tubings leach organic constituents under either
cant losses of two VOCs from a test solution that
static or dynamic conditions. This is especially
was pumped through PTFE tubing but did not
true for flexible tubings such as PVC and various
quantify what those losses were. Only one study
(Devlin 1987) has addressed what happens to
types of rubber (e.g., black latex, silicone) (Cur-
analyte concentrations when the test solution is
ran and Tomson 1983, Barcelona et al. 1985). One
pumped through tubing for an extended period
reason some flexible products tend to leach or-
of time, i.e., whether equilibration occurs. Devlin
ganic constituents is that they contain large per-
(1987) reported that representative samples
centages of plasticizers. For example, flexible
could be obtained through 100-ft sections of PE
PVC contains 3050% plasticizers (by weight)
tubing after first flushing the tubing for 510
(Junk et al. 1974, Aller et al. 1989), while rigid
min, and that the equilibration time depended
PVC contains less than 0.01% (Barcelona et al.
upon the length of the tubing and the pumping
1984). In contrast, PTFE and other fluoropoly-
rate. However, Devlin did not provide any data
mers have been shown not to leach any organic
that showed this.
constituents (Junk et al. 1974, Curran and Tom-
Therefore, while we know that concentrations
son 1983, Barcelona et al. 1985). These materials
of some organic analytes can be affected when
do not contain plasticizers and generally do not
contaminated water is pumped through some
contain many additives.
tubings, we do not know the full extent of this
We (Parker and Ranney 1996) evaluated twen-
effect. Other unanswered questions include 1)
ty tubings for evidence of leaching after 24 and
72 hr, using reversed-phase high performance
achieved? 3) How long does it take to reach equi-
liquid chromatography (RP-HPLC) analysis and
librium? 4) What is the extent of loss at equilibri-
an ultraviolet (UV) detector. Some of the organic
um? and 5) Does flow rate affect the amount of
compounds were later identified by gas chroma-
tographymass spectrometry (GCMS). Among
the rigid tubings, we found that after 72 hours'
contact, several constituents had leached from
Leaching of organic constituents
Several studies (Junk et al. 1974, Curran and
the polyester-lined PVC and polyamide tubings
Tomson 1983, Barcelona et al. 1985, Parker and
(Table 2). In contrast, we were unable to detect
Ranney 1996) have shown that some polymeric
that any constituents had leached from the six
Table 2. Number of spurious peaks and possible identity (from
Parker and Ranney 1996).
Contact time
Material
1 hr
72 hr
Possible identity
Flexible tubings
plasticized PP1
1
1
not identified
plasticized PP2
0
0
PVC
3
8
hexacosane
TPE
1
4
hexanedioic acid, dioctyl ester
P(VDF-HFP)
1
1
not identified
polyurethane
5
12
hexanoic acid, 2-ethyl
fluoroelastomer
1
1
not identified
Rigid tubings
LDPE
0
0
XLPE
0
0
PE in EVA shell
0
0
PE x-linked EVA shell
0
0
Polyester-lined PVC
1
4
not identified
PP
1
1
hexanedioic acid, dioctyl ester
polyamide
2
9
benzene sulfonamide, N-butyl
PTFE
0
0
PFA
0
0
ETFE
0
0
PVDF
0
0
FEP
0
0
FEP-lined PE
0
0
4