Mahajan et al.
849
oxygenates from synthesis gas using homogeneous systems.
The use of transition-metal carbonyls especially those of Ru
(5) and Rh (6) for synthesis of methanol, ethanol, other
higher alcohols, and ethylene glycol is well documented for
synthesis gas conversion but with these systems the overall
reaction parameters are not economically attractive.
We previously reported (7) our approach to methanol syn-
thesis from synthesis gas that utilized base-activated nickel
tetracarbonyl as a catalyst for operation in homogeneous
mode. In a follow-up paper (8), we reported on the kinetics
of methanol synthesis catalyzed by the Ni(CO)4–KOMe sys-
tem in 1,4-dioxane–MeOH solvent mixture. Our further
work on this catalyst suggested that 1,4-dioxane–MeOH was
not particularly a good solvent mixture for this reaction be-
cause the solution homogeneity could not be maintained un-
der a wide range of Ni and base concentrations. In this
paper, we report on our work with other solvents for the re-
action including a kinetic study in the MeOH–1,2-bis(2-
methoxy ethoxy)ethane (triglyme) solvent mixture.
gassed with N2 and the weighed KOCH3 in the vial was
mixed with the degassed solvent mixture to obtain a light
yellow homogeneous solution. The solution was poured into
the pressure vessel and the vessel was quickly sealed and
purged several times with N2. A known amount of nickel
tetracarbonyl was then injected into the base solution
through the catalyst injection port and the vessel was imme-
diately pressurized with syngas to about 750 psig. After
10 min, a gas sample was taken to establish the initial gas
composition in the vessel. The automatic temperature con-
troller and the stirrer were set at 120°C and 1600 rpm re-
spectively. The stirring speed of 1600 rpm ensured that the
reaction was operating out of the mass transfer regime. The
vessel contents were then stirred for 15 min at room temper-
ature to monitor initial gas absorption by the solvent and the
base. At this time, methanol synthesis was initiated by heat-
ing the solution. The temperature and pressure were re-
corded as a function of time until the reaction became very
slow. The reaction was quenched by replacing the heater
with an ice water bath. Once the vessel cooled to room tem-
perature, the final pressure and temperature were recorded.
Gas and liquid samples were taken for analysis and the final
liquid volume was measured. For this study, methanol syn-
thesis was carried out under conditions with respect to
nickel, base, and methanol concentrations that allowed col-
lection of several data points during the runs. The data
points were collected by analyzing the vapor-phase compo-
sition every 2 to 3 min during the run.
Gas samples were analyzed for H2 and CO using Gow-
Mac 550 gas chromatographs in the TCD mode: a molecular
sieve column (8′ × 1/8′′) with He carrier gas for CO and a
molecular sieve column (6′ × 1/8′′) with N2 carrier gas for H2
with data reproducibility within ±2%. Liquid phase samples
(2µl) were analyzed on chromosorb-102 (8′ × 1/8′′) column
fitted in a PerkinElmer Model 8500 GC in the TCD mode
with the data reproducibility within ±5%. All gas
chromatographs were connected to HP Model 3390A inte-
grators for peak quantification. A qualitative detection of
Ni(CO)4 in the vapor phase was achieved as follows. A 1-cm
gas cell with KBr windows was evacuated and filled with the
gas sample from the pressure vessel. The IR spectrum of the
sample was recorded between 4000 and 400 cm–1 on a
PerkinElmer Model 1330 IR spectrophotometer. The broad
peaks at 2170, 2120 cm–1 (free CO), 2060 cm–1 (Ni(CO)4),
and 1760 cm–1 (CH3O2CH) were monitored.
Experimental
Materials
Potassium methoxide (>95% pure) and nickel
tetracarbonyl (>99.9% pure) were purchased from Alfa and
used as received. Methanol, triglyme, and other solvents
were obtained from Aldrich. For the kinetic study, methanol
was distilled in 400mL batches with magnesium turnings
and iodine under dry argon and triglyme was stored over
molecular sieves prior to use. Pure CO, H2, and syngas (H2
and CO) mixtures were purchased in aluminum cylinders (to
avoid any iron pentacarbonyl impurity) from Scott Specialty
Gases.
Apparatus
A stainless steel MagneDrive II Packless Zipperclave
0.5 L reactor manufactured by Autoclave Engineers, Inc.
(AE) was modified for this study. The reactor was equipped
with a Dispersamax six-blade impeller mounted on a shaft
driven by an AE variable speed motor. Ports were provided
for loading nickel tetracarbonyl, reactant gases, and sam-
pling vapor and liquid phases. The temperature of the reac-
tor was maintained with a Parr 4831 temperature controller,
which controlled an external heating mantle and an internal
air-cooling system. The pressure was monitored with a Setra
204 pressure transducer (accuracy to ±1 psig). The trans-
ducer and temperature outputs were recorded using an
Omega dual pen continuous chart recorder. The unit ratings
were as follows: stirrer = 0–2000 rpm, T = 25–350°C, P =
0.1–14 MPa.
For the kinetic study, the Redlich–Kwong equation of
state was used to calculate the number of moles of H2 and
CO in the gas phase from the experimental data of syngas
consumption vs. time. These data were further processed to
yield rate constant values.
Run procedure and analysis
Results and discussion
All runs containing nickel tetracarbonyl were performed
under a well-ventilated fume hood (Caution: Ni(CO)4 is vol-
atile and extremely toxic!).2 In a typical kinetic run, a speci-
fied amount of KOCH3 was weighed inside a Labconco
glove box under N2 and was brought out in a closed vial.
The methanol–triglyme solvent mixture (100mL) was de-
Catalyst performance
It has been shown in an earlier study (8) that the
Ni(CO)4–KOMe system is a versatile catalyst to affect meth-
anol synthesis from syngas. Table 1 lists representative runs
2 Pure Ni is commercially manufactured via the Mond process (9) that involves the intermediacy of Ni(CO)4. Ni(CO)4 is volatile (bp =
43.2°C at 25°C; vapor pressure @ 20°C = 315 mmHg (1 mmHg = 133.322 Pa)) and extremely toxic. The OSHA limit for Ni(CO)4 is set at
1 ppb in air for an 8-h daily exposure.
© 2001 NRC Canada