2570 J . Org. Chem., Vol. 65, No. 8, 2000
Notes
Sch em e 1
For either GC or NMR analyses, the difference in ROH
detected in reaction aliqouts before and after aqueous KI
treatment corresponds nicely with the levels of ROCl
observed directly by titrimetry and NMR.
Exp er im en ta l Section
Ma ter ia ls a n d Gen er a l P r oced u r es. All compounds em-
ployed were secured from commercial suppliers. Aqueous hy-
pochlorite (“5.25%”) was obtained in the form of commercial
Clorox bleach. In all cases, the phase-transfer catalyst (PTC)
used was tetrabutylammonium hydrogen sulfate (TBAHS). All
1H NMR spectra were recorded at 60 MHz. Gas chromatographic
(GC) instruments were equipped with capillary columns and
flame ionization detectors. The pH’s of aqueous layers of biphasic
systems were set and maintained at desired levels by addition
of aqueous NaOH or HCl, and the pH was monitored with pH
meters equipped with gel-filled plastic combination electrodes.
Progress of reactions was followed by GC using chlorobenzene
as an internal standard, which was shown to be stable to the
reaction conditions and to have retention times different from
both reactants and products. All reactions were conducted at
ambient temperatures.
Gen er a l Rea ction s of Ter tia r y Alcoh ols (Ta ble 1). Sub-
strate alcohols and chlorobenzene (2.5 mmol) were dissolved in
50 mL of CH2Cl2 and stirred magnetically with 100 mL (70
mmol) of hypochlorite adjusted to pH 8.8-9.3 and containing
0.20 g (0.59 mmol) of TBAHS. Reactions were conducted under
conventional fluorescent lighting and analyzed by GC to deter-
mine the types and percentages of products formed. Potassium
iodide (KI) workups were accomplished by treating a 0.5 mL
reaction aliquots with two drops of 1 M KI in 0.5 M HCl. Under
the comparable conditions, except with the aqueous phase pH
∼11 (maintained by addition of 5% aqueous NaOH), compounds
3 and 7 were found to be unreactive to bleach and TBAHS for 3
h and up to 3 days, respectively.
Ketone products from pH 9 reactions of substrates 5-7 were
isolated from two-phase systems that did not contain an internal
standard. After reactions had run for a minimum of 1 h, the
CH2Cl2 phase was extracted six times with water, poured
through fluted filter paper into a round-bottom flask, subjected
to rotary evaporation, and weighed. For 7-chloro-2-heptanone:
1H NMR (CCl4) δ 1.5 (br m 6H), δ 2.1 (s, 3H), δ 2.4 (t, 2H), δ 3.5
(t, 2H); 2,4-dinitrophenylhydrazone (DNP), mp 94-95 °C (lit.15
mp 95-96 °C). For 5-chloro-1-phenyl-1-pentanone: 1H NMR
(DCCl3) δ 1.6 (m, ∼4H), δ 2.7 (m, ∼2H), δ 3.4 (m, ∼2), δ 7.7 (m,
∼5H); DNP mp 176-178 °C, (lit.15 mp 76-178 °C). For 6-chloro-
1-phenyl-1-hexanone: 1H NMR (DCCl3) δ 1.6 (br m, 6H), δ 2.9
(t, 2H, J ≈ 6 Hz), δ 3.5 (t, 2H, J ≈ 6 Hz), δ 7.7 (m, 5H); DNP mp
139.5-141 °C (lit.15 mp 141.5-143 °C).
Rea ction s of 2-P h en yl-2-P r op a n ol(1). (a ) Rea ction in
CDCl3. An a lysis by 1H NMR (Ta ble 2). Compound 1 (0.134
g, 0.984 mmol), TBAHS (0.0191 g, 0.056 mmol), chlorobenzene
(0.0552, 0.590 mmol), and tert-butylbenzene (0.0645 g, 0.481
mmol) were dissolved in 10 mL of CDCl3. The solution was
stirred with 40 mL (28 mmol) of bleach at pH 9. At intervals,
aliquots of the organic layer were removed and analyzed by GC
and NMR. A 0.2 mL aliquot was added to 15 mL of reagent-
grade 2-propanol containing 2 mL of acetic acid and 0.25 g of
NaI. The iodine was titrated to a colorless endpoint with 0.01
M sodium thiosulfate. The concentrations of the following
compounds were determined from NMR by integration of the
appropriate methyl signal relative to that of tert-butyl benzene
(δ ) 1.33): 2-phenyl-2-propanol (δ ) 1.60), 2-phenyl-2-propyl
hypochlorite (δ ) 1.70), acetophenone (δ ) 2.60), and chlo-
romethane (δ ) 3.02). When a reaction aliquot was treated with
aqueous KI, the signal at δ ) 1.70 disappeared, and the signal
at δ ) 1.60 increased by a corresponding amount.
induced reactions of hypochlorite with tertiary alcohols
is suggested in Scheme 1, with Cl2O potentially playing
the role indicated.10
The stability of YZQCOCl prior to addition of the
catalyst is not unexpected. Although it is generally
accepted that alkyl hypochlorites undergo a rapid light-
catalyzed chain decomposition, Walling and J acknow
have shown that the chain reaction is inhibited by
oxygen.11 Evidently, in a system that has a relatively low
alkyl hypochlorite concentration and is not deoxygenated,
chain reactions may not occur unless the initiation rate
is substantially increased through the addition of the
phase-transfer catalyst.
The quaternary salt may function in the traditional
phase-transfer catalytic role, increasing concentration of
ionic species, particularly including hypochlorite ion
(OCl-), in the organic phase to serve as a participant for
several steps. Rationales for increased efficiency at pH
8-10 vs pH > 11 include the following: enhanced
formation of Cl2O, suggested as the active agent in other
phase-transfer reactions of aqueous hypochlorite;12,13
enhanced efficiency of coextraction of hypochlorous acid
along with hypochlorite by catalyst at pH near the pKa
(7.5-7.6) of HOCl;14 or by influencing efficiency of
competing reactions,12 including the chain length of
radical propagating processes.
It is very important that instability of alkyl hypochlo-
rites in nonaqueous solvents during GC analysis be
recognized. Heat-induced â-scission of alkyl hypochlorites
takes place readily in the inlet ports of gas chromato-
graphs (typically > 100 °C). This is made apparent if
duplicate aliquots of reaction mixtures are analyzed by
GC after one is treated with KI. Alkyl hypochlorites
present have been shown to react with KI and revert (be
reduced) to the corresponding alcohol. This has permitted
another way to estimates levels of alkyl hypochlorites.
(10) Chlorine monoxide is known to react with alcohols to form
ROCl; see: Anbar, M.; Ginsburg, D. Chem. Rev. 1954, 54, 925 and
references therein. Other radical species, such as chlorine atoms, also
may participate in chain propagation steps analogous to those shown
in Scheme 1.
(11) Walling, C.; J acknow, B. B. J . Am. Chem. Soc. 1960, 82, 6108.
(12) Fonouni, H. E.; Krishnan, S.; Kuhn, D. G.; Hamilton, G. A. J .
Am. Chem. Soc. 1983, 105, 7672.
(13) Dneprovskii, A. S.; Eliseenkov, E. V. Russ. J . Org. Chem. 1994,
30, 235.
(14) Abramovici, A.; Neuman, R.; Sasson, Y. J . Mol. Catal. 1985,
29, 291. The pKa of HOCl reported therein is 7.53; elsewhere it is cited
as 7.58.
After KI treatment, levels of 1 directly measured by GC
included, in addition to unreacted starting material, some alcohol
due to reduction of 8 by KI. Direct GC analyses of aliquots (no
KI treatment) resulted in significant thermal decomposition of
8. For Table 2 and Figures 1 and 2, concentrations of unreacted
starting material were determined by subtracting the titrimetri-
(15) Wilt, J . W.; Hill, J . W. J . Org. Chem. 1961, 26, 3523.