identification of unknown microcystins in alberta … of unknown microcystins in alberta lake water...

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Identification of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu Zhang and David Kinniburgh Alberta Centre for Toxicology Alberta Health & Wellness University of Calgary Calgary, Alberta Canada Application Note Environmental Abstract Detection, characterization, and tentative identification of very low levels of unknown microcystins in lake water are possible in the absence of analytical stan- dards using a combination of triple quadrupole LC/MS and LC/Q-TOF analysis and a Personal Compound Database (PCD) compiled from the Word Health Organization (WHO) list of microcystins.

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Page 1: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

Identification of UnknownMicrocystins in Alberta Lake Water

Authors

Ralph Hindle

Vogon Laboratory Services Ltd.

Cochrane, Alberta

Canada

Xu Zhang and David Kinniburgh

Alberta Centre for Toxicology

Alberta Health & Wellness

University of Calgary

Calgary, Alberta

Canada

Application Note

Environmental

Abstract

Detection, characterization, and tentative identification of very low levels of

unknown microcystins in lake water are possible in the absence of analytical stan-

dards using a combination of triple quadrupole LC/MS and LC/Q-TOF analysis and a

Personal Compound Database (PCD) compiled from the Word Health Organization

(WHO) list of microcystins.

Page 2: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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Figure 1. General microcystin (MC) structure.

O

CH3

CH3

CH2

CH3

CH3 H3C

H3C

NHNH

NHHN

HO

HO

OC

C

O

N

O

O

OO

R4

R2

O

Mdha7Glu6

Adda5 Ala1

MeAsp3

General microcystin structure

Position Abbreviation Amino acid

R1 Ala1 Alanine

R2 Leu2 (L) Leucine

R3 MeAsp3 Methylaspartic acid

R4 Arg4 (R) Arginine

R5 Adda5 3-amino-9-methoxy-2,6,6-trimethyl-10-phenyldeca-4(E),6(E)-dienoic acid

R6 Glu6 Glutamic acid

R7 Mdha7 N-methyldehydroalanine

Table 1. Eight Microcystins Surveyed in Alberta Lakes*

Microcystin R2 R4 Formula Neutral mass

LR Leucine Arginine C49H74N10O12 994.5488

Desmethyl LR Leucine Arginine C48H72N10O12 980.5331

RR Arginine Arginine C49H75N13O12 1037.5658

YR Tyrosine Arginine C52H72N10O13 1044.5280

LA Leucine Alanine C46H67N7O12 909.4848

LW Leucine Phenylalanine C54H72N8O12 1024.5270

LF Leucine Tryptophan C52H71N7O12 985.5161

HtyR Homotyrosine Arginine C53H74N10O13 1058.5437

*See Figure 1 for the general microcystin structure

Introduction

The occurrence of cyanobacterial toxins in Canadian freshwaters is a serious environmental and public health concern[1]. Microcystins (MCs) are a class of common cyanobacterialtoxins present in Canadian lakes, and they are potentinhibitors of eukaryotic protein phosphatases [2].Microcystins are also powerful hepatotoxins, and may pro-mote tumor development in mammals, presenting a seriousthreat to livestock and human drinking water sources. Thesecyanobacterial toxins have been detected in every province inCanada, often at levels above maximum guidelines for recre-ational water quality [2].

The MCs are cyclic peptides containing seven amino acids.They have the general structure shown in Figure 1. Table 1gives the chemical structures for eight microcystins surveyedin Alberta lakes. The most frequently reported MC is LR, containing leucine and arginine at positions R2 and R4,respectively.

The Alberta Centre for Toxicology (ACFT) conducted a com-prehensive study of microcystins in Alberta lakes, and it con-tinues to monitor fresh water sources using liquid chromatog-raphy and triple quadrupole mass spectrometry. While thismethod tests for eight microcystins, a nontargeted compoundwas also detected in a sample with the same transition quali-fier ion as MC YR (m/z 1045), but it had an incorrect retentiontime (RT) and qualifier ion ratio.

This application note describes two methods developedthrough a collaboration between Alberta Centre forToxicology (ACFT) and Vogon Laboratory Services to providesensitive detection of a wide range of microcystins andestablish the identity of this newly observed compound. Aconfirmation method was first developed using an Agilent1290 Infinity LC System and an Agilent 6460 TripleQuadrupole LC/MS, with a different retention time patternfrom the reference ACFT method. Accurate mass determina-tion on an Agilent 6540 Q-TOF LC/MS system was then usedto provide tentative identification of the unknown peak asdesmethylated microcystin HtyR.

All microcystins were detected at 0.1 ng/mL, which is wellbelow the 2007 Canadian Drinking Water Guideline of 1.5 µg/L.Using a Personal Compound Database (PCD) of 52 compoundscreated in the Agilent MassHunter software suite from theWorld Health Organization (WHO) list of microcystins, the Q-TOF data enabled the tentative identification of an additionalseven microcystins.

Page 3: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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Analysis parametersThe 6460 Triple Quadrupole LC/MS multiple reaction monitoring (MRM) analysis parameters are shown in Table 3.

Experimental

InstrumentsThe confirmation method was developed on an Agilent 1290Infinity LC System equipped with an Agilent G4226AAutosampler and coupled to an Agilent 6460 Triple QuadrupoleLC/MS System. The instrument conditions are listed in Table 2.

The method for tentative identification of unknown micro-cystins was developed on a 1290 Infinity LC system equippedwith a G4226A Autosampler and coupled to an Agilent 6540BQ-TOF LC/MS System with Jet Stream electrospray source.The instrument conditions are listed in Table 2.

LC conditions

Column Agilent Poroshell SB-C18, 3.0 × 100 mm, 2.7 µm(p/n 685975-306)

Column temperature 50 °CInjection volume 20 µLMobile phase A) 1 mM ammonium fluoride in water (HPLC grade)

B) 20% isopropanol in acetonitrile (LC/MS grade)Autosampler temperature 5 °C

Flow rate 0.6 mL/min

Gradient Time (min) % B

0 203.0 305.0 506.0 100

Stop 7 minutes

Post time 2 minutes

Triple quadrupole MS conditions

Ionization mode ESI with Agilent Jet Stream Technology

Drying gas temperature 350 °C

Drying gas flow 12 L/min

Nebulizer pressure 40 psig

Sheath gas temperature 400 °C

Sheath gas flow 11 L/min

Capillary voltage 4,000 V

Nozzle voltage 1,000 V

EMV 400 V

Q-TOF MS conditions

Mode Targeted MS/MS

Acquisition Profile and centroid; 2 GHz

Range 100–1,700 amu

Acquisition rate (MS) 3 scans/s

Acquisition rate (MS/MS) 1 scan/s

Reference masses 121.0509 and 922.0098

Table 2. LC and Triple Quadrupole MS Run Conditions

Table 3. MRM Analysis Parametersa for the Target Compounds Using aTriple Quadrupole LC/MS

MicrocystinPrecursorb

(m/z)Product ion (m/z)

Collision energy(V)

LR 995.6135.2 80

213.2 80

Desmethyl-LR 981.5135.2 80

213.2 80

RR 520.0135.2 30

213.2 40

YR 1045.5135.2 80

213.2 70

LA 910.5135.2 70

213.2 70

LY 1002.5135.2 80

213.2 70

LW 1025.5135.2 80

213.2 60

LF 986.5135.2 70

213.2 50

HtyR 1059.5135.2 80

213.2 70

a The fragmentor and cell acceleration voltages were 150 V and 2 V, respectively, for alltransitions.

b All precursors are singly charged, except RR which is doubly charged.

Sample preparationWater samples (10 mL) were taken through threefreeze/thaw cycles, then sonicated for 5 minutes, followed byfiltration through 0.2-µm cellulose filters directly intoautosampler vials.

Page 4: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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Lowest level calibrator

0.1 µg/L for YR, LR, and RR0.2 µg/L for all others

Calibrator near DW guidelines

0.9 µg/L for YR, LR, and RR1.9 µg/L for all others

Figure 2. Example total ions chromatograms (TICs) for nine microcystins at concentrations approximately 10% (A) and 100% (B) of the CDWG of 2007.

1.0×102

×101

×101

×101

×101

×102

×102

×102

×102

0.5

0.51.0

0.5

1.0

2.50

5.0

6

6

6

54

42.0 2.2 2.4 2.6 2.8

2.28A B

2.38

2.70

2.82

2.97

2.98

3.50

4.37

4.51

3.0 3.2 3.4Acquisition time (min)

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

3.6 3.8 4.0 4.2 4.4 4.6

4

1

64

5.0×102

×102

×102

×102

×102

×103

×102

×103

×102

02.5

0.50

1.0

05

0

5

20

4

2.55.0

2

2

0

0

02.0 2.2 2.4 2.6 2.8

2.24YR

HtyR

LR

dm-LR

LA

RR

LY

LW

LF

2.33

2.61

2.78

2.90

2.97

3.45

4.36

4.50

3.0 3.2 3.4Acquisition time (min)

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

Cou

nts

3.6 3.8 4.0 4.2 4.4 4.6

420

Results and Discussion

Identifying an unknown microcystinOne sample analyzed using the ACFT method revealed a com-pound with the same transition and qualifier ion asYR (m/z 1045), but at the wrong retention time (RT) and quali-fier ion ratio. It was tentatively identified as desmethyl-HtyR,based on the loss of 14 amu from HtyR (m/z 1059).

To confirm the identification of this unknown MC, a triplequadrupole LC/MS confirmation method was developed,which provided a different retention time pattern from the ref-erence ACFT method. Additional microcystin analytes wereadded to the method to help characterize compounds. Finally,samples were also analyzed using an LC/Q-TOF method toconfirm the identity of the unknown compound.

Confirmation methodThe triple quadrupole LC/MS confirmation method was opti-mized to provide a minimum detection level at approximately10% of the Canadian Drinking Water Guidelines (CDWG),which is 1.5 µg/L, based on MC LR. The lowest level calibra-tors used for the method were 0.1 µg/L for MCs YR, LR, andRR, and 0.2 µg/L for all others. Figure 2 illustrates the com-plete separation achieved for nine MCs with the high perfor-mance liquid chromatography (HPLC) chromatographicmethod at both the lowest calibrator levels and calibratorlevels near the CDWG.

Page 5: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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Quantitation calibration coefficients (R2) were excellent, rang-ing from 0.9978 to 0.9995 for the six MCs using a minimumcalibrator level of 0.2 µg/L and a maximum calibrator level of50 µg/L (Table 4). The R2 values ranged from 0.9992 to 0.9997for the three MCs using a minimum calibrator level of 0.1 µg/L and a maximum calibrator level of 25 µg/L. A repre-sentative calibration curve for MC LR is shown in Figure 3,illustrating excellent linearity even at extremely low concen-trations. Accuracy ranged from 84% to 121% for the six MCswith a minimum calibrator level of 0.2 µg/L, and 110% to119% for the three MCs with a minimum calibrator level of 0.1 µg/L (Table 4).

Analyzing the unknownUsing the confirmation method to analyze the unknown MCfrom an Alberta lake water sample showed a peak with thesame transition and qualifier ions as YR, but with an RT of1.91 minutes, rather than 2.24 minutes. The qualifier ion ratio(m/z 213.2/135.2) was also too low to be YR (2% versus24%). The low abundance of the m/z 213.2 peak indicatespossible desmethylation of the N-methyldehydroalanine(Mdha) moiety in the YR structure. Unfortunately, desmethylHtyR is not commercially available. Therefore, Q-TOF for accurate mass analysis was used to further confirm thedesmethylation hypothesis.

Table 4. Calibration Coefficients and Accuracy of Recovery

Calibration range MC R2 Accuracya (%)

0.2 to 50 µg/L

Hty R 0.9995 95

Desmethyl-LR 0.9993 84

LA 0.9988 121

LY 0.9998 92

LW 0.9989 118

LF 0.9978 119

0.1 to 25 µg/L

YR 0.9993 118

LR 0.9997 110

RR 0.9992 119

a Quantitative accuracy is listed for calibrator 1 (0.1 or 0.2 µg/L)

1.2

×105

1

0.8

Res

pons

es

0.6

0.4

0.2

0

33.5

4×103

2.52

Res

pons

es

1.51

0.50

0 2 4 6 8 10 12Concentration (ng/mL)

14 16 18 20 22 24 26

0 0.1 0.2 0.3 0.4 0.5 0.6Concentration (ng/mL)

0.7 0.8 0.9 1

Expanded range from 0.10 to 0.92 µg/L

Figure 3. A calibration curve for MC LR using three-fold serial dilutions from 0.1 to 25 µg/L, including the expanded range from 0.10 to 0.92 µg/L, to illustrateexcellent linearity.

Page 6: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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LC/Q-TOF analysisThe accurate mass determined for the precursor ion for theunknown MC using liquid chromatography/Q-TOF MS (LC/Q-TOF) was 1059.5500, which matches the actual mass fordesmethylated HtyR with a mass error of 5.0 ppm. This furthersupports the hypothesis that the unknown is formed by the

YR

Unknown microcystin

×103

1.4

1.2

1.0

0.8

0.6

0.4

0.2

0

×103

1.41.6

1.21.00.80.60.40.2

134.8 135 135.2 135.4 135.6 135.8 136

135.079814,079

135.115814,383

136.076111,504

136.118813,258

136.0821136.118514,569

137.078314,237

135.079513,998

135.115714,372

Mass-to-charge (m/z)

Cou

nts

Cou

nts

136.2 136.4 136.6 136.8 137 137.2 137.40

O

CH3

CH3

CH2

CH3

CH3 H3C

H3C

NHNH

NHHN

HO

HO

OC

C

O

N

O

O

OO

Z

X

O

O

CH3

CH3

CH2

CH3

CH3 H3C

H3C

NHNH

NHHN

HO

HO

OC

C

O

N

O

O

OO

Z

X

O

135.0804 = C9H11O+

135.1168 = C10H15+

The two Adda ions formed from allmicrocystins during analysis MS.

Figure 4. The two ions derived from the Adda group and characteristic of all microcystins are present and well separated in both YR and the unknown microcystin, using LC/Q-TOF.

desmethylation of HtyR. Examination of the transition ionsreveals that both the unknown and YR contain the two m/z 135nominal mass ions characteristic for microcystins (Figure 4).The actual masses of the two ions are 135.0804 and 135.1168,formed by different fragmentation patterns of the Adda group.Both ions are well separated in both microcystins at mass resolution 14,000.

Page 7: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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However, the m/z 213 ion formed from cleavage of the Glu +Mdha groups from the microcystins is present as expected inMC YR, but present at only trace levels in the unknown MC(Figure 5). This indicates that the unknown MC is not YR.Desmethylation of the Glu + Mdha group would be expected toproduce an ion with an accurate mass of 199.0713 (Figure 6).This ion is observed in the spectra from the unknown MC, butnot in the spectra of MC YR. These results also support thehypothesis that the unknown MC is dm-HtyR.

A previous structural LC/MS/MS characterization of micro-cystins had identified eight major ions designated a-h [3]. Twoof these, ions f and h, can be used to confirm the identity ofthe unknown MC. Ion f contains the R7 and R2 moieties(Figure 1), which should be dm-Mdha (Dha) and Hty, respec-tively for the microcystin dm-HtyR. Ion h contains the R2

moiety, as well as a second possible desmethylation site,MeAsp3. Depending on the identities of R7 and R2 and thepresence or absence of desmethylation at position R3, theaccurate masses of these two ions will vary and be diagnosticof the microcystin structure.

YR

Unknown microcystin

O

CH3

CH3

CH2

CH3

CH3

H3C

H3C

NHNH

NHHN

HO

HO

OC

C

O

N

O

O

OO

R4

R2

O

Glu6 + Mdha7 = C9H

13N

2O

4+

m/z = 213.0870

×102

6

5

4

3

2

1

0

Cou

nts

×102

6

5

4

3

2

1

0

Cou

nts

212 212.2 212.4 212.6 212.8 213.0 213.2

213.1322

213.0862

213.1342 214.0899

Mass-to-charge (m/z)213.4 213.6 213.8 214 214.2 214.4

Figure 5. Q-TOF spectra of YR and the unknown microcystin in the m/z range from 212 to 214.4. The m/z 213 ion characteristic of the Glu + Mdha group is present in microcystin YR but at low abundance in the unknown MC.

Desmethylation of Glu6 + Mdha

C8H11N2O4 + fragment ion from[Glu6 + Mdha7 − CH2] will haveaccurate mass 199.0713

YR2.5

2.0

1.5

1.0

0.5

0

Unknown microcystin

×102

2.5

2.0

1.5

1.0

0.5

198 198.5 199 199.5 200

200.1130

201.0982

200.1129

201.0969

198.1221

199.0695

200.5 201 201.5 202 202.50

×102

Mass-to-charge (m/z)

Cou

nts

Cou

nts

Figure 6. Q-TOF spectra of YR and the unknown microcystin in the m/z range from 198 to 202. Them/z 199 peak is present in the unknown microcystin, indicating desmethylation of the Glu + Mdha group. This peak is not present in YR.

Page 8: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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Analysis by Q-TOF of ion f in the unknown microcystinrevealed accurate masses that confirmed the presence of Dhaat position 7 and Hty at position 2, consistent with the identi-fication of the unknown as dm-HtyR. Analysis of the HtyRstandard also gave the correct accurate mass for ion f (Figure 7).

Unknown microcystin

Sequence for Ion f: R7_Ala1_R2_MeAsp3_Arg4

� Structure of MC HtyR:

���

HtyR

R7 = Mdha; R2 = HtyCalc m/z: 617.3042Measured: 617.3059 (2.8 ppm mass error)

� Proposed structure (dm-HtyR) for the unknown compound,with desmethylation of Mdha7 to Dha7:

���

R7 = Dha; R2 = HtyCalc m/z: 603.2885Measured: 603.2884 (0.2 ppm mass error)

2.50

2.0

1.50

1.0

0.50

198 198.5 199 199.5 200

620.3135603.2884

617.3059

200.5 2010

0.75

0.25

1.25

1.75

2.25

×102

Mass-to-charge (m/z)

Cou

nts

1.0

0.8

0.6

0.4

0.2

0

0.3

0.1

0.5

0.7

0.9

×103

Cou

nts

Figure 7. Q-TOF spectra of ion f for HtyR and the unknown microcystin. The accurate mass for the f ion observed in HtyR (upper)matched the calculated mass for the ion containing Hty at position 7 and Mdha at position R3. In contrast, the mass observedfor ion f in the unknown MC matched the calculated mass for the ion containing Hty at position 7 and Dha at position R3.

Page 9: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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The spectra of the h ion confirmed that minimal desmethyla-tion is occurring in the R3 position in the unknown MC, as itsaccurate mass matched the calculated mass for methylatedaspartic acid in position 3, in both the unknown and the HtyRstandard (Figure 8).

����

���

Sequence for Ion h: Ala1_R2_MeAsp3_Arg4

Structure of MC HtyR:

R2 = HtyCalc m/z: 534.2671Measured: 534.2692 (2.3 ppm mass error)

Proposed structure (dm-HtyR) for the unknown compound,with no desmethylation at position 3:

R7 = HtyCalc m/z: 534.2671Measured: 534.2683 (4.0 ppm mass error)

6

5

2

1

520 522 526 528 530

529.2782526.2295

520.3068

534.2683

534.2692

520.2560525.2403

530.2872

532 5360

3

4

×101

524 534Mass-to-charge (m/z)

Cou

nts

3.5

2.5

2.0

1.0

0

1.5

0.5

3.0

4.0

×102

Cou

nts

Figure 8. Q-TOF spectra of ion h for HtyR and the unknown microcystin. The accurate mass for the h ion observed in both HtyR(upper) and the unknown MC matched the calculated mass for the ion containing Hty at position R7 and Mdha at positionR3. In contrast, only a very small peak was observed at nominal mass m/z 520 in both microcystins, indicating that little orno desmethylation was occurring at position R3.

Page 10: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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Lake A

2.0

1.0

4.0

4.1738,163

4.5942,731

4.74422,076

4.97548,460

4.2424,156

4.661,853,141

4.6936,788

4.84653,497

5.1223,535

0

1.5

0.5

2.53.03.54.04.55.05.56.06.57.07.5

×105

4.1 4.2 4.3 4.4 4.5 4.6 4.7 4.8 4.9 5.0 5.1 5.2 5.3Acquisition time (min)

Cou

nts

Figure 9. Extracted ion chromatograms of a water sample from Lake A, and a table including retention time (RT), compound name, calculated m/z, and differ-ence of the calculated mass from the theoretical mass for each unknown tentatively identified using the Find by Formula tool in MassHunter and thepersonal compound database (PCD) created for the microcystins in the WHO list. A mass tolerance of 5 ppm and a minimum match score of 70 wereused to make the identification of H+ adducts.

RT Compound name Formula m/z Area Score Mass diff (ppm)*

4.66 MC-YR C52 H72 N10 O13 1045.5346 1,853,141 98.5 -0.7

4.69 MC-LR C49 H74 N10 O12 995.5549 36,788 90.4 -0.1

4.74 MC-HtyR-DAsp3-Dha7 C51 H70 N10 O13 1031.5185 422,076 96.8 -0.7

4.76 MC-HtyR C53 H74 N10 013 1059.5501 94,974 98.4 -0.3

4.84 MC-DesMe-LR C48 H72 N10 O12 981.5405 653,497 99.1 -0.1

4.97 MC-HphR-Dha7 C52 H72 N10 O12 1029.5400 548,460 99.6 -0.2

4.99 MC-LR-DAsp3-Dha7 C47 H70 N10 O12 967.5236 116,668 94.3 -1.5

4.99 MC-LR C49 H74 N10 O12 995.5559 32,185 92.7 -0.6

*Mass difference determined by subtracting the theoretical mass of the compound from the calculated mass derived from the Q-TOF analysis, expressed in ppm.

Using a Personal Compound Database to identifymultiple unknown microcystinsThe accurate mass capabilities of the Q-TOF can be used totentatively identify other microcystins that may be present inAlberta lakes, based only on the mass of their H+ adducts.The first step in the process is to build a Personal CompoundDatabase (PCD) using the Agilent MassHunter PCDL ManagerSoftware, which enables the user to create and edit a cus-tomizable PCD, including compounds, accurate-mass, andretention time information. One of the advantages of accuratemass scan data is the ability to retrospectively searchacquired data for new compounds using such a database.

In this study, the WHO list of microcystins [4] was used toenter the formulas for 52 microcystins into a PCD, which gen-erates accurate masses for the H+ adducts. The Find byFormula tool in MassHunter was then used to search forthese accurate masses in the sample total ions chromatogram(TIC) data file. Using this process with the Q-TOF, sevenunknowns were tentatively identified in samples from Lake Aand Lake B, in addition to the desmethyl HtyR (Figures 9 and10). Additional analysis by Q-TOF MS/MS and comparison toanalytical standards is needed to confirm the presence andidentity of these MCs. Work is on-going to develop an exact-mass calculator model to help identify nontargeted MCs and their variants.

Page 11: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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Conclusion

When analytical standards are available, the Agilent 1290Infinity LC System and an Agilent 6460 Triple QuadrupoleLC/MS provides an excellent platform for the targeted analy-sis of microcystins. Analysis by triple quadrupole LC/MSusing the Agilent 6540 Q-TOF LC/MS System can confirmsuspect compounds using the accurate mass of the molecularion adducts, as well as MS/MS fragments. The combination

of these two technologies supported the hypothesis thatdm-HtyR was present in an Alberta lake water sample.Databases can be compiled using the Agilent MassHunterPCDL Manager Software to include the chemical formula foradditional microcystins based on reported analogues in theliterature. Using MassHunter Find by Formula, previouslyacquired data files can be retrospectively searched againstPCDL databases and libraries for these additional compoundsas they become known.

Lake B

0.4

0.2

4.0

4.131,200,312

4.93425,603

4.30468,450

4.5017,615

4.663,048,472

4.813,720,594

5.0638,769

0

0.6

0.8

1.0

1.2

1.4

1.6×106

4.1 4.2 4.3 4.4 4.5 4.6 4.7 4.8 4.9 5.0 5.1 5.2 5.3 5.4Acquisition time (min)

Cou

nts

RT Compound name Formula m/z Area Score Mass diff (ppm)*

4.13 MC-HtyR-DAsp3-Dha7 C51 H70 N10 O13 1031.5193 1,200,312 99.5 -0.4

4.30 MC-LR-DAsp3-Dha7 C47 H70 N10 O12 967.5246 468,450 99.7 -0.3

4.50 MC-LR-DAsp3-Dha7 C47 H70 N10 O12 967.5256 17,615 86.4 0.7

4.66 MC-HtyR-DAsp3-ADMAdda5-Dhb7 C53 H72 N10 014 1073.5305 3,048,472 99.4 0.4

4.68 MC-LR C49 H74 N10 O12 995.5549 18,836 97.7 -1.1

4.81 MC-LR-DAsp3-ADMAdda5-Dhb7 C49 H72 N10 O13 1009.5359 3,720,594 99.6 0.5

4.93 MC-LY C52 H71 N7 O13 1002.5181 425,603 99.4 -0.3

5.06 MC-LR-ADMAdda5 C50 H74 N10 O13 1023.5505 38,769 95.9 -0.6

*Mass difference determined by subtracting the theoretical mass of the compound from the calculated mass derived from the Q-TOF analysis, expressed in ppm.

Figure 10. Extracted ion chromatograms of a water sample from Lake B, and a table including retention time (RT), compound name, calculated m/z, and differ-ence of the calculated mass from the theoretical mass for each unknown tentatively identified using the Find by Formula tool in MassHunter and thepersonal compound database (PCD) created for the microcystins in the WHO list. A mass tolerance of 5 ppm and a minimum match score of 70 wereused to make the identification of H+ adducts.

Page 12: Identification of Unknown Microcystins in Alberta … of Unknown Microcystins in Alberta Lake Water Authors Ralph Hindle Vogon Laboratory Services Ltd. Cochrane, Alberta Canada Xu

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References

1. B.G. Kotak, A.K.-Y. Lam, E. E. Prepas, and S.E. Hrudey.“Role of chemical and physical variables in regulatingmicrocystin-LR concentration in phytoplankton ofeutrophic lakes.” Can. J. Fish. Aquat. Sci. 57, 1584–1593(2000).

2. D. M. Orihel, D. F. Bird, M. Brylinsky, H. Chen, D. B. Donald,D. Y. Huang, A. Giani, D. Kinniburgh, H. Kling, B. G. Kotak,P. R. Leavitt, C. C. Nielsen, S. Reedyk, R. C. Rooney, S. B.Watson, R. W. Zurawell, and R. D. Vinebrooke. ” Highmicrocystin concentrations occur only at low nitrogen-to-phosphorus ratios in nutrient-rich Canadian lakes.” Can. J. Fish. Aquat. Sci. 69, 1457-1462 (2012).

3. T. Mayumi, H. Kato, S. Imanishi, Y. Kawasaki,M. Hasegawa, K. Harada. “Structural characterization ofmicrocystins by LC/MS/MS under ion trap conditions.”J. Antibiot (Tokyo) 59, 710-719 (2006).

4. I. Chorus and J. Bartram (Eds.). “Toxic Cyanobacteria inWater—A Guide to Their Public Health Consequences,Monitoring, and Management. E & FN Spon, published onbehalf of the World Health Organization, New York (1999).

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