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18
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Page 1: Information archivée dans le Web - canada.ca · Information archivée dans le Web Information archivée dans le Web à des fins de consultation, de recherche ou de tenue de documents.

Ce contenu a été archivé le 30 juillet 2013.

Information archivée dans le Web

Information archivée dans le Web à des fins de consultation, de recherche ou de tenue de

documents. Cette dernière n'a aucunement été modifiée ni mise à jour depuis sa date de mise

en archive. Les pages archivées dans le Web ne sont pas assujetties aux normes qui

s'appliquent aux sites Web du gouvernement du Canada. Conformément à la Politique de

communication du gouvernement du Canada,

vous pouvez demander de recevoir cette information dans tout autre format de

rechange à la page « Contactez-nous ».

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This content was archived on July 30, 2013.

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 30 of 61

Figure 3a: Finished Water Quality Descriptive Results (Jan. 1, 1993 to Dec. 31, 1998) Rossdale plant

(i) Daily mean finished water turbidity(NTU) (span 25 days) 5

(ii) Daily mean finished water particle counts (span 25 days)

(iii) Distribution of observed daily mean (iv) Distribution of observed daily mean finished water turbidity values finished water particle counts

5 25-day span may be interpreted as a weighted moving average, based on surrounding observations within an 25-day interval

1/01/93 1/01/94 1/01/95 1/01/96 12/31/96 12/31/97 12/31/98

0.00

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 31 of 61

Figure 3b: Finished Water Quality Descriptive Results (Jan. 1, 1993 to Dec. 31, 1998) E.L. Smith plant

(i) Daily mean finished water turbidity (NTU) (span 25 days)

(ii) Daily mean finished water particle counts (span 25 days)

(iii) Distribution of observed daily mean (iv) Distribution of observed daily mean finished water turbidity values finished water particle counts

1/01/93 1/01/94 1/01/95 1/01/96 12/31/96 12/31/97 12/31/98

0.00

0.05

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 32 of 61

Figure 4a: Raw Water Quality Descriptive Results (Jan. 1, 1993 to Dec. 31, 1998) Rossdale plant

(i) Daily mean raw water turbidity (span 60 days) 6

(ii) Daily raw water faecal coliform counts (span 60 days)

(iii) Density plot of observed daily mean (iv) Density plot of observed daily mean raw water turbidity values raw water faecal counts

6 60-day span may be interpreted as a weighted moving average, based on surrounding observations within an 60-day interval

1/01/93 1/01/94 1/01/95 1/01/96 12/31/96 12/31/97 12/31/98

0

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1/01/93 1/01/94 1/01/95 1/01/96 12/31/96 12/31/97 12/31/980

50100150200250300350 12/10/97

0 100 200 300 400 500 600 700 800 900 10000

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orm

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 33 of 61

Figure 4b: Raw Water Quality Descriptive Results (Jan. 1, 1993 to Dec. 31, 1998) E.L. Smith plant

(i) Daily mean raw water turbidity (span 60 days)

(ii) Daily raw water faecal coliform counts (span 60 days)

(iii) Density plot of observed daily mean raw (iv) Density plot of observed daily mean raw water turbidity values water faecal counts

0 100 200 300 400 500 600 700 800 900 10000

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Daily Raw Water Fecal Coliform Counts

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 34 of 61

4.1 b) Environmental parameters

Summary statistics are provided for the environmental parameters in Table 9. Temporal trends

for daily extreme temperatures and precipitation are provided in Figures 5 and 6, respecti vely. Strong

seasonal patterns were apparent for these data, with peaks being observed during the spring and

summer season.

Figures 7 and 8 visually describe the relationship between raw water turbidity and

environmental factors. In general, increases in temperature and precipitation were accompanied by an

increase in raw water turbidity.

Table 9: Summary statistics for environmental parameters (Jan. 1, 1993 to Dec. 31, 1998)

Figure 5: Maximum and minimum daily temperatures (°C) (Jan. 1, 1993 to Dec. 31, 1998) (span=25 days) (refer to footnote 5)

Figure 6: Daily precipitation (mm) (Jan. 1, 1993 to Dec. 31, 1998) (span=25 days)

1/01/93 1/01/94 1/01/95 1/01/96 12/31/96 12/31/97 12/31/98

-40

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MaximumMinimum

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0.0

2.5

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7.5

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Environmental Parameter Std. Dev. Median Mean95% Confidence Interval (Mean)

Daily maximum temperature (degrees Celsius) -30.9 to 34.5 13.2 10.7 8.7 (8.2 , 9.2)

Daily minimum temperature (degrees Celsius) -37.8 to 18.6 11.8 0.5 -1.3 (-1.8 , -0.8)

Daily precipitation (millimetres) 0 to 63.4 4.1 0 1.3 (1.1 , 1.5)

Range

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 35 of 61

Figure 7: Comparing daily maximum temperature and daily mean raw water turbidity (a) Rossdale plant

(b) E.L. Smith plant

Figure 8: Comparing daily precipitation and daily mean raw water turbidity (a) Rossdale plant

(b) E.L. Smith plant

mm and

NTU

°C and NTU

°C and NTU

1/01/93 1/01/94 1/01/95 1/01/96 12/31/96 12/31/97 12/31/98-50

0

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mm and

NTU

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 36 of 61

4.1 c) Socio-economic data Average annual household incomes reported in 1995 are shown in Figure 9.

Figure 9: Distribution of average annual household incomes per postal code in Edmonton, 1995

4.1 d) Health outcome data

To ensure that all individuals could be linked to water quality values up to 40 days prior their

date of illness, February 10 th 1993 was the first service date considered for analysis, and December 31,

1998 was the last. Detailed profiles of each data source are provided in Figures 10a to 10d. The

majority of cases were captured by utilizing the physician-office data from the AHCIPP database.

Although long-term care centres also provide regular treatment to individuals suffering from persistent

mental illness and physical disabilities, the majority of patients (70%) captured in this database were

greater than 65 years of age. In contrast, only 10% of selected cases in the emergency room and

physician-visit billing data sources were greater than 65 years.

The distribution of cases by the most responsible ICD-9 code is also provided. For

comparative purposes, the same ICD-9 codes are presented for each data source, and represent the

majority of what was observed in the respective databases.

The seasonal distribution of cases on a bi-weekly basis was also apparent, with a higher

incidence of cases observed during the spring and early summer months. More cases were also

admitted to the hospital at the beginning rather than during the work week. In contrast, more cases

sought emergency room services during the weekend.

- > $80,000 - $65,000 - $80,000 - $50,000-$65,000 - $35,000-$50,000

- $20,000-$35,000 - < $20,000

-113.7 -113.6 -113.5 -113.4 -113.3

LONGITUDE

53.4

53.5

53.6

53.7

LA

TIT

UD

E

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 37 of 61

Figure 10a: Data Profile (February 10, 1993 to December 31, 1998) : Hospital Admissions (CIHI data source)

(i) Distribution of cases by age group and water service area

(ii) Number of cases per 14-day interval (seasonal distribution) (iii) Proportion of cases by most responsible ICD-9 code (iv) Proportion of cases by day of week

Rossdale E.L. Smith Mixed Zone

2 to 18 302 (24.5%) 140 (27.6%) 359 (33.1%)

> 18 to 65 548 (44.4%) 214 (42.2%) 443 (40.9%)

> 65 383 (31.1%) 153 (30.2%) 282 (26.0%)

Total Cases per Water Service Area

1,233 (100%) 507 (100%) 1,084 (100%)

Water Service Area

Age Group (yrs)

0

20

40

60

80

100

001 002 003 004 005 006 007 008 009 276 535 558 578 780 783 787 7890

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15

20

25

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ll C

IHI

ca

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(%)

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f all

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I ca

ses

(%)

1993/01/01 1994/01/01 1995/01/01 1996/01/01 1997/01/01 1998/01/01

5

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35

No.

ca

ses

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 38 of 61

Figure 10b: Data Profile (February 10, 1993 to December 31, 1998) : Emergency room-related visits (EMRG data source)

(i) Distribution of cases by age group and water service area

(ii) Number of cases per 14-day interval (seasonal distribution) (iii) Proportion of cases by most responsible ICD-9 code (iv) Proportion of cases by day of week

Rossdale E.L. Smith Mixed Zone

2 to 18 2,079 (31.4%) 1,361 (37.2%) 2,952 (38.8%)

> 18 to 65 3,834 (57.8%) 2,000 (54.7%) 4,068 (53.5%)

> 65 718 (10.8%) 295 (8.1%) 580 (7.6%)

Total Cases per Water Service Area

6,631 (100%) 3,656 (100%) 7,600 (100%)

Water Service Area

Age Group (yrs)

0

20

40

60

80

100

001 002 003 004 005 006 007 008 009 276 535 558 578 780 787 7890

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25

Sun Mon Tue Wed Thu Fri Sat

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po

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EMR

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ase

s (%

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EMRG

ca

ses

(%)

1993/01/01 1994/01/01 1995/01/01 1996/01/01 1997/01/01 1998/01/01

60

100

140

180

No.

ca

ses

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 39 of 61

Figure 10c: Data Profile (February 10, 1993 to December 31, 1998) : Physician-office visits (PHYS data source)

(i) Distribution of cases by age group and water service area

(ii) Number of cases per 14-day interval (seasonal distribution) (iii) Proportion of cases by most responsible ICD-9 code (iv) Proportion of cases by day of week

Rossdale E.L. Smith Mixed Zone

2 to 18 20,659 (33.3%) 11,449 (38.4%) 23,366 (36.5%)

> 18 to 65 36,955 (59.5%) 16,369 (54.9%) 32,105 (54.3%)

> 65 4,446 (7.2%) 2,004 (6.7%) 3,708 (6.3%)

Total Cases per Water Service Area

62,060 (100%) 29,822 (100%) 59,179 (100%)

Water Service Area

Age Group (yrs)

0

20

40

60

80

100

001 002 003 004 005 006 007 008 009 276 535 558 578 780 787 789

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ase

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200

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1000

1400

No.

ca

ses

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 40 of 61

Figure 10d: Data Profile (February 10, 1993 to December 31, 1998) : Long-term care vists (LTC data source)

(i) Distribution of cases by age group and water service area

(ii) Number of cases per 14-day interval (seasonal distribution) (iii) Proportion of cases by most responsible ICD-9 code (iv) Proportion of cases by day of week

Rossdale E.L. Smith Mixed Zone

2 to 18 22 (6.8%) 10 (8.2%) 20 (8.3%)

> 18 to 65 59 (18.3%) 30 (24.6%) 56 (23.3%)

> 65 241 (74.8%) 82 (67.2%) 164 (68.3%)

Total Cases per Water Service Area

322 (100%) 122 (100%) 240 (100%)

Water Service Area

Age Group (yrs)

0

20

40

60

80

100

001 002 003 004 005 006 007 008 009 276 535 558 578 780 787 7890

5

10

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20

25

Sun Mon Tue Wed Thu Fri Sat

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ca

ses

(%)

Pro

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f all

LTC

ca

ses

(%)

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0

5

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No

. ca

ses

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 41 of 61

4.2 Statistical Analyses 4.2 a) Multivariate logistic regression

As described in section 3.2, multivariate logistic regression analysis was conducted to

determine if the risk of gastroenteritis varied for residents of different water service areas. The final

model derived using the generalised linear model (GLM) was :

(refer to Table 5 for a complete description of variable names)

As time was both a component of the seasonal parameter and of the categorical source variable

(SOURCE), the impact of water source was assessed by calculating the relative change after

December 10, 1997 in the risk of gastroenteritis between Rossdale and E.L. Smith serviced residents.

Presented in Table 10 are the results of this comparison, carried out using appropriate contrasts within

the final logistic regression model for each health outcome data set. The odds ratios equate to the

relative change in risk among service areas after Dec 10 ’97. For example, the “risk” in hospitalisation

for gastroenteritis among Rossdale serviced residents in comparison to E.L. Smith serviced residents

fell by a magnitude of 0.18 times after December 10, 1997 (Table 10).

Table 10: Multivariate Logistic Regression Results: Comparisons Among Service Areas

Comparison Parameter

Estimate P-value Odds Ratio

Hospital Admissions (all age groups) (< Dec ‘97): Rossdale \ E.L. Smith vs.

0.1669 0.0557 1.18

(≥ Dec ’97): Rossdale \ E.L. Smith

Emergency Room Visits (all age groups) (< Dec ‘97): Rossdale \ E.L. Smith vs.

0.0956 0.0026 1.10

(≥ Dec ’97) Rossdale \ E.L. Smith

Physician Visits (all age groups) (< Dec ‘97): Rossdale \ E.L. Smith vs.

-0.0147 0.5544 0.99

(≥ Dec ’97): Rossdale \ E.L. Smith

Long-term Care (≥ 65 year olds) (< Dec ‘97): Rossdale \ E.L. Smith vs.

0.1973 0.3145 1.22

(≥ Dec ’97): Rossdale \ E.L. Smith

The results of Table 10 suggest a small lowering in risk of gastroenteritis among Rossdale

residents (in comparison to E.L. Smith serviced residents) after Dec 10 ’97. Statistically significant (P <

0.10) relative “risk” reductions were noted among hospitalisations and emergency room visits.

Logit (case/control) = SOURCE + INCOME + AGEGROUP + SPLINE1st 2 months + … + SPLINE last 2 months

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 42 of 61

Based on the model above, the following spatial model was determined using generalised

additive modeling (GAM):

(refer to Table 5 for a complete description of variable names)

Figure 11 shows the distribution of centroid points associated with all Edmonton postal codes

and their assigned water source.

Figure 11: Spatial distribution of postal codes within Edmonton and corresponding water

service areas

Odds ratios corresponding to each longitude and latitude combination for each captured postal

code were determined, both before and after December 10, 1997. For illustrative purposes, an odds

ratio of 1.2 for each spatial location represents a 20% increase in the likelihood of illness associated

with that centroid point, compared to the predicted probability associated with the mean location effect,

after adjusting for other parameters in the model. Results for each data source are presented in

Figures 12a to 12d. Spatially, there does not appear to be an obvious association between the risk of

gastroenteritis and water supply area after controlling for other important risk factors.

Logit (case/control) = loess (LONGITUDE, LATITUDE, span=0.2) + DEC1097 + INCOME + AGEGROUP + loess (Seasonal parameter, span=220 days)

Rossdale w.s.a

E.L. Smith w.s.a.

Mixed w.s.a.

-113.7 -113.6 -113.5 -113.4 -113.3LONGITUDE

53.4

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LATI

TUD

E

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 43 of 61

Figure 12a: Spatial distribution of disease risks within the city of Edmonton between 1993-1998: CIHI hospitalisation data source, excluding infants (less than 2 year-olds)

(i) Prior to December 10, 1997

(ii) After December 10, 1997

< 1.0 1.0 – 1.1 1.1 – 1.2 1.2 – 1.3 > 1.3

Odds Ratios

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longitude

53.4

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lati

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longitude

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ude

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 44 of 61

Figure 12b: Spatial distribution of disease risks within the city of Edmonton between 1993-1998: Emergency room visit data source, excluding infants (less than 2 year-olds)

(i) Prior to December 10, 1997

(ii) After December 10, 1997

< 1.0 1.0 – 1.1 1.1 – 1.2 1.2 – 1.3 > 1.3

Odds Ratios

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53.4

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Investigating the relationship between drinking water and gastroenteritis: Edmonton, 1993-1998 November 29th, 2002

Page 45 of 61

Figure 12c: Spatial distribution of disease risks within the city of Edmonton between 1993-1998: Physician-office billing data source (randomised subset),

excluding infants (less than 2 year-olds) (ii) Prior to December 10, 1997

(ii) After December 10, 1997

< 1.0 1.0 – 1.1 1.1 – 1.2 1.2 – 1.3 > 1.3

Odds Ratios

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longitude

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longitude

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ude