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Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne Poulstrup & Dr. Henrik L. Hansen Regional Public Health Office Southern Jutland and Funen, Denmark Vedelsgade 17 A, DK – 7100 Vejle E-mail: [email protected]

Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

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Page 1: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Use of Exposure Simulation Models and GIS-integrated health registers

EUROHEIS/SAHSU Conference March 2003Östersund, Sweden 30 – 31 March 2003

Dr. Arne Poulstrup & Dr. Henrik L. Hansen

Regional Public Health Office

Southern Jutland and Funen, Denmark

Vedelsgade 17 A, DK – 7100 Vejle

E-mail: [email protected]

Page 2: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Case Study:

Cancer development in an urban population due to airborne dioxin,

assessed by use of an exposure simulation model

and a GIS-integrated health register

Page 3: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Prevailing problems concerning environmental exposures and health outcomes:

Levels of exposure of individuals are often unknown

Areas of exposure are difficult to demarcate

Time of exposure is difficult to determine

Hence: the number of individuals in time and space exposed for certain levels of environmental

hazards are rarely possible to identify precisely

Page 4: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

A solution to environmental exposure level assessment:

Simulation models for exposure can be used, like atmospheric dispersion models for airborne pollution:

A Danish Gaussian plume model (OML) simulates the dispersion of plumes, incorporating features like Heights of one or more stacks (more sources) Smoke emissions, velocity and temperature High rise nearby buildings, surrounding terrains Atmospheric conditions, like prevailing wind

directions, wind temperatures, fall of rain, snow etc.

Page 5: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Case Study: Simulated immissions of hourly conc. of dioxin, using OML, has been geo-coded and layered into GIS.

Colours represent conc. of dioxin

Page 6: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

A solution to the demarcation of the exposed population:

The population at risk is identified by applying all addresses (inclusive historical) into GIS, using geo-coded addresses

And by linkage of all individuals to these addresses using the unique CPR number (10 digit number in Central Population Register [Civil Registration System])

Page 7: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

All addresses since 1986 have been applied as a layer in GIS.

Each address contains info on migration of every indivi-dual who lives or has lived there, as well as duration of stay

Page 8: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

The boundaries of the dioxin exposure (simulated immission of dioxin > 0 pg/h/m3)

is then used to demarcate the exposed area.

Polygon 1.

Page 9: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Polygon 2:

area with

dioxin conc.

≥ 3 pg/h/m3

Page 10: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Polygon 3:

area with

dioxin conc.

≥ 4.5 pg/h/m3

Page 11: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Polygon 4:

area with

dioxin conc.

between

0 -3 pg/h/m3

Page 12: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Polygon 5:

Area with

dioxin conc.

between

3-4.5 pg/h/m3

Page 13: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Solution to exposure time assessment:

Number of records are reduced to number of individuals

Only individuals who have stayed more than two years are selected

Only individuals relevant for selected health outcome, e.g. cancer are selected

Page 14: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

The selected exposed individuals in time and space are then linked to the National Cancer Registry using the CPRs.The map shows the diagnosed cancers (in dark blue) among all exposed individuals (in yellow) in polygon 1

Page 15: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Same procedure is used to select and demarcate the control area:

Selection of a suitable area (non exposure)

Selection of sufficient number of controls

Selection of individuals who have stayed sufficient time in the area

Page 16: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Final analyses of the case area will include the different bands of exposure (from 0 – 6 g-12 of dioxin/hour),

and in the analyses of health outcome (i.e. “all cancer”) in the selected open cohorts, the following confounders will be controlled for gender ratio, age stratas and at least one socio-economic variable

Page 17: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

So far analyses have been made, comparing cancer rates from the exposed area from the period 1986 – 1998 with national cancer rates, and:

SIR (Standardized Incidence Ratio) and

IRR (Incidence Rate Ratio)

showed no excess of cancer in the area of exposure

Page 18: Use of Exposure Simulation Models and GIS-integrated health registers EUROHEIS/SAHSU Conference March 2003 Östersund, Sweden 30 – 31 March 2003 Dr. Arne

Medical Office of Health, Province of Vejle, Denmark

Financially the study has been supported by

grants from:

European Commission,DG for Health and Consumer Protection

Ministry of Health, Denmark