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2

Routine, Targeted and Non-Targeted Analysis of Environmental Contaminants of Emerging Concern – Development and Validation of a UHPLC Orbitrap MS Method

Overview

The purpose of this work was to develop a method for the targeted, quantitative

analysis of 61 contaminants of emerging concern (CECs) and non-targeted screening

of 312 CECs in wastewater treatment plant (WWTP) samples. The method used a

solid phase extraction procedure (SPE), ultrahigh performance liquid chromatography

(UHPLC) separation, Thermo Scientific™ Orbitrap™ mass spectrometry analysis

(UHPLC-Orbitrap MS) and the Thermo Scientific™ TraceFinder™ software tool. An in-

house compound database consisting of 312 CECs including parents products and

their metabolites, conjugates and treatment by-products was used in the verification of

the workflow as well as the non-targeted identification of CECs. Samples collected

from WWTPs were used to demonstrate the effectiveness of this method for both

targeted and non-targeted CEC analysis without using analytical standards.

Introduction

Contaminants of emerging concern in the environment are generally described as

compounds that are unknown or unrecognized, undetected or not routinely monitored,

and represent a diverse group of chemicals that may pose a risk to human health and

the environment. New CECs were discovered by using recently available analytical

technologies and implicated by a prior knowledge of the process details. Due to limited

analytical capability and available resources (e.g., hardware, software, analytical

standards and capacity), monitoring of CECs has been focused on selected analytes

rather than a holistic approach which includes as many known chemical classes in the

analysis as possible. Presented in this poster is a new analytical method that can be

used in the quantitative analysis of 61 targeted and 312 non-targeted CECs. Analytical

results obtained for a series of WWTP samples were used to evaluate and

demonstrate the effectiveness of this method.

Methods

Sampling

Grab samples were collected from a pilot WWTP (Figure 1) and two WWTPs (Figure

2) using a nitrifying process and ultraviolet disinfection technologies. Following

screening, primary sewage grab samples were taken from the aerated grit tank

(Figures 1 and 2, S1) and thickened waste activated sludge tank (Figure 1, TWAS,

S2). Primary effluent samples (Figure 2, S3) were taken after primary sedimentation

(with settled solids removed at this stage) and after the first point of addition of ferric

chloride to reduce total phosphorous through precipitation. Secondary and final

effluent grab samples (Figure 2, S4 and S6) and permeate (Figure 1, S5) were also

collected from the WWTPs. A total of ten samples were collected and stored at 4

±

2 ºC

until ready for analysis.

Figure 1. Schematic of the pilot WWTP identifying the three locations of sampling

points.

Chemicals, Sample Preparat

HPLC grade acetonitrile (CH

3

Scientific (Ottawa, ON, Canad

and sample preparation was p

Thermo Scientific™ Barnstea

ON, Canada). Laboratory Ser

prepare samples for targeted

screening. Waters OASIS® (

(SPE) cartridge (6 cc, 500 mg

accredited by the Canadian A

2004.

Neat standards of native targe

(Oakville, ON, Canada). Deut

from CDN Isotopes (Pointe-Cl

(Andover, MA, US). Native an

were prepared by mixing the c

analytical standard solutions

CH

3

OH.

Sample analysis was achieve

UHPLC consisting of a HRG-3

TCC-3400 column compartme

a Thermo Scientific™ Betasil

2.1x100 mm coreshell technol

Orbitrap MS analysis. Details

The UHPLC was interfaced to

using a heated electrospray io

was tuned and calibrated in p

mixtures of MSCAL5 and MS

source (35 L/min). Spray volta

negative modes. Mass spectr

140,000 (defined as full-width-

resulting a scanning rate of >

of 1.6x10

6

and a C-trap inject

Data Analysis

TraceFinder software was use

The same software was also

database of 312 CECs consist

hormones, surfactants and pe

search for adduct ions (M+H)

+

H)

molecular ion in the negati

software then creates an extra

window (MEW) of 5 ppm. Anal

threshold of 50,000 (approxim

ppm mass accuracy for the m

threshold of 90% with relative

about 65 sec/sample using th

manually for the top 10

th

perc

which analytical data were co

S1

S2

S5

Results

Targeted Compound Analysi

Table 1 lists results obtained fr

samples along with their respe

61 target compounds were fou

Figure 2. Schematic of the