Background Image
Table of Contents Table of Contents
Previous Page  83 / 302 Next Page
Information
Show Menu
Previous Page 83 / 302 Next Page
Page Background

5

Thermo Scientific Poster Note

PN-64109-ASMS-EN-0614S

Conclusion

Quantitative results of PP

Semi-quantitative results,

PPCP by-products were o

Efforts to obtain analytical

References

1.

“The Determination of Em

Liquid Chromatography-T

Ministry of the Environme

laboratoryservicesbranch

2.

“Monitoring

the photoche

and sunlight using solid-p

M., Lores, M., García-Jare

65(8), pp. 1338-1347.

Acknowledgem

We would like to thank Dr. Vince

Ms. Renee Luniewski for providi

PPCPs

FIGURE 2. Overall effect of treatment temperatures

Semi-Quantitative Determination of PPCPs

In this presentation, TCS (antimicrobial agent) and CBZ (anticonvulsant drug) will be

used for the demonstration of by-product formation during wastewater treatment

processes. They are representative of pharmaceuticals and are the two most studied

groups of medicines. The effect of treatment temperatures and seasonal changes

were first investigated using principal component analysis. As shown in Figure 2,

scores for samples treated at 20

°

C (red, summer) and 55

°

C (brown, winter) were

similar; while scores for samples obtained from 35

°

C (green, winter) and standards

(blue) were quite different. An indication that treatment temperatures exerted more

effect on samples than seasonal changes.

Despite the vast number of TCS by-products proposed in the literature

2

, five

compounds (i.e., dichlorohydroxy-diphenyl ether, 2- and 4-chlorophenol (Cl-Ph),

methyl Triclosan (Me-TCS), and 4- and 5-chloro Triclosan, (Cl-TCS)). Semi-

quantitative concentrations of TCS, deuterium labelled TCS (TCS-D3), Cl-Ph, Cl-TCS

and Me-TCS are shown in Figure 3, indicating population of Cl-Ph were minimum

while other compounds reached their maximum at 35

°

C.

Concentration (ng/L)

Min

Max

Median

2.95E+02 2.52E+04 5.45E+03

6.96E+02 1.12E+04 2.52E+03

2.19E+02 1.81E+03 6.52E+02

1.75E+02 3.41E+03 6.48E+02

5.18E+01 9.29E+03 6.36E+02

4.56E+01 3.51E+02 1.27E+02

3.41E+01 3.24E+02 7.16E+01

1.16E+01 1.14E+02 3.12E+01

1.60E+03 2.80E+06 9.42E+03

3.52E+02 7.86E+05 8.03E+03

2.70E+00 2.08E+04 1.27E+03

1.91E+02 1.03E+03 4.33E+02

1.04E+01 1.27E+03 2.97E+02

2.07E+02 1.26E+05 3.30E+03

5.10E+00 1.64E+03 2.65E+02

7.89E+01 6.42E+03 1.62E+02

1.80E+00 1.43E+04 2.95E+02

4.64E+01 1.46E+03 2.75E+02

9.34E+02 5.76E+04 4.00E+03

2.69E+01 2.31E+04 6.57E+02

1.49E+01 1.25E+05 4.37E+03

urrence in the 35

25th-75th

Percentile

median

Standards

20

°

C, Sept 2012

35

°

C, Jan 2012

55

°

C, Jan 2013

Figure 3. Relative concentration of TCS and the three TCS by-products found

In comparison with other PPCPs

in this work. The unequivocal

challenge as many of these com

the same monoisotopic mass

reference standards, the chrom

structure with the most domin

concentrations of CBZ, deuteriu

found are shown in Figure 4.

Figure 4. Relative concentratio

Microsoft

®

and Excel

®

are trademarks of M

other trademarks are the property of Ther

Chemspider is a trademark of ChemZoo In

This information is not intended to encoura

intellectual property rights of others.