Upload
elizabeth-gibson
View
212
Download
0
Embed Size (px)
Citation preview
MATERIALS AND METHODS
In order to find the determining factors in the migration process 4 assays were carried out.
Assay design table:
Static: Water remains still in pipe.Open Dynamic: Fresh treated water runs through pipe.
All pipes were brand new, set in dark isothermic room.
Pipes used in STATIC Flow Mode:-HDPE: Internal diameter: 90 mm
Length: 2,1m Internal Volume: 13,35 l Contact
area: 5,9 m2
-LDPE: Internal diameter: 45,8 mm Length: 8,1m
Internal Volume: 13,35 l Contact area: 11,6 m2
Pipes used in open DYNAMIC Flow mode:-HDPE: Internal diameter: 90 mm
Length: 2 m Water flow: 0,8 m/s Contact
area: 5,6 m2
-LDPE: Internal diameter: 45,8 mm Length: 2 m
Water flow: 0,9 m/s Contact area: 2,9 m2
POTENTIAL WATER MIGRATION OF ORGANIC COMPOUNDS FROM
POLYETHYLENE (PE) PIPES. ANALYSIS BY CLSA AND GC/MS M. Om, M. Cortina, J. Caixach* and J.
RiveraLaboratori d’Espectrometria de Masses, Dept. d’Ecotecnologies, IIQAB-CSIC, Jordi Girona 18-26, 08034 Barcelona.
C. de Ciurana, X. BallellLaboratori d’Aigües de Girona, Salt i Sarria de Ter S.A.ETAP Montfullà, 17162 Bescanó Girona.
INTRODUCTION
Polyethylene pipes (PE) are widely used in treated water distribution services. Migration of low molecular weight compounds from PE into the treated water can change its final quality. This study was done to identify and quantify the migration compounds from two types of PE pipes; high density HDPE and low density LDPE polyethylene, under different conditions of temperature, time of contact and water flow.
RESULTS AND DISCUSSION
Low density polyethylene (LDPE) shows the highest migration potential at 40ºC; 8 times higher than the HDPE at 40ºC, and around 22 times over the LDPE at 14ºC. (Static Assays).
Compounds detected:
1. Among BHT degradation by-products (8 metabolites were detected); dm-BHT, ox-BHT and Quinona-BHT are found to be the major.
Mass Spectra related:
BHT CAS nº 128-37-0
dm-BHT CAS nº 128-39-2
Quinona-BHT CAS nº 719-22-2
2. Plastic manufacturing by-products such as aldehides, cetones and short-chain hidrocarbons and alkylbenzenes were also detected.These chemicals are susceptible to change water organoleptic quality giving taste and odor.
ACKNOWLEDGMENTS
The Authors wish to thank both Laboratories staff for their collaboration in this study.
REFERENCES 1.Productos Químicos Industriales, H.A,Wittcoff, B.G. Reuben: Vol 2.; Editorial Limusa, 1985.2. Plastics Additives Handbook, 3 rd Edition, R. Gächter and H. Müller Editors. Hanser Publishers, Munich, Viena New, York.3. A. Bruchet, C. Hochereau, Analysis, 25, M32-M34, 1997.4. J. Rivera et al., J.Chromatography, 562, 481-492, 1991.5. Standard Methods, 20 th Edition, 1998. Part 6000, 8-18 6040B.6. D.W Shorten, Food Chem., 8, 109-119, 1982.7. A. Hoff et al., Scand. J. Work Environ. Health, 8 (sup. 2) 3-27 1982.8. J. P. H. Linsen et al., Food Chemistry, 46, 367-371, 1993.9. S. Monarca et al., Food Chemistry Toxic., 32, 783-788,1994.10. B. Rindone et al., Water Research, 28, 1595-1600, 1994.11. S. rigal, J. Dasnjou, Water Sci. & Tech., 406, 203-208, 1999.12. M. van Leeuwen et al., Polym. Laminations Coat Conference, Vol 1, 229-237, 1998.
Assay Flow mode Temperature Contact time1 Static 40 ºC 72 h2 Static 14 ºC 8 h3 Open Dynamic 14 ºC 24 h4 Open Dynamic 14 ºC 11h, 5 h, 30 min
ANALYSIS
Identification and quantification were carried out using CLSA (Closed Loop Striping Analysis) extraction technique and Gas Chromatography coupled to Mass Spectrometry (MD-800 Thermo-Finnigan) using a 60 m J&W column (0,25 m film thickness) with “on Column” sample injection in electron impact ionisation mode (70 eV). Data was processed using Masslab software, Wiley 6th and NIST 98 libraries were used.
Acquired 22-Apr-1999 at 09:04:28Sample ID: LDPE1604
50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200 210 220 230 240 250 260 270 280 290 300m/z0
100
%
191
57
551639173
6560 6774 88
7911510710595
147128117 133 135 161175
164 176
206
192
193 207
9A22_1 4164 (55.529) Scan EI+ 4.18e6
Acquired 22-Apr-1999 at 09:04:28Sample ID: LDPE1604
50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200 210 220 230 240 250 260 270 280 290 300m/z0
100
%
177
67
5753
65
63
9177
6975
79
81 85
135
95121105
103107 133
149
136144
163159
151164
220
205178
192187 193206 221
9A22_1 4029 (53.729) Scan EI+ 8.50e4
Acquired 05-Jul-2001 at 09:38:21
50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200 210 220 230 240 250 260 270 280 290 300m/z0
100
%
205
57
5553 145918177676558 69 10595 115 119128
133 177161149
163 189178
220206
207 221
1JL5_2 390 (13.203) Scan EI+ 1.47e6