Use of External Radical Sources in Flash Vacuum Pyrolysis
1341
ppm downfield from tetramethylsilane with deuterochloroform
(d 77.16) as a secondary reference. Analysis and integration of
1H and 13C NMR spectra was accomplished using MestreC
NMR software. Preparative thin layer chromatography was
performed on 20 cm ꢂ 20 cm Analtech Uniplate Taper plates,
Alumina GF. For column chromatography, silica gel 32–63 mm
was used. Gas chromatography–mass spectrometry (GCMS)
analysis was performed on a Thermo Finnigan Trace DSQ
with electron impact ionization with a Restek Rtx-PCB
(30 m ꢂ 0.25 mm ꢂ 0.25 mm film) column, and GC integrations
were accomplished using the Avalon integration program. High-
resolution mass spectrometry (HRMS) was performed by the
Mass Spectrometry Center, Boston College. All FVPs were
done according to the procedure developed by Necula and
Scott.[13] To ensure an accurate view of the product distribu-
tions limited purification was done on each sample. Typically
samples were passed through a silica gel plug with dichlor-
omethane as the eluent. Following the plug, samples were
concentrated under reduced pressure and dried under high
vacuum. These purifications provided better 1H NMR spectra,
however they did not remove higher molecular weight soluble
polymers that were created during the pyrolysis and in some
cases led to mass recoveries greater than 100 %.
N2-solvent vapour
ϩ
1100ЊC, 0.67–1.33 hPa
10
11
13
12
Scheme 7. Pyrolysis of benzo[c]phenanthrene (10) with various solvents,
at a temperature of 11008C and 0.67–1.33 hPa.
Table 4. Pyrolysis of benzo[c]phenanthrene (10) with various solvents
Solvent
10A
11A
12A
13A
Hexanes
53 %
81 %
63 %
69 %
58 %
32 %
19 %
27 %
25 %
29 %
11 %
0 %
4 %
0 %
1 %
2 %
2 %
Dichloromethane
Nitromethane
10 %
4 %
Trimethyl orthoformate
Methyl tert-butyl ether
11 %
AThe percent product ratios were calculated from the integration of known
signals for 10, 11, 12, and 13 in the 1H NMR of the crude pyrolysate of each
reaction.
External Radical Source Introduction Method
The introduction of an external radical source was accomplished
by splitting the nitrogen carrier gas into two streams that were
regulated by flow meters. One flow meter was used for pure
nitrogen gas, and the other regulated the flow of nitrogen gas
through two reservoirs of the solvent used as the radical gen-
erator, connected in series. The pure nitrogen gas stream and the
stream carrying the external radical source were combined and
used as the carrier gas for FVP. The amount of solvent in the
carrier gas (reported in mol-%) was determined by capturing the
solvent vapours in a liquid nitrogen cooled trap over a period of
time. The solvent was removed, and its volume was measured to
provide a lower limit for the amount of solvent per unit time. The
Scienceware flow meters were calibrated to supply 961 mL
minꢁ1 of gas at a reading of 20 mm. Knowing both the volume of
nitrogen gas and the amount of solvent collected per unit time,
the mole fractions were calculated, assuming 24.47 L molꢁ1 for
nitrogen gas. The design of this setup also allowed for per-
turbations to be made to the apparatus. These had a direct affect
on the amount of solvent vapour in the gas phase (i.e. 1 chamber,
2 chambers, and with or without sparging), and all perturbations
used in our study were calibrated. To determine the effective-
ness of this procedure, we examined the ratio of products to
starting material by the integration of the signals in the chro-
matogram of the GCMS or by the integration of known
356 kJ molꢁ1).[41,53] The substrate chosen for this solvent screen
was benzo[c]phenanthrene (10) (Scheme 7), as this substrate
will not suffer the loss of appended phenyl or naphthyl groups
that o-terphenyl (4) and 1,10-binaphthyl (7) can. The results of
this study are summarized in Table 4.
Each solvent did act as a radical generator in FVP to a varying
extent, with methyl tert-butyl ether having the best products to
starting material distribution among the four new solvents
tested, with 11 being produced in 29 % yield. The best ratio of
10 to 11 was obtained using dichloromethane, but this result is
deceiving, as the pyrolysis of dichloromethane produced
HCl, which likely caused the polymerization of cyclopenta
[cd]pyrene (12). We have demonstrated that all four solvents
studied can be used as external radical sources, with hexanes and
methyl tert-butyl ether providing the best results.
Conclusions
The use of external radical sources in FVP has been a successful
venture, and this new technique shows great promise. We
have shown that the introduction of an external radical source
can greatly increase the reactivity of usually inert PAHs such as
o-terphenyl (4) and benzo[c]phenanthrene (10) at 11008C.
Hexanes were used extensively throughout this study, but our
work has shown that other solvents such as dichloromethane,
methyl tert-butyl ether, nitromethane, and methyl orthoformate
all have the ability to generate radicals at high temperatures and
facilitate the cyclodehydrogenation of PAHs.
1
signals in H NMR of the crude pyrolysate. The calibration
data and all spectra for each experiment are provided in the
Supplemental Material.
General Procedure for the FVP of o-Terphenyl (4)
With and Without an External Radical Source
Experimental
Flash vacuum pyrolysis was performed on 100 mg (0.435 mmol)
of o-terphenyl (4) at 11008C with a steady flow of carrier gas
with a composition of 0–12.2 mol-% hexanes vapour in the
nitrogen gas (final pressure 0.67–1.33 hPa) over 4–6 h utilizing
one or two reservoirs and with or without sparge. The pyrolysis
was accomplished in a quartz tube (length ¼ 105.4 cm and int-
erior diameter ¼ 3.4 cm), in an electric oven (length ¼ 61 cm).
General Experimental Procedures
All solvents and commercial chemicals were used without
purification, unless otherwise stated. Proton NMR chemical
shifts are reported in ppm downfield from tetramethylsilane
with deuterochloroform (d 7.26) as a secondary reference,
unless otherwise specified. Carbon NMR shifts are reported in