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LC-MS/MS Analysis of Anti-Infectives

In Raw and Treated Sewage

P.A. Segura

1

, A.Garcia Ac

1

, A. Lajeunesse

2

, D.Ghosh

3

, C. Gagnon

2

and S. Sauvé

1

1

Département de Chimie, Université de Montréal, C.P. 6128, succursale Centre-ville, Montréal, QC, Canada H3C 3J7

2

Centre Saint-Laurent, Environnement Canada, 105, rue McGill, Montréal, QC, Canada H2Y 2E7

3

Thermo Fisher Scientific, San Jose, CA, USA

Application

Note: 372

Key Words

• TSQ Quantum

Ultra

• Surveyor HPLC

• Antibiotics

• SPE

Introduction

“Anti-infectives” is a general term that refers to several

classes of biologically active compounds used to treat

or prevent infections. Therapeutic agents such as anti-

microbials (synthetic) and antibiotics (natural or

semi-natural) are examples of anti-infectives.

The widespread utilization of anti-infectives in urban

centers as well as their resistance to biodegradation or

elimination in wastewater treatment plants (WWTPs) has

led to their appearance in effluents and surface waters

[1-3]

.

In the last few years there has been a growing concern

about the environmental fate and the possible effects of

these agents on the aquatic environment

[4,5]

.

The first report on the occurrence of anti-infective

traces in the aquatic environment was published as early

as 1983

[6]

. A later study

[7]

acknowledged that pharmaceu-

ticals would enter the water cycle mainly via a “domestic

route” (

i.e.

by the excreta of individuals taking medication

at homes, hospitals or clinics). It is therefore important to

know the amounts of these substances released in the

aquatic environment to be able to evaluate potential effects.

A sensitive and robust method was developed for the

determination of some of the most prescribed anti-infec-

tives in trace amounts (lower nanogram-per-liter range) in

raw and treated wastewaters.

Goals

Quantify several anti-infectives at the lower nanogram-

per-liter level in raw and treated wastewaters.

Apply two specific single reaction monitoring mode

(SRM) transitions and their peak ratio to avoid the

presence of false positives.

Method

Raw sewage (north and south influent) was collected and

treated (effluent) 24-h composite samples at the municipal

wastewater treatment plant of the City of Montréal

(Québec, Canada). This plant has physico-chemical treat-

ments only and its effluent is one of the largest in North

America. We analyzed six of the most prescribed com-

pounds (sulfamethoxazole, trimethoprim, ciprofloxacin,

levofloxacin, clarithromycin and azithromycin) (Figure 1),

by using solid phase extraction (SPE) and liquid chro-

matography-tandem mass spectrometry (LC-MS/MS).

The compounds were selected based on drugstore sales.

NH

2

S

O

O HN

N

O

O

O

O

N

N NH

2

N H

2

N

O

O H

F

N

HN

O

N

O

O H

F

N

N

O

O

N

N

N H

2

N H

2

C l

O

O

O

O

HO

O H

O

O

OH

N

O O H

O

O

O

N

O

OH

HO

OH

O

O

OH

N

O OH

O

O

Sulfamethoxazole

Trimethoprim

Ciprofloxacin

Levofloxacin

Pyrimethamine (IS)

Clarithromycin

Azithromycin

O

O

N

N NH

2

NH

2

N

O

OH

F

N

HN

O

F

Diaveridine (IS)

Lomefloxacin (IS)

Josamycin (IS)

O

O

HO

O

O

O

O

O O O

OH

N

O

O

OH

O

a.

b.

c.

Figure 1: Molecular structures of the anti-infectives studied (a), the surrogate standard (b), and the internal standards (c).