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Analysis of Triazine Pesticides in Drinking

Water Using LC-MS/MS (EPA Method 536.0)

Jonathan Beck, Thermo Fisher Scientific, San Jose, CA, USA

Introduction

The US EPA has recently issued a draft form of a proposed

method for the analysis of triazine compounds in drinking

water.

1

This method uses a simple method to directly analyze

triazine compounds using LC-MS/MS without requiring any

solid phase extraction (SPE) or other lengthy sample

preparation steps. This application note demonstrates the

analysis of these compounds over the concentration range

0.25 – 5.0 ng/mL (ppb) using the Thermo Scientific TSQ

Quantum Access

triple stage quadrupole mass spectrometer

and the Thermo Scientific Accela

HPLC system.

Experimental Conditions

The following triazine and triazine degradates were analyzed:

Atrazine, Atrazine-desethyl, Atrazine-desisopropyl,

Cyanazine, Propazine, and Simazine, purchased from

Sigma-Aldrich, St. Louis, MO, and Ultra Scientific, North

Kingstown, RI. The following internal standards were used:

Atrazine-d

5

, Atrazine-desethyl-d

7

, Atrazine-desisopropyl-d

5

,

Cyanazine-d

5

, Propazine-d

14

, and Simazine-d

10

, purchased

from C/D/N Isotopes, Inc., Pointe-Claire, Quebec, Canada.

Standards and internal standard stocks were prepared in

solutions of methanol and diluted to their appropriate

concentrations prior to analysis.

Sample Preparation

While no SPE was required for this method, samples were

treated as per the EPA’s draft method. The method calls

for the addition of ammonium acetate at 20 mM for pH

adjustment and dechlorination and sodium omadine at

64 mg/L to prevent microbial degradation, both purchased

from Sigma-Aldrich, St. Louis, MO. All samples were

prepared in reagent water. All samples were spiked with

the internal standard solution, resulting in a final

concentration of 5 ng/mL (ppb) for each internal standard.

Calibration standards were prepared at the following

levels: 0.25, 0.5, 1, 2, 2.5 and 5 ng/mL.

HPLC Conditions

Column:

Thermo Scientific Hypersil GOLD

100 x 2.1 mm, 3 µm

Solvent A:

5 mM Ammonium Acetate

Solvent B:

Methanol

Flow Rate:

400 µL/min

Injection Volume:

100 µL

HPLC Gradient:

Time

%A

%B

0:00

98

2

10:00

98

2

20:00

10

90

25:00

10

90

25:06

98

2

30:00

98

2

Mass Spectrometer Conditions

Ionization Source:

Positive Electrospray

Sheath Gas:

30 arbitrary units

Auxiliary Gas:

10 arbitrary units

ESI Voltage:

3.5 kV

Ion Transfer Tube Temperature:

350 °C

Collision Gas:

1.5 mTorr

Q1/Q3 Peak Resolution:

0.7 Da

Scan Width:

0.01 Da

MS Parameters

Precursor

Product

Collision

Tube

Compound

Mass

Mass

Energy

Lens

Atrazine-desisopropyl

174

132

17

90

Atrazine-desethyl

188

146

16

95

Simazine

202

124

17

80

Atrazine

216

174

16

85

Propazine

230

124

17

80

Cyanazine

241

214

15

100

Atrazine-desisopropyl-d

5

179

137

17

85

Atrazine-desethyl-d

7

195

147

17

95

Simazine-d

10

212

137

19

95

Atrazine-d

5

221

179

17

95

Propazine-d

14

244

196

18

95

Cyanazine-d

5

246

219

16

100

Key Words

• Drinking Water

Analysis

• Herbicides

• Hypersil GOLD

Columns

• Triazines

• TSQ Quantum

Access

Application

Note: 434