2.0 3.8 0.9 3,676 288 79 140 42 39 86.2 4.6 1.9 3.3 1.0 69.0 71.1 64.2 60.6 76.4 0.026 Survey year 1994 1997 1999/2000 2002/2003 2005/2006 1243 1188 1250 1250 1264 20.1 19.2 20.2 20.2 20.4 854 921 802 808 879 20.0 68.7 <0.001 21.6 77.5 18.8 64.2 18.9 64.6 20.6 69.5 * Fitzpatrick sun-sensitivity scale, modified. Percentages may not total 100% due to rounding. All respondent characteristics were statistically significantly associated with being outdoors, with males, younger people, those with skin types I-III, Maori and those responding in 1997 more likely to report being outside than females, older people, those with skin type IV, Pacific and Asian respondents and those responding in other survey years. The following results are based on the 4,264 respondents who reported \u226515 minutes of outdoor activity, 11am-4pm, during the previous weekend. Sub-group analyses by ethnicity, while of potential interest, were not undertaken because of relatively small numbers in some categories. Sunburn experience Overall, 20.7% (n=882) of 4,259 outdoor respondents with valid datareported sunburn on the recall day (Table 2). Overall, sunburn experience was more common among males, younger respondents and those with vulnerable skin types than females, older respondents and those with less vulnerable skin types. Sunburn rates varied by year between 17.0% and 23.9%, but without a consistent pattern despite being somewhat higher in the most recent year than in the baseline survey. Table 2. Sunburn experience by sex, age and skin type* All Sunburned P value n %

Summary

Abstract

Aim

To describe summer weekend sun exposure and sunburn experience, 1994-2006, among urban New Zealanders (15-69 years) by sex, age group, skin type and outdoor activity type.

Method

A series of five telephone surveys undertaken in the summers of 1994, 1997, 1999-2000, 2002-3 and 2005-6 provided a sample of 6,195 respondents with usable data from five major cities (Auckland, Hamilton, Wellington, Christchurch and Dunedin). Respondents were administered a Computer Assisted Telephone Interview (CATI) questionnaire which sought sociodemographic information, sun exposure, and sunburn experience during the most recent weekend.

Results

Overall, 69% of the sample had spent at least 15 minutes outdoors between 11am and 4pm. Weekend sunburn was reported by 21%, and was more common among males, young adults and those with highly sun-sensitive skin than females, older adults and those with less sensitive skin. The head/face/neck was the body area most frequently and severely sunburned. Sunburn was associated with greater time spent outdoors and occurred most frequently during water-based (29%) and passive recreational activities (25%) and paid work (23%).

Conclusion

Sun protection strategies could usefully be targeted not only towards at-risk population groups, but also towards those activities and contexts most strongly associated with potentially harmful sun exposure.

Author Information

Geraldine (Geri) F. H. McLeod, Research Fellow, Christchurch Health and Development Stud, Department of Psychological Medicine, University of Otago, Christchurch; Anthony I Reeder,* Research Associate Professor, Cancer Society of New Zealand Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Andrew R. Gray, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Rob McGee, Professor, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin

Acknowledgements

The data analysed in this research were collected by contractors to the owners of the data, the Health Sponsorship Council (HSC) (now the Health Promotion Agency), SunSmart programme, and the Cancer Society of New Zealand Inc (CSNZ).Data were collected by Roy Morgan Research Centre Pty Ltd. (1994), MRL Research Group (1997), and TNS New Zealand Ltd., made up of CM Research and NFO NZ (1999/00-2005/06). The data were analysed by the authors. Geri McLeod received support from the Health Sponsorship Council SunSmart PhD Scholarship. Associate Professor Reeder and the Cancer Society Social & Behavioural Research Unit receive support from the CSNZ Inc. and the University of Otago. Professor McGee and Mr Gray receive support from the University of Otago.The authors also thank Nathalie Huston and Margaret Henry for providing research support services, Helen Glasgow for initial work developing the survey, and Dr Simon Horsburgh for data management assistance.The Cancer Society Social & Behavioural Research Units role was primarily limited to the provision of advice about the more recent survey waves, data analysis and reporting.

Correspondence

Associate Professor Anthony Reeder, Cancer Society Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, PO Box 913, Dunedin 9054, New Zealand. Fax: +64 3 479 7298;

Correspondence Email

tony.reeder@otago.ac.nz

Competing Interests

None identified.

Ministry of Health. Cancer: New Registrations and Deaths 2009. Wellington 2012.O'Dea D. The Costs of Skin Cancer to New Zealand. Wellington: Wellington School of Medicine, 2009.Pearce D, Williford PM, Blakrishnan R, Feldman SR. Economics of skin cancer. In: Nouri K, editor. Skin Cancer: New York: McGraw Hill; 2008, p679-85.Armstrong B. How sun exposure causes skin cancer: an epidemiological perspective. In: Hill D, Elwood JM, English DR, editors. Prevention of Skin Cancer. Dordrecht: Kluwer Academic Publishers; 2004, p89-116.Green A, Siskind V, Bain C, Alexander J. Sunburn and malignant melanoma. Br J Cancer. 1985;51:393-397.Watts C, Reeder AI, Glasgow H. A cover-up story: the Cancer Society Melanoma Prevention Programme. UV radiation and its effects - an update. Wellington: Royal Society of New Zealand; 2002, p83.McGee R, Williams S, Cox B, Elwood M, Bulliard J-L. A community survey of sun exposure, sunburn and sun protection. N Z Med J. 1995;108:508-10.Richards R, McGee R, Knight RG. Sunburn and sun protection among New Zealand adolescents over a summer weekend. Aust NZ J Publ Health. 2001;25:352-54.Borland R, Hill D, Noy S. Being SunSmart: changes in community awareness and reported behaviour following a primary prevention program for skin cancer control. Behav Change. 1990;7:126-35.Ministry of Health. Ethnicity data protocols for the health and disability sector. Wellington: Ministry of Health; 2004.Fitzpatrick TB. The validity and practicality of sun-reactive skin types I through VI. Arch Dermatol. 1988;124:869-71.Taylor Nelson Sofres Group (TNS). Sun Protection Market Research Report. Report 1301934 prepared for Health Sponsorship Council and Cancer Society of NZ; Wellington: 2006.SAS System for XP_PRO [computer program]. Version v 9.1.3 2000-2003.Stata statistical software: Release 12, [computer program]. Version Release 12.0 College Station, Texas: StataCorp LP; 2011.http://www.stata.com/support/faqs/resources/citing-software-documentation-faqsDobbinson S, Wakefield M, Hill D, et al. Prevalence and determinates of Australian adolescents' and adults' weekend sun protection and sunburn, summer 2003-2004. J Am Acad Dermatol 2008;59:602-14Volkov A, Dobbinson S, Wakefield M, Slevin T. Seven-year trends in sun protection and sunburn among Australian adolescents and adults. Aust NZ J Publ Health 2013;37:63-9.Bulliard JL. Site-specific risk of cutaneous malignant melanoma and pattern of sun exposure in New Zealand. Int J Cancer. 2000;85:627-32.Hill D, White V, Marks R et al. Melanoma prevention: behavioural and nonbehavioral factors in sunburn among an Australian urban population. Prev Med. 1992;21:654-69.Horsburgh-McLeod GF, Gray AR, Reeder AI, McGee R. Sunburn in a New Zealand Urban Population, 1994-2006. Australasian Epidemiologist. Apr 2010;17(1):40-46.Dunn J, Lynch B, Dip G. Climatic conditions and the reporting of sun-protective behavior survey data: a brief report. Am J Health Promot. 2001;15:241-43.Broadstock M. Sun protection at the cricket. Med J Aust. 1991; 154:430.Hammond VA, Reeder AI, Gray A, Bell M. Are workers or their workplaces the key to occupational sun protection? Health Promotion J. Aust. 2008;19:97-101.Reeder AI, Gray A, McCool JP. Occupational sun protection: workplace culture, equipment provision and outdoor workers' characteristics. J Occup Health. 2013;in press.McLeod G. Sunburn in a New Zealand urban population, 1994-2006 [PhD]. Dunedin: Department of Preventive & Social Medicine, University of Otago; 2012.International Agency for Research on Cancer. Globocan 2008. Cancer incidence, mortality and prevalence worldwide. Lyons: IARC 2012; http://globocan.iarc.fr/.

For the PDF of this article,
contact nzmj@nzma.org.nz

View Article PDF

Skin cancers are a significant public health problem in New Zealand (NZ). In 2009, cutaneous malignant melanoma (melanoma) was the fourth most commonly registered cancer and resulted in 326 deaths.1There are significant sex differences with the male age-standardised registration rate 27% higher than the female rate, and the male death rate more than twice that recorded for females (7.2:3.3 per 100,000).1Non-melanoma skin cancers, estimated to exceed 67,000 cases per annum2 and resulting in 97 reported deaths in 2009,1 are not required to be notified to the New Zealand Cancer Registry, but place a substantial burden on the health system and society.2,3Most skin cancers are potentially preventable through the avoidance of excessive, harmful exposure to ultraviolet radiation (UVR),4 with sunburn associated with increased risk.5For these reasons, national and regional SunSmart health promotion programs have been initiated in NZ since 1988, aimed at increasing public awareness of skin cancer, particularly melanoma, and reducing excessive UVR exposure.6As it was important to evaluate these efforts, the Cancer Society of New Zealand Inc. (CSNZ) and the Health Sponsorship Council (HSC) - now the Health Promotion Agency (HPA), commissioned the Triennial Sun Protection Survey (Sun Survey) series.From 1994 to 2006, cross-sectional surveys were carried out every three years among the NZ urban population. Data collected included sociodemographic information, outdoor sun exposure time, associated activity types and sunburn experience.To date, two peer-reviewed publications have reported descriptive Sun Survey data: one focused on respondents, 15-69 years, in 1994,7 and the other on the youngest age group, 12-17 years, in 1997.8The aim of the present paper is to extend the knowledge gained from these two reports by including data for three additional summers (1999/00, 2002/03 and 2005/06). As previously, outdoor sun exposure (activity type and duration) and sunburn experience for the recall weekends will be described, by sex, age group and skin type.Method Sample selection Respondents, 15-69 years inclusive, were residents of five surveyed metropolitan areas (Auckland, Wellington, Hamilton, Christchurch, and Dunedin) which represented approximately 55% of the total NZ population in the 2006 Census. Data were collected during summer, based on procedures used for a survey administered in Victoria, Australia.9 Participants were recruited either from randomly selected households using random digit dialling in the predetermined areas (1994 and 1997), or through telematching from electoral rolls, 1999-2006. Overall, data usable for analysis were obtained from 6,195 respondents with the breakdown by year as follows: 1994 n=1,243, 1997 n=1,188, 1999/00 n=1,250, 2002/03 n=1,250, and 2005/06 n=1,264. Given a primary prevention focus, interview protocols prioritised younger household members, but a quota system ensured approximately equal numbers by sex and city of residence. Procedures and instrument Data were obtained from computer-assisted telephone interviews (CATI), usually conducted on either the Monday or Tuesday evening, following selected survey weekends. Meteorological data were used to select appropriate survey weekends, with the main criterion being that the weather had been fine enough for potentially harmful sun exposure to have occurred.7 TNS was the contracted data collection agency in 2006, 2003 (then known as NFO New Zealand), and 2000 (then known as CM Research). The MRL Research group (1997) and Roy Morgan Research (1994) were contracted for previous survey years. The surveys used much common questionnaire content to facilitate comparisons across time. Sociodemographic information sought included sex, age and self-defined ethnicity (prioritised according to Level 1, the highest, of the NZ Ministry of Health ethnicity and data protocols).10 Self-reported skin type was based on a modified Fitzpatrick classification of skin sun-reaction: Type I (always burn, never tan), Type II (usually burn, tan with difficulty), Type III (sometimes burn, tan moderately), Type IV (rarely burn, tan easily).11 The exposure days selected varied by year. Data for both Saturdays and Sundays were recorded in 1994, however, due to possible respondent fatigue from survey length and cost issues, Sunday was preferentially selected in 1997 (unless the respondent was only outdoors and sunburnt on Saturday) so 1994 data were treated equivalently. Thereafter the recall day was selected using a standardised procedure.12 Information on sunburn (defined as any amount of reddening of the skin after being in the sun) and the body areas affected were recorded. Those who had spent longer than 15 minutes outdoors on the exposure day, 11am-4pm during daylight savings time (NZ Standard Time +1 hour), provided information on the type and duration of outdoor activities. Activities were classified slightly differently in 1994,7 therefore it was necessary to reclassify and collapse categories, to permit comparisons by year. The six activity categories formed were active recreation (e.g. sports), passive recreation (e.g. reading), water-based recreation (e.g. swimming), paid work, unpaid work (e.g. gardening), or unspecified recreation. The duration of the main outdoor activity (in minutes) was collected from respondents estimates. Analyses Chi-squared tests for association were used to identify significant between-group differences in sunburn patterns, including between years, sexes, age groups, skin sensitivities, and activities. Linear regression models were used to examine associations with duration outdoors. All data were analysed without sampling or post-stratification weights and using SAS 9.1.313 and Stata v12.1 software,14 with two-tailed tests used for the regression models. Statistical significance was determined by p<0.05 in all cases. Ethical approval Participation was taken as informed consent. Participants had previously been notified of the survey by mail from the commissioned market research agency. The proposed project analyses, reported here, were reviewed and ethical approval granted at the Departmental level, following University of Otago Human Ethics Committee procedures. Results Respondent characteristics Overall, 68.8% (n=4,264/6,195) of respondents reported meeting the outdoor status criterion (\u226515 minutes outdoors, 10am-4pm on recall weekend) (Table 1). Table 1. Respondent characteristics by outdoor status, 1994-2006 inclusive Variable All respondents n=6,195 Outdoor respondents n=4,264 P value n % n % of all outdoors % within category outdoors Sex Male Female 3,084 3,111 49.8 50.2 2,273 1,991 53.3 46.7 73.7 64.0 <0.001 Age group (years) 15-19 20-29 30-39 40-49 50-59 60-69 756 1,270 1,416 1,109 999 645 12.2 20.5 22.9 17.9 16.1 10.4 551 907 1,002 748 658 398 12.9 21.3 23.5 17.5 15.4 9.3 72.9 71.4 70.8 67.4 65.9 61.7 <0.001 Skin type* I II III IV Missing data 1,494 3,432 1,109 84 76 24.4 56.1 18.1 1.4 1,014 2,404 773 41 32 23.8 56.4 18.1 1.0 67.9 70.0 69.7 48.8 <0.001 City Auckland Hamilton Wellington Christchurch Dunedin 1,254 1,237 1,230 1,242 1,232 20.2 20.0 19.9 20.1 19.9 891 876 857 808 832 20.9 20.5 20.1 19.0 19.5 71.1 70.8 69.7 65.1 67.5 0.005 Priority ethnicity NZ European M\u0101ori Pacific Asian All other Missing data 5,326 405 123 231 55 55 86.7 6.6 2.0 3.8 0.9 3,676 288 79 140 42 39 86.2 4.6 1.9 3.3 1.0 69.0 71.1 64.2 60.6 76.4 0.026 Survey year 1994 1997 1999/2000 2002/2003 2005/2006 1243 1188 1250 1250 1264 20.1 19.2 20.2 20.2 20.4 854 921 802 808 879 20.0 68.7 <0.001 21.6 77.5 18.8 64.2 18.9 64.6 20.6 69.5 * Fitzpatrick sun-sensitivity scale, modified. Percentages may not total 100% due to rounding. All respondent characteristics were statistically significantly associated with being outdoors, with males, younger people, those with skin types I-III, Maori and those responding in 1997 more likely to report being outside than females, older people, those with skin type IV, Pacific and Asian respondents and those responding in other survey years. The following results are based on the 4,264 respondents who reported \u226515 minutes of outdoor activity, 11am-4pm, during the previous weekend. Sub-group analyses by ethnicity, while of potential interest, were not undertaken because of relatively small numbers in some categories. Sunburn experience Overall, 20.7% (n=882) of 4,259 outdoor respondents with valid datareported sunburn on the recall day (Table 2). Overall, sunburn experience was more common among males, younger respondents and those with vulnerable skin types than females, older respondents and those with less vulnerable skin types. Sunburn rates varied by year between 17.0% and 23.9%, but without a consistent pattern despite being somewhat higher in the most recent year than in the baseline survey. Table 2. Sunburn experience by sex, age and skin type* All Sunburned P value n %

Summary

Abstract

Aim

To describe summer weekend sun exposure and sunburn experience, 1994-2006, among urban New Zealanders (15-69 years) by sex, age group, skin type and outdoor activity type.

Method

A series of five telephone surveys undertaken in the summers of 1994, 1997, 1999-2000, 2002-3 and 2005-6 provided a sample of 6,195 respondents with usable data from five major cities (Auckland, Hamilton, Wellington, Christchurch and Dunedin). Respondents were administered a Computer Assisted Telephone Interview (CATI) questionnaire which sought sociodemographic information, sun exposure, and sunburn experience during the most recent weekend.

Results

Overall, 69% of the sample had spent at least 15 minutes outdoors between 11am and 4pm. Weekend sunburn was reported by 21%, and was more common among males, young adults and those with highly sun-sensitive skin than females, older adults and those with less sensitive skin. The head/face/neck was the body area most frequently and severely sunburned. Sunburn was associated with greater time spent outdoors and occurred most frequently during water-based (29%) and passive recreational activities (25%) and paid work (23%).

Conclusion

Sun protection strategies could usefully be targeted not only towards at-risk population groups, but also towards those activities and contexts most strongly associated with potentially harmful sun exposure.

Author Information

Geraldine (Geri) F. H. McLeod, Research Fellow, Christchurch Health and Development Stud, Department of Psychological Medicine, University of Otago, Christchurch; Anthony I Reeder,* Research Associate Professor, Cancer Society of New Zealand Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Andrew R. Gray, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Rob McGee, Professor, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin

Acknowledgements

The data analysed in this research were collected by contractors to the owners of the data, the Health Sponsorship Council (HSC) (now the Health Promotion Agency), SunSmart programme, and the Cancer Society of New Zealand Inc (CSNZ).Data were collected by Roy Morgan Research Centre Pty Ltd. (1994), MRL Research Group (1997), and TNS New Zealand Ltd., made up of CM Research and NFO NZ (1999/00-2005/06). The data were analysed by the authors. Geri McLeod received support from the Health Sponsorship Council SunSmart PhD Scholarship. Associate Professor Reeder and the Cancer Society Social & Behavioural Research Unit receive support from the CSNZ Inc. and the University of Otago. Professor McGee and Mr Gray receive support from the University of Otago.The authors also thank Nathalie Huston and Margaret Henry for providing research support services, Helen Glasgow for initial work developing the survey, and Dr Simon Horsburgh for data management assistance.The Cancer Society Social & Behavioural Research Units role was primarily limited to the provision of advice about the more recent survey waves, data analysis and reporting.

Correspondence

Associate Professor Anthony Reeder, Cancer Society Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, PO Box 913, Dunedin 9054, New Zealand. Fax: +64 3 479 7298;

Correspondence Email

tony.reeder@otago.ac.nz

Competing Interests

None identified.

Ministry of Health. Cancer: New Registrations and Deaths 2009. Wellington 2012.O'Dea D. The Costs of Skin Cancer to New Zealand. Wellington: Wellington School of Medicine, 2009.Pearce D, Williford PM, Blakrishnan R, Feldman SR. Economics of skin cancer. In: Nouri K, editor. Skin Cancer: New York: McGraw Hill; 2008, p679-85.Armstrong B. How sun exposure causes skin cancer: an epidemiological perspective. In: Hill D, Elwood JM, English DR, editors. Prevention of Skin Cancer. Dordrecht: Kluwer Academic Publishers; 2004, p89-116.Green A, Siskind V, Bain C, Alexander J. Sunburn and malignant melanoma. Br J Cancer. 1985;51:393-397.Watts C, Reeder AI, Glasgow H. A cover-up story: the Cancer Society Melanoma Prevention Programme. UV radiation and its effects - an update. Wellington: Royal Society of New Zealand; 2002, p83.McGee R, Williams S, Cox B, Elwood M, Bulliard J-L. A community survey of sun exposure, sunburn and sun protection. N Z Med J. 1995;108:508-10.Richards R, McGee R, Knight RG. Sunburn and sun protection among New Zealand adolescents over a summer weekend. Aust NZ J Publ Health. 2001;25:352-54.Borland R, Hill D, Noy S. Being SunSmart: changes in community awareness and reported behaviour following a primary prevention program for skin cancer control. Behav Change. 1990;7:126-35.Ministry of Health. Ethnicity data protocols for the health and disability sector. Wellington: Ministry of Health; 2004.Fitzpatrick TB. The validity and practicality of sun-reactive skin types I through VI. Arch Dermatol. 1988;124:869-71.Taylor Nelson Sofres Group (TNS). Sun Protection Market Research Report. Report 1301934 prepared for Health Sponsorship Council and Cancer Society of NZ; Wellington: 2006.SAS System for XP_PRO [computer program]. Version v 9.1.3 2000-2003.Stata statistical software: Release 12, [computer program]. Version Release 12.0 College Station, Texas: StataCorp LP; 2011.http://www.stata.com/support/faqs/resources/citing-software-documentation-faqsDobbinson S, Wakefield M, Hill D, et al. Prevalence and determinates of Australian adolescents' and adults' weekend sun protection and sunburn, summer 2003-2004. J Am Acad Dermatol 2008;59:602-14Volkov A, Dobbinson S, Wakefield M, Slevin T. Seven-year trends in sun protection and sunburn among Australian adolescents and adults. Aust NZ J Publ Health 2013;37:63-9.Bulliard JL. Site-specific risk of cutaneous malignant melanoma and pattern of sun exposure in New Zealand. Int J Cancer. 2000;85:627-32.Hill D, White V, Marks R et al. Melanoma prevention: behavioural and nonbehavioral factors in sunburn among an Australian urban population. Prev Med. 1992;21:654-69.Horsburgh-McLeod GF, Gray AR, Reeder AI, McGee R. Sunburn in a New Zealand Urban Population, 1994-2006. Australasian Epidemiologist. Apr 2010;17(1):40-46.Dunn J, Lynch B, Dip G. Climatic conditions and the reporting of sun-protective behavior survey data: a brief report. Am J Health Promot. 2001;15:241-43.Broadstock M. Sun protection at the cricket. Med J Aust. 1991; 154:430.Hammond VA, Reeder AI, Gray A, Bell M. Are workers or their workplaces the key to occupational sun protection? Health Promotion J. Aust. 2008;19:97-101.Reeder AI, Gray A, McCool JP. Occupational sun protection: workplace culture, equipment provision and outdoor workers' characteristics. J Occup Health. 2013;in press.McLeod G. Sunburn in a New Zealand urban population, 1994-2006 [PhD]. Dunedin: Department of Preventive & Social Medicine, University of Otago; 2012.International Agency for Research on Cancer. Globocan 2008. Cancer incidence, mortality and prevalence worldwide. Lyons: IARC 2012; http://globocan.iarc.fr/.

For the PDF of this article,
contact nzmj@nzma.org.nz

View Article PDF

Skin cancers are a significant public health problem in New Zealand (NZ). In 2009, cutaneous malignant melanoma (melanoma) was the fourth most commonly registered cancer and resulted in 326 deaths.1There are significant sex differences with the male age-standardised registration rate 27% higher than the female rate, and the male death rate more than twice that recorded for females (7.2:3.3 per 100,000).1Non-melanoma skin cancers, estimated to exceed 67,000 cases per annum2 and resulting in 97 reported deaths in 2009,1 are not required to be notified to the New Zealand Cancer Registry, but place a substantial burden on the health system and society.2,3Most skin cancers are potentially preventable through the avoidance of excessive, harmful exposure to ultraviolet radiation (UVR),4 with sunburn associated with increased risk.5For these reasons, national and regional SunSmart health promotion programs have been initiated in NZ since 1988, aimed at increasing public awareness of skin cancer, particularly melanoma, and reducing excessive UVR exposure.6As it was important to evaluate these efforts, the Cancer Society of New Zealand Inc. (CSNZ) and the Health Sponsorship Council (HSC) - now the Health Promotion Agency (HPA), commissioned the Triennial Sun Protection Survey (Sun Survey) series.From 1994 to 2006, cross-sectional surveys were carried out every three years among the NZ urban population. Data collected included sociodemographic information, outdoor sun exposure time, associated activity types and sunburn experience.To date, two peer-reviewed publications have reported descriptive Sun Survey data: one focused on respondents, 15-69 years, in 1994,7 and the other on the youngest age group, 12-17 years, in 1997.8The aim of the present paper is to extend the knowledge gained from these two reports by including data for three additional summers (1999/00, 2002/03 and 2005/06). As previously, outdoor sun exposure (activity type and duration) and sunburn experience for the recall weekends will be described, by sex, age group and skin type.Method Sample selection Respondents, 15-69 years inclusive, were residents of five surveyed metropolitan areas (Auckland, Wellington, Hamilton, Christchurch, and Dunedin) which represented approximately 55% of the total NZ population in the 2006 Census. Data were collected during summer, based on procedures used for a survey administered in Victoria, Australia.9 Participants were recruited either from randomly selected households using random digit dialling in the predetermined areas (1994 and 1997), or through telematching from electoral rolls, 1999-2006. Overall, data usable for analysis were obtained from 6,195 respondents with the breakdown by year as follows: 1994 n=1,243, 1997 n=1,188, 1999/00 n=1,250, 2002/03 n=1,250, and 2005/06 n=1,264. Given a primary prevention focus, interview protocols prioritised younger household members, but a quota system ensured approximately equal numbers by sex and city of residence. Procedures and instrument Data were obtained from computer-assisted telephone interviews (CATI), usually conducted on either the Monday or Tuesday evening, following selected survey weekends. Meteorological data were used to select appropriate survey weekends, with the main criterion being that the weather had been fine enough for potentially harmful sun exposure to have occurred.7 TNS was the contracted data collection agency in 2006, 2003 (then known as NFO New Zealand), and 2000 (then known as CM Research). The MRL Research group (1997) and Roy Morgan Research (1994) were contracted for previous survey years. The surveys used much common questionnaire content to facilitate comparisons across time. Sociodemographic information sought included sex, age and self-defined ethnicity (prioritised according to Level 1, the highest, of the NZ Ministry of Health ethnicity and data protocols).10 Self-reported skin type was based on a modified Fitzpatrick classification of skin sun-reaction: Type I (always burn, never tan), Type II (usually burn, tan with difficulty), Type III (sometimes burn, tan moderately), Type IV (rarely burn, tan easily).11 The exposure days selected varied by year. Data for both Saturdays and Sundays were recorded in 1994, however, due to possible respondent fatigue from survey length and cost issues, Sunday was preferentially selected in 1997 (unless the respondent was only outdoors and sunburnt on Saturday) so 1994 data were treated equivalently. Thereafter the recall day was selected using a standardised procedure.12 Information on sunburn (defined as any amount of reddening of the skin after being in the sun) and the body areas affected were recorded. Those who had spent longer than 15 minutes outdoors on the exposure day, 11am-4pm during daylight savings time (NZ Standard Time +1 hour), provided information on the type and duration of outdoor activities. Activities were classified slightly differently in 1994,7 therefore it was necessary to reclassify and collapse categories, to permit comparisons by year. The six activity categories formed were active recreation (e.g. sports), passive recreation (e.g. reading), water-based recreation (e.g. swimming), paid work, unpaid work (e.g. gardening), or unspecified recreation. The duration of the main outdoor activity (in minutes) was collected from respondents estimates. Analyses Chi-squared tests for association were used to identify significant between-group differences in sunburn patterns, including between years, sexes, age groups, skin sensitivities, and activities. Linear regression models were used to examine associations with duration outdoors. All data were analysed without sampling or post-stratification weights and using SAS 9.1.313 and Stata v12.1 software,14 with two-tailed tests used for the regression models. Statistical significance was determined by p<0.05 in all cases. Ethical approval Participation was taken as informed consent. Participants had previously been notified of the survey by mail from the commissioned market research agency. The proposed project analyses, reported here, were reviewed and ethical approval granted at the Departmental level, following University of Otago Human Ethics Committee procedures. Results Respondent characteristics Overall, 68.8% (n=4,264/6,195) of respondents reported meeting the outdoor status criterion (\u226515 minutes outdoors, 10am-4pm on recall weekend) (Table 1). Table 1. Respondent characteristics by outdoor status, 1994-2006 inclusive Variable All respondents n=6,195 Outdoor respondents n=4,264 P value n % n % of all outdoors % within category outdoors Sex Male Female 3,084 3,111 49.8 50.2 2,273 1,991 53.3 46.7 73.7 64.0 <0.001 Age group (years) 15-19 20-29 30-39 40-49 50-59 60-69 756 1,270 1,416 1,109 999 645 12.2 20.5 22.9 17.9 16.1 10.4 551 907 1,002 748 658 398 12.9 21.3 23.5 17.5 15.4 9.3 72.9 71.4 70.8 67.4 65.9 61.7 <0.001 Skin type* I II III IV Missing data 1,494 3,432 1,109 84 76 24.4 56.1 18.1 1.4 1,014 2,404 773 41 32 23.8 56.4 18.1 1.0 67.9 70.0 69.7 48.8 <0.001 City Auckland Hamilton Wellington Christchurch Dunedin 1,254 1,237 1,230 1,242 1,232 20.2 20.0 19.9 20.1 19.9 891 876 857 808 832 20.9 20.5 20.1 19.0 19.5 71.1 70.8 69.7 65.1 67.5 0.005 Priority ethnicity NZ European M\u0101ori Pacific Asian All other Missing data 5,326 405 123 231 55 55 86.7 6.6 2.0 3.8 0.9 3,676 288 79 140 42 39 86.2 4.6 1.9 3.3 1.0 69.0 71.1 64.2 60.6 76.4 0.026 Survey year 1994 1997 1999/2000 2002/2003 2005/2006 1243 1188 1250 1250 1264 20.1 19.2 20.2 20.2 20.4 854 921 802 808 879 20.0 68.7 <0.001 21.6 77.5 18.8 64.2 18.9 64.6 20.6 69.5 * Fitzpatrick sun-sensitivity scale, modified. Percentages may not total 100% due to rounding. All respondent characteristics were statistically significantly associated with being outdoors, with males, younger people, those with skin types I-III, Maori and those responding in 1997 more likely to report being outside than females, older people, those with skin type IV, Pacific and Asian respondents and those responding in other survey years. The following results are based on the 4,264 respondents who reported \u226515 minutes of outdoor activity, 11am-4pm, during the previous weekend. Sub-group analyses by ethnicity, while of potential interest, were not undertaken because of relatively small numbers in some categories. Sunburn experience Overall, 20.7% (n=882) of 4,259 outdoor respondents with valid datareported sunburn on the recall day (Table 2). Overall, sunburn experience was more common among males, younger respondents and those with vulnerable skin types than females, older respondents and those with less vulnerable skin types. Sunburn rates varied by year between 17.0% and 23.9%, but without a consistent pattern despite being somewhat higher in the most recent year than in the baseline survey. Table 2. Sunburn experience by sex, age and skin type* All Sunburned P value n %

Summary

Abstract

Aim

To describe summer weekend sun exposure and sunburn experience, 1994-2006, among urban New Zealanders (15-69 years) by sex, age group, skin type and outdoor activity type.

Method

A series of five telephone surveys undertaken in the summers of 1994, 1997, 1999-2000, 2002-3 and 2005-6 provided a sample of 6,195 respondents with usable data from five major cities (Auckland, Hamilton, Wellington, Christchurch and Dunedin). Respondents were administered a Computer Assisted Telephone Interview (CATI) questionnaire which sought sociodemographic information, sun exposure, and sunburn experience during the most recent weekend.

Results

Overall, 69% of the sample had spent at least 15 minutes outdoors between 11am and 4pm. Weekend sunburn was reported by 21%, and was more common among males, young adults and those with highly sun-sensitive skin than females, older adults and those with less sensitive skin. The head/face/neck was the body area most frequently and severely sunburned. Sunburn was associated with greater time spent outdoors and occurred most frequently during water-based (29%) and passive recreational activities (25%) and paid work (23%).

Conclusion

Sun protection strategies could usefully be targeted not only towards at-risk population groups, but also towards those activities and contexts most strongly associated with potentially harmful sun exposure.

Author Information

Geraldine (Geri) F. H. McLeod, Research Fellow, Christchurch Health and Development Stud, Department of Psychological Medicine, University of Otago, Christchurch; Anthony I Reeder,* Research Associate Professor, Cancer Society of New Zealand Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Andrew R. Gray, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Rob McGee, Professor, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin

Acknowledgements

The data analysed in this research were collected by contractors to the owners of the data, the Health Sponsorship Council (HSC) (now the Health Promotion Agency), SunSmart programme, and the Cancer Society of New Zealand Inc (CSNZ).Data were collected by Roy Morgan Research Centre Pty Ltd. (1994), MRL Research Group (1997), and TNS New Zealand Ltd., made up of CM Research and NFO NZ (1999/00-2005/06). The data were analysed by the authors. Geri McLeod received support from the Health Sponsorship Council SunSmart PhD Scholarship. Associate Professor Reeder and the Cancer Society Social & Behavioural Research Unit receive support from the CSNZ Inc. and the University of Otago. Professor McGee and Mr Gray receive support from the University of Otago.The authors also thank Nathalie Huston and Margaret Henry for providing research support services, Helen Glasgow for initial work developing the survey, and Dr Simon Horsburgh for data management assistance.The Cancer Society Social & Behavioural Research Units role was primarily limited to the provision of advice about the more recent survey waves, data analysis and reporting.

Correspondence

Associate Professor Anthony Reeder, Cancer Society Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, PO Box 913, Dunedin 9054, New Zealand. Fax: +64 3 479 7298;

Correspondence Email

tony.reeder@otago.ac.nz

Competing Interests

None identified.

Ministry of Health. Cancer: New Registrations and Deaths 2009. Wellington 2012.O'Dea D. The Costs of Skin Cancer to New Zealand. Wellington: Wellington School of Medicine, 2009.Pearce D, Williford PM, Blakrishnan R, Feldman SR. Economics of skin cancer. In: Nouri K, editor. Skin Cancer: New York: McGraw Hill; 2008, p679-85.Armstrong B. How sun exposure causes skin cancer: an epidemiological perspective. In: Hill D, Elwood JM, English DR, editors. Prevention of Skin Cancer. Dordrecht: Kluwer Academic Publishers; 2004, p89-116.Green A, Siskind V, Bain C, Alexander J. Sunburn and malignant melanoma. Br J Cancer. 1985;51:393-397.Watts C, Reeder AI, Glasgow H. A cover-up story: the Cancer Society Melanoma Prevention Programme. UV radiation and its effects - an update. Wellington: Royal Society of New Zealand; 2002, p83.McGee R, Williams S, Cox B, Elwood M, Bulliard J-L. A community survey of sun exposure, sunburn and sun protection. N Z Med J. 1995;108:508-10.Richards R, McGee R, Knight RG. Sunburn and sun protection among New Zealand adolescents over a summer weekend. Aust NZ J Publ Health. 2001;25:352-54.Borland R, Hill D, Noy S. Being SunSmart: changes in community awareness and reported behaviour following a primary prevention program for skin cancer control. Behav Change. 1990;7:126-35.Ministry of Health. Ethnicity data protocols for the health and disability sector. Wellington: Ministry of Health; 2004.Fitzpatrick TB. The validity and practicality of sun-reactive skin types I through VI. Arch Dermatol. 1988;124:869-71.Taylor Nelson Sofres Group (TNS). Sun Protection Market Research Report. Report 1301934 prepared for Health Sponsorship Council and Cancer Society of NZ; Wellington: 2006.SAS System for XP_PRO [computer program]. Version v 9.1.3 2000-2003.Stata statistical software: Release 12, [computer program]. Version Release 12.0 College Station, Texas: StataCorp LP; 2011.http://www.stata.com/support/faqs/resources/citing-software-documentation-faqsDobbinson S, Wakefield M, Hill D, et al. Prevalence and determinates of Australian adolescents' and adults' weekend sun protection and sunburn, summer 2003-2004. J Am Acad Dermatol 2008;59:602-14Volkov A, Dobbinson S, Wakefield M, Slevin T. Seven-year trends in sun protection and sunburn among Australian adolescents and adults. Aust NZ J Publ Health 2013;37:63-9.Bulliard JL. Site-specific risk of cutaneous malignant melanoma and pattern of sun exposure in New Zealand. Int J Cancer. 2000;85:627-32.Hill D, White V, Marks R et al. Melanoma prevention: behavioural and nonbehavioral factors in sunburn among an Australian urban population. Prev Med. 1992;21:654-69.Horsburgh-McLeod GF, Gray AR, Reeder AI, McGee R. Sunburn in a New Zealand Urban Population, 1994-2006. Australasian Epidemiologist. Apr 2010;17(1):40-46.Dunn J, Lynch B, Dip G. Climatic conditions and the reporting of sun-protective behavior survey data: a brief report. Am J Health Promot. 2001;15:241-43.Broadstock M. Sun protection at the cricket. Med J Aust. 1991; 154:430.Hammond VA, Reeder AI, Gray A, Bell M. Are workers or their workplaces the key to occupational sun protection? Health Promotion J. Aust. 2008;19:97-101.Reeder AI, Gray A, McCool JP. Occupational sun protection: workplace culture, equipment provision and outdoor workers' characteristics. J Occup Health. 2013;in press.McLeod G. Sunburn in a New Zealand urban population, 1994-2006 [PhD]. Dunedin: Department of Preventive & Social Medicine, University of Otago; 2012.International Agency for Research on Cancer. Globocan 2008. Cancer incidence, mortality and prevalence worldwide. Lyons: IARC 2012; http://globocan.iarc.fr/.

Contact diana@nzma.org.nz
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Skin cancers are a significant public health problem in New Zealand (NZ). In 2009, cutaneous malignant melanoma (melanoma) was the fourth most commonly registered cancer and resulted in 326 deaths.1There are significant sex differences with the male age-standardised registration rate 27% higher than the female rate, and the male death rate more than twice that recorded for females (7.2:3.3 per 100,000).1Non-melanoma skin cancers, estimated to exceed 67,000 cases per annum2 and resulting in 97 reported deaths in 2009,1 are not required to be notified to the New Zealand Cancer Registry, but place a substantial burden on the health system and society.2,3Most skin cancers are potentially preventable through the avoidance of excessive, harmful exposure to ultraviolet radiation (UVR),4 with sunburn associated with increased risk.5For these reasons, national and regional SunSmart health promotion programs have been initiated in NZ since 1988, aimed at increasing public awareness of skin cancer, particularly melanoma, and reducing excessive UVR exposure.6As it was important to evaluate these efforts, the Cancer Society of New Zealand Inc. (CSNZ) and the Health Sponsorship Council (HSC) - now the Health Promotion Agency (HPA), commissioned the Triennial Sun Protection Survey (Sun Survey) series.From 1994 to 2006, cross-sectional surveys were carried out every three years among the NZ urban population. Data collected included sociodemographic information, outdoor sun exposure time, associated activity types and sunburn experience.To date, two peer-reviewed publications have reported descriptive Sun Survey data: one focused on respondents, 15-69 years, in 1994,7 and the other on the youngest age group, 12-17 years, in 1997.8The aim of the present paper is to extend the knowledge gained from these two reports by including data for three additional summers (1999/00, 2002/03 and 2005/06). As previously, outdoor sun exposure (activity type and duration) and sunburn experience for the recall weekends will be described, by sex, age group and skin type.Method Sample selection Respondents, 15-69 years inclusive, were residents of five surveyed metropolitan areas (Auckland, Wellington, Hamilton, Christchurch, and Dunedin) which represented approximately 55% of the total NZ population in the 2006 Census. Data were collected during summer, based on procedures used for a survey administered in Victoria, Australia.9 Participants were recruited either from randomly selected households using random digit dialling in the predetermined areas (1994 and 1997), or through telematching from electoral rolls, 1999-2006. Overall, data usable for analysis were obtained from 6,195 respondents with the breakdown by year as follows: 1994 n=1,243, 1997 n=1,188, 1999/00 n=1,250, 2002/03 n=1,250, and 2005/06 n=1,264. Given a primary prevention focus, interview protocols prioritised younger household members, but a quota system ensured approximately equal numbers by sex and city of residence. Procedures and instrument Data were obtained from computer-assisted telephone interviews (CATI), usually conducted on either the Monday or Tuesday evening, following selected survey weekends. Meteorological data were used to select appropriate survey weekends, with the main criterion being that the weather had been fine enough for potentially harmful sun exposure to have occurred.7 TNS was the contracted data collection agency in 2006, 2003 (then known as NFO New Zealand), and 2000 (then known as CM Research). The MRL Research group (1997) and Roy Morgan Research (1994) were contracted for previous survey years. The surveys used much common questionnaire content to facilitate comparisons across time. Sociodemographic information sought included sex, age and self-defined ethnicity (prioritised according to Level 1, the highest, of the NZ Ministry of Health ethnicity and data protocols).10 Self-reported skin type was based on a modified Fitzpatrick classification of skin sun-reaction: Type I (always burn, never tan), Type II (usually burn, tan with difficulty), Type III (sometimes burn, tan moderately), Type IV (rarely burn, tan easily).11 The exposure days selected varied by year. Data for both Saturdays and Sundays were recorded in 1994, however, due to possible respondent fatigue from survey length and cost issues, Sunday was preferentially selected in 1997 (unless the respondent was only outdoors and sunburnt on Saturday) so 1994 data were treated equivalently. Thereafter the recall day was selected using a standardised procedure.12 Information on sunburn (defined as any amount of reddening of the skin after being in the sun) and the body areas affected were recorded. Those who had spent longer than 15 minutes outdoors on the exposure day, 11am-4pm during daylight savings time (NZ Standard Time +1 hour), provided information on the type and duration of outdoor activities. Activities were classified slightly differently in 1994,7 therefore it was necessary to reclassify and collapse categories, to permit comparisons by year. The six activity categories formed were active recreation (e.g. sports), passive recreation (e.g. reading), water-based recreation (e.g. swimming), paid work, unpaid work (e.g. gardening), or unspecified recreation. The duration of the main outdoor activity (in minutes) was collected from respondents estimates. Analyses Chi-squared tests for association were used to identify significant between-group differences in sunburn patterns, including between years, sexes, age groups, skin sensitivities, and activities. Linear regression models were used to examine associations with duration outdoors. All data were analysed without sampling or post-stratification weights and using SAS 9.1.313 and Stata v12.1 software,14 with two-tailed tests used for the regression models. Statistical significance was determined by p<0.05 in all cases. Ethical approval Participation was taken as informed consent. Participants had previously been notified of the survey by mail from the commissioned market research agency. The proposed project analyses, reported here, were reviewed and ethical approval granted at the Departmental level, following University of Otago Human Ethics Committee procedures. Results Respondent characteristics Overall, 68.8% (n=4,264/6,195) of respondents reported meeting the outdoor status criterion (\u226515 minutes outdoors, 10am-4pm on recall weekend) (Table 1). Table 1. Respondent characteristics by outdoor status, 1994-2006 inclusive Variable All respondents n=6,195 Outdoor respondents n=4,264 P value n % n % of all outdoors % within category outdoors Sex Male Female 3,084 3,111 49.8 50.2 2,273 1,991 53.3 46.7 73.7 64.0 <0.001 Age group (years) 15-19 20-29 30-39 40-49 50-59 60-69 756 1,270 1,416 1,109 999 645 12.2 20.5 22.9 17.9 16.1 10.4 551 907 1,002 748 658 398 12.9 21.3 23.5 17.5 15.4 9.3 72.9 71.4 70.8 67.4 65.9 61.7 <0.001 Skin type* I II III IV Missing data 1,494 3,432 1,109 84 76 24.4 56.1 18.1 1.4 1,014 2,404 773 41 32 23.8 56.4 18.1 1.0 67.9 70.0 69.7 48.8 <0.001 City Auckland Hamilton Wellington Christchurch Dunedin 1,254 1,237 1,230 1,242 1,232 20.2 20.0 19.9 20.1 19.9 891 876 857 808 832 20.9 20.5 20.1 19.0 19.5 71.1 70.8 69.7 65.1 67.5 0.005 Priority ethnicity NZ European M\u0101ori Pacific Asian All other Missing data 5,326 405 123 231 55 55 86.7 6.6 2.0 3.8 0.9 3,676 288 79 140 42 39 86.2 4.6 1.9 3.3 1.0 69.0 71.1 64.2 60.6 76.4 0.026 Survey year 1994 1997 1999/2000 2002/2003 2005/2006 1243 1188 1250 1250 1264 20.1 19.2 20.2 20.2 20.4 854 921 802 808 879 20.0 68.7 <0.001 21.6 77.5 18.8 64.2 18.9 64.6 20.6 69.5 * Fitzpatrick sun-sensitivity scale, modified. Percentages may not total 100% due to rounding. All respondent characteristics were statistically significantly associated with being outdoors, with males, younger people, those with skin types I-III, Maori and those responding in 1997 more likely to report being outside than females, older people, those with skin type IV, Pacific and Asian respondents and those responding in other survey years. The following results are based on the 4,264 respondents who reported \u226515 minutes of outdoor activity, 11am-4pm, during the previous weekend. Sub-group analyses by ethnicity, while of potential interest, were not undertaken because of relatively small numbers in some categories. Sunburn experience Overall, 20.7% (n=882) of 4,259 outdoor respondents with valid datareported sunburn on the recall day (Table 2). Overall, sunburn experience was more common among males, younger respondents and those with vulnerable skin types than females, older respondents and those with less vulnerable skin types. Sunburn rates varied by year between 17.0% and 23.9%, but without a consistent pattern despite being somewhat higher in the most recent year than in the baseline survey. Table 2. Sunburn experience by sex, age and skin type* All Sunburned P value n %

Summary

Abstract

Aim

To describe summer weekend sun exposure and sunburn experience, 1994-2006, among urban New Zealanders (15-69 years) by sex, age group, skin type and outdoor activity type.

Method

A series of five telephone surveys undertaken in the summers of 1994, 1997, 1999-2000, 2002-3 and 2005-6 provided a sample of 6,195 respondents with usable data from five major cities (Auckland, Hamilton, Wellington, Christchurch and Dunedin). Respondents were administered a Computer Assisted Telephone Interview (CATI) questionnaire which sought sociodemographic information, sun exposure, and sunburn experience during the most recent weekend.

Results

Overall, 69% of the sample had spent at least 15 minutes outdoors between 11am and 4pm. Weekend sunburn was reported by 21%, and was more common among males, young adults and those with highly sun-sensitive skin than females, older adults and those with less sensitive skin. The head/face/neck was the body area most frequently and severely sunburned. Sunburn was associated with greater time spent outdoors and occurred most frequently during water-based (29%) and passive recreational activities (25%) and paid work (23%).

Conclusion

Sun protection strategies could usefully be targeted not only towards at-risk population groups, but also towards those activities and contexts most strongly associated with potentially harmful sun exposure.

Author Information

Geraldine (Geri) F. H. McLeod, Research Fellow, Christchurch Health and Development Stud, Department of Psychological Medicine, University of Otago, Christchurch; Anthony I Reeder,* Research Associate Professor, Cancer Society of New Zealand Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Andrew R. Gray, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin; Rob McGee, Professor, Department of Preventive & Social Medicine, Dunedin School of Medicine, University of Otago, Dunedin

Acknowledgements

The data analysed in this research were collected by contractors to the owners of the data, the Health Sponsorship Council (HSC) (now the Health Promotion Agency), SunSmart programme, and the Cancer Society of New Zealand Inc (CSNZ).Data were collected by Roy Morgan Research Centre Pty Ltd. (1994), MRL Research Group (1997), and TNS New Zealand Ltd., made up of CM Research and NFO NZ (1999/00-2005/06). The data were analysed by the authors. Geri McLeod received support from the Health Sponsorship Council SunSmart PhD Scholarship. Associate Professor Reeder and the Cancer Society Social & Behavioural Research Unit receive support from the CSNZ Inc. and the University of Otago. Professor McGee and Mr Gray receive support from the University of Otago.The authors also thank Nathalie Huston and Margaret Henry for providing research support services, Helen Glasgow for initial work developing the survey, and Dr Simon Horsburgh for data management assistance.The Cancer Society Social & Behavioural Research Units role was primarily limited to the provision of advice about the more recent survey waves, data analysis and reporting.

Correspondence

Associate Professor Anthony Reeder, Cancer Society Social & Behavioural Research Unit, Department of Preventive & Social Medicine, Dunedin School of Medicine, PO Box 913, Dunedin 9054, New Zealand. Fax: +64 3 479 7298;

Correspondence Email

tony.reeder@otago.ac.nz

Competing Interests

None identified.

Ministry of Health. Cancer: New Registrations and Deaths 2009. Wellington 2012.O'Dea D. The Costs of Skin Cancer to New Zealand. Wellington: Wellington School of Medicine, 2009.Pearce D, Williford PM, Blakrishnan R, Feldman SR. Economics of skin cancer. In: Nouri K, editor. Skin Cancer: New York: McGraw Hill; 2008, p679-85.Armstrong B. How sun exposure causes skin cancer: an epidemiological perspective. In: Hill D, Elwood JM, English DR, editors. Prevention of Skin Cancer. Dordrecht: Kluwer Academic Publishers; 2004, p89-116.Green A, Siskind V, Bain C, Alexander J. Sunburn and malignant melanoma. Br J Cancer. 1985;51:393-397.Watts C, Reeder AI, Glasgow H. A cover-up story: the Cancer Society Melanoma Prevention Programme. UV radiation and its effects - an update. Wellington: Royal Society of New Zealand; 2002, p83.McGee R, Williams S, Cox B, Elwood M, Bulliard J-L. A community survey of sun exposure, sunburn and sun protection. N Z Med J. 1995;108:508-10.Richards R, McGee R, Knight RG. Sunburn and sun protection among New Zealand adolescents over a summer weekend. Aust NZ J Publ Health. 2001;25:352-54.Borland R, Hill D, Noy S. Being SunSmart: changes in community awareness and reported behaviour following a primary prevention program for skin cancer control. Behav Change. 1990;7:126-35.Ministry of Health. Ethnicity data protocols for the health and disability sector. Wellington: Ministry of Health; 2004.Fitzpatrick TB. The validity and practicality of sun-reactive skin types I through VI. Arch Dermatol. 1988;124:869-71.Taylor Nelson Sofres Group (TNS). Sun Protection Market Research Report. Report 1301934 prepared for Health Sponsorship Council and Cancer Society of NZ; Wellington: 2006.SAS System for XP_PRO [computer program]. Version v 9.1.3 2000-2003.Stata statistical software: Release 12, [computer program]. Version Release 12.0 College Station, Texas: StataCorp LP; 2011.http://www.stata.com/support/faqs/resources/citing-software-documentation-faqsDobbinson S, Wakefield M, Hill D, et al. Prevalence and determinates of Australian adolescents' and adults' weekend sun protection and sunburn, summer 2003-2004. J Am Acad Dermatol 2008;59:602-14Volkov A, Dobbinson S, Wakefield M, Slevin T. Seven-year trends in sun protection and sunburn among Australian adolescents and adults. Aust NZ J Publ Health 2013;37:63-9.Bulliard JL. Site-specific risk of cutaneous malignant melanoma and pattern of sun exposure in New Zealand. Int J Cancer. 2000;85:627-32.Hill D, White V, Marks R et al. Melanoma prevention: behavioural and nonbehavioral factors in sunburn among an Australian urban population. Prev Med. 1992;21:654-69.Horsburgh-McLeod GF, Gray AR, Reeder AI, McGee R. Sunburn in a New Zealand Urban Population, 1994-2006. Australasian Epidemiologist. Apr 2010;17(1):40-46.Dunn J, Lynch B, Dip G. Climatic conditions and the reporting of sun-protective behavior survey data: a brief report. Am J Health Promot. 2001;15:241-43.Broadstock M. Sun protection at the cricket. Med J Aust. 1991; 154:430.Hammond VA, Reeder AI, Gray A, Bell M. Are workers or their workplaces the key to occupational sun protection? Health Promotion J. Aust. 2008;19:97-101.Reeder AI, Gray A, McCool JP. Occupational sun protection: workplace culture, equipment provision and outdoor workers' characteristics. J Occup Health. 2013;in press.McLeod G. Sunburn in a New Zealand urban population, 1994-2006 [PhD]. Dunedin: Department of Preventive & Social Medicine, University of Otago; 2012.International Agency for Research on Cancer. Globocan 2008. Cancer incidence, mortality and prevalence worldwide. Lyons: IARC 2012; http://globocan.iarc.fr/.

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