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Conclusions

The developed analytical method allowed the extraction,

detection and quantification of six of the most used

anti-infectives in untreated and treated sewage. Detection

limits ranged from 0.3 to 22 ng L

-1

and instrument

response was linear (

r

2

0.99) in the dynamic range

(25–1000 ng L

-1

). The use of two specific SRM transitions

and their peak area ratios proved to be a reliable and

effective way to reduce false positives and confirm the

presence of targeted substances. All the studied anti-

infectives were found in the wastewater samples in con-

centrations ranging from 39 to 276 ng L

-1

. More studies

are necessary to elucidate the fate of these anti-infectives

after they are discharged into the St. Lawrence River as

well as their effects on aquatic biota and the environment.

0

100

200

300

Sulfamethoxazole

Trimethoprim

Ciprofloxacin

Levofloxacin

Clarithromycin

Azithromycin

Concentration (ng/L)

North Influent

South Influent

Effluent

Figure 4: Occurrence of the studied anti-infectives in the dissolved phase of raw and treated

sewage of the City of Montréal (

n

=3)

Table 4: Removal efficiency of the Montréal wastewater

treatement plant and average mass flow of the studied

anti-infectives.

Mean mass flow in

the St. Lawrence

Compound

River (g day

-1

)

Sulfamethoxazole

340 ± 30

Trimethroprim

310 ± 20

Ciprofloxacin

320 ± 10

Levofloxacin

118 ± 2

Clarithromycin

830 ± 60

Azithromycin

310 ± 20

References

1

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Barber L.B., and Buxton H.T. (2002)

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2

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Total Environment

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3

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4

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5

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Chemistr

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6

Watts CD, Crathorne B, Fielding M, and Steel CP (1983)

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Organic Micropollutants in Water

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7

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8

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AN62489_E 11/07S

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