Background Image
Table of Contents Table of Contents
Previous Page  228 / 302 Next Page
Information
Show Menu
Previous Page 228 / 302 Next Page
Page Background

10

PAH

MDL

(ng/L)

RL

(ng/L)

Measured

Conc

(ng/L)

Measured

Conc

(ng/L)

Measured

Conc

in Fortified

Matrix

Experiment

(ng/L)

Fortification

Level

(ng/L)

% Recovery

Acenaphthene

15

45

-

-

203

176

115

Acenaphthylene

16

49

-

-

162

176

92

Antracene

29

86

-

-

185

176

105

Benz[

a

]anthracene

12

36

-

-

164

176

117

Benzo[

b

]

fluoranthene,

perylene

34

102

-

-

363

373

97

Benzo[

g,h,i

]

perylene

19

57

-

-

150

176

85

Benzo[

k

]

fluoranthene

21

63

-

-

219

176

124

Crysene

11

33

-

-

210

176

119

Dibenz[

a,h

]

anthracene

16

48

-

-

156

176

88

Fluoranthene

12

36

-

-

209

176

116

Fluorene

7.9

24

-

-

168

176

95

Indeno[1,2,3-

cd

]

pyrene

26

78

-

-

174

176

99

Naphthalene

20

60

-

-

161

176

91

C1-naphthalenes

13

40

-

-

364

353

103

C2-naphthalenes

15

44

-

<RL

228

176

118

Phenanathrene

19

57

-

-

175

176

99

Pyrene

17

50

-

-

200

176

111

Total PAH

0

0

% Recovery

Average

104±12

Table 4. Method performance upon analysis of reclaimed water obtained from the Miami-Dade North District Wastewater Treatment

Plant for US EPA priority PAHs.

Conclusion

An automated protocol for the comprehensive analysis of

28 parent PAHs and their extended alkylated homologues

by online SPE-LC-MS/MS was successfully developed

with optimized parameters for extraction, separation, and

detection using dopant-assisted APPI. Method

performance and the control of matrix effects were

demonstrated by obtaining good recoveries upon analysis

of seawater, reclaimed water, and rainwater runoff fortified

with certified standards, showing the utility of this method

to survey the occurrence of PAHs in waters at the urban

environment. A survey of PAH concentration in a seawater

environment influenced by a large urban area was

conducted, and although background concentrations were

below MDLs, localized PAH input events from boating

activities were detected above reporting limits. With lower

run times, very simple sample preparation, lower

generation of toxic solvent waste, and higher sensitivity

per volume of sample used, this method could represent a

viable alternative to LLE-GC-MS for routine PAH

monitoring, providing laboratories with a much higher

sample throughput while reducing overall operation costs

and the environmental impact of PAH analysis.