Liquid hydrocarbon fuels from cellulosic feedstocks via thermal deoxygenation of levulinic acid and formic acid salt mixtures

Paige A. Case , Adriaan R. P. van Heiningen and M. Clayton Wheeler *
Department of Chemical and Biological Engineering and Forest, Bioproducts Research Institute, 5737 Jenness Hall, Orono, ME 04469-5737, USA. E-mail: cwheeler@umche.maine.edu; Fax: +1 207 581 2323; Tel: +1 207 581 2280

Received 27th July 2011 , Accepted 2nd November 2011

First published on 18th November 2011


Abstract

Formic acid is demonstrated as a hydrogen source in a solid reaction system by first stabilizing the acid as a calcium salt which then decomposes at temperatures of relevance in pyrolytic reactions. High yields of deoxygenated hydrocarbons are produced by thermal decomposition of formic and levulinic acid mixtures where the optimum feed stoichiometry is consistent with that of cellulose hydrolysis and dehydration. The method promises a high-yield, robust, low-pressure, non-catalytic route for converting biomass hydrolyzates to hydrocarbon mixtures which are similar to petroleum crude oils.


Two techno-economic barriers hinder commercial implementation of renewable transportation fuel production from lignocellulosic biomass. First, the capital cost per unit product is high because the present largest wood processing facilities, as exemplified by pulp mills, are almost two orders of magnitude smaller in feed stock energy feed rate than an average oil refinery. The worlds largest pulp mills are capable of processing about 2 million dry metric tons (MT) per year,1 and a large refinery can process over 200 million barrels per year.2 Therefore, the energy feed rates are 1 GW for wood and 40 GW for oil (assuming a higher heating value of 17.5 GJ/tonne for wood and 6.1 GJ per barrel of oil equivalent (BOE)). The scale difference is caused by the high transport cost of biomass ($0.10/km/tonne)3 combined with the slow natural growth of lignocellulosics which limits the harvest radius around a production facility. The second techno-economic barrier is the high operating cost to convert lignocellulosics into energy dense biofuels. This is caused by the natural resistance of woody biomass to decomposition, i.e. the “recalcitrance” to convert lignocellulosics into monosugars and lignin at high yield4 and/or by the high cost to remove oxygen from lignocellulosics.5

From the perspective of an overall material balance, there are two practical forms in which oxygen can be removed: either as CO2 or as H2O.6 The advantage of removing oxygen from biomass with a minimal amount of hydrogen may be quantified by considering the following general reaction for deoxygenating cellulose to an aliphatic hydrocarbon (H/C ratio = 2/1):

 
ugraphic, filename = c1gc15914c-t1.gif(1)
where C6H10O5 is a cellulose monomer unit, CH2 represents an aliphatic hydrocarbon product on a per-mole-of-carbon basis, and y is a stoichiometric coefficient with values between 0 and 1. Eqn (2) shows that without additional hydrogen, 1/5 of the oxygen is removed as H2O and 4/5 are removed as CO2, while at y = 1 all oxygen is removed as water. Furthermore, it shows that the use of hydrogen for deoxygenation is economically-favored when the value of hydrogen is less than 1/12 that of cellulose on a molar basis, or less than 6.75 times that of cellulose on a mass basis, i.e. less than about $1000/MT H2 at a biomass cost of $60/MT biomass with cellulose content of 40%. We can also use this equation to explore the effects of hydrogen addition on the theoretical mass efficiency, carbon efficiency, and energy efficiency. The results of the analysis are plotted in Fig. 1 where we have assumed the higher heating values of cellulose, hydrogen and hydrocarbon are 17.5, 142, and 45 MJ kg−1 respectively.


Effects of hydrogen usage for deoxygenation of cellulose on carbon efficiency, mass efficiency, and energy efficiency.
Fig. 1 Effects of hydrogen usage for deoxygenation of cellulose on carbon efficiency, mass efficiency, and energy efficiency.

Important observations from Fig. 1 are that it is more energy efficient to remove oxygen as CO2 than H2O. The energy content of the products compared to the original energy content of the feedstock decreases from a maximum of 90% to 83% as hydrogen is used to remove the oxygen. Also the maximum energy efficiency is accompanied by only 35% mass efficiency and 67% carbon efficiency. This is to be expected since the goal is to increase the energy density from the feed of 17.5 MJ kg−1 to the product of 45 MJ kg−1 (diesel). Thus this simple analysis shows that it is advantageous to remove oxygen as CO2 and minimize the use of hydrogen for deoxygenation if possible. Without using hydrogen for deoxygenation, the theoretical hydrocarbon yield is approximately 2.6 BOE/MT cellulose.

A recent estimate of the capital cost of present cellulosic biofuel demonstration and commercial projects in the US is about 5 times higher than the $2.0 to $3.0 per annual gallon for corn ethanol.7 Thus, for cost-competitive production of lignocellulosic biofuels it is necessary to develop efficient, small scale conversion processes which can be located close to the biomass source.8

There are a number of biological and thermochemical biomass conversion technologies which can produce liquid fuels such as methanol, dimethyl ether, biodiesel, ethanol, butanol and pyrolysis.9–12 Some of these products can also be catalytically upgraded to deoxygenated liquid hydrocarbon fuels (LHFs). In a recent review, two routes were identified with potential to achieve economic production of liquid hydrocarbon fuels (LHF) at high yield and low complexity on an optimum scale for lignocellulosics; whole biomass pyrolysis to bio-oil and pretreatment-hydrolysis to sugars, coupled in both cases with upgrading processes.13 The latter should be carried out with a small number of reactors and with minimum utilization of external fossil-fuel hydrogen.

In the present study a novel route to LHFs has been discovered by combining hydrolysis and pyrolysis. First levulinic acid and formic acid were produced from biomass by hydrolysis through the Biofine process,14 and then the neutralized organic salt mixture was pyrolyzed to a LHF. The uniqueness of the second step is that ketonic decarboxylation15 and deoxyhydrogenation is achieved in one step at atmospheric pressure without a catalyst or externally supplied hydrogen, while the char producing reactions which hamper upgrading of pyrolysis oil16 are minimized by the stability of the organic salts in the temperature region below the pyrolysis temperature. The current method differs from ketonization such as that which is employed in the MixAlco™ process17 because our objective is to optimize hydrocarbon production during the carboxylate salt decomposition rather than to optimize ketone production.

Ketonization of organic acid salts is one pathway in which a significant amount of oxygen can be removed as CO2. In the general ketonization reaction equation:

 
R1COOH + R2COOH + M(OH)2 → R1COR2 + 2H2O + MCO3(2)
three of the four oxygen atoms in the two carboxyl groups are removed without the addition of hydrogen. The letter M in this example represents a basic divalent cation, but monovalent cations are also possible. Ketonization may be applied to the product of acid-catalyzed hydrolysis of cellulose, i.e. the equimolar mixture of levulinic acid and formic acid as demonstrated by Biofine on a one ton per day scale.18 Yields as high as 70% of the theoretical value have been achieved, and yields approaching 80% of theoretical have been predicted.19 We previously reported results of the pyrolysis of calcium levulinate by a combined ketonization/condensation route which forms a range of products with an increased energy density.20 This process was called thermal deoxygenation (TDO), and the products from TDO of pure calcium levulinate are primarily cyclic ketones which are water soluble and have an energy density of 35 MJ kg−1.

Formic acid has long been known as a potential source of hydrogen for transfer hydrogenation.21 Kleinert and Barth showed that high-pressure solvolysis/pyrolysis of lignin with formic acid significantly decreases the oxygen to carbon ratio of the product and produces products with a completely different structure than the starting material.22,23 Heeres et al.24 used formic acid for transfer hydrogenation of C6 sugars to γ-valerolactone with Ru/C and trifluoroacetic acid as catalysts. Haan et al.25 reported the catalytic conversion of levulinic acid with coproduct formic acid from cellulosic biomass to produce γ-valerolactone, and more recently Kopetzki and Antonietti26 demonstrated a similar conversion to γ-valerolactone via transfer hydrogenation under hydrothermal conditions.

TDO of calcium levulinate and formate mixtures

The quality and yield of the levulinic acid TDO products can be greatly improved by adding formic acid. When formic acid is present as a reactant, a highly deoxygenated hydrocarbon oil is formed. This oil has a mass density which is lower than water and is easily phase-separated as shown in Fig. 2. The organic phase also has a neutral pH (TAN ≅ 1 mg KOH/g), viscosity of 20 cP at 23 °C and an energy density higher than 40 MJ kg−1 which is about 15% greater than that for the product of pure levulinic acid TDO.
Thermal deoxygenation of a mixture of calcium formate and calcium levulinate produces a hydrocarbon oil which phase separates from water.
Fig. 2 Thermal deoxygenation of a mixture of calcium formate and calcium levulinate produces a hydrocarbon oil which phase separates from water.

Fig. 3 presents product distributions for a range of formic/levulinic acid molar ratios. The yield of hydrocarbon oil increases and the quantity of carbon in the char decreases as the formic acid concentration increases suggesting that more hydrogen is available for deoxygenation during TDO. Furthermore, although the yield of hydrocarbon oil is about the same for formic/levulinic acid ratios of 1 and 1.5, the ratio of hydrocarbon produced to carbon fed is maximum for a ratio of 1 because carbon from the formate did not contribute to the liquid product above this point.


Effect of formic/levulinic acid ratio on the distribution of carbon in solid char, aqueous liquid, organic liquid and gas phases. The lower error bar represents the standard deviation of solid mass remaining in the reactor. The upper error bar represents the standard deviation of the mass of hydrocarbon oil. Data for formic/levulinic acid ratio = 0 from Schwartz et al.20
Fig. 3 Effect of formic/levulinic acid ratio on the distribution of carbon in solid char, aqueous liquid, organic liquid and gas phases. The lower error bar represents the standard deviation of solid mass remaining in the reactor. The upper error bar represents the standard deviation of the mass of hydrocarbon oil. Data for formic/levulinic acid ratio = 0 from Schwartz et al.20

The hydrocarbon oil formed at each formic acid concentration was analyzed using H NMR, 13C NMR, GC-MS, bomb calorimetry and combustion analysis. The results of these analyses are presented in Table 1 to compare the effect of formic acid concentration on the quality of the oil product. The hydrogen to carbon ratio and higher heating value do not change significantly between the four formic ratios although they may increase slightly as the formic/levulinic acid ratio increases.

Table 1 Heating value and chemical properties of hydrocarbon oils produced by TDO treatment of mixtures of calcium levulinate and calcium formate
Formic/levulinic acid ratio (molar) Higher heating value (MJ kg−1) Hydrogen/carbon ratio (mol/mol) % Alkyl carbon area 13C NMR % Aromatic/alkene carbon area 13C NMR
a Schwartz et al.20
0a 35 40 44
1/20 39.5 1.21 57.1 41.7
1/2.5 40.9 1.35 44.4 55.5
1/1 40.7 1.27 38.2 61.5
1.5/1 41.3 1.29 38.8 60.9


There is almost no evidence of oxygenates in the hydrocarbon oil based on 13C NMR as shown in Fig. 4 and also confirmed by H NMR. By integrating the regions in 13C NMR spectra for different acid ratios, we also determined that as formic acid concentration is increased, the oils have more conjugated double bond character, which could be either aromatics or olefins. The GC-MS data indicate that the oils contain hundreds of compounds including a significant number of alkylated aromatics and conjugated alkenes, which are consistent with the NMR analysis. The aqueous phase was found to contain hydrocarbon products, such as methyl-cyclopentenones, also found in TDO of pure levulinic acid. The non-condensable gases included CO2, CO, and C1–C3 hydrocarbons.



            13C NMR spectra of the TDO hydrocarbon product with regions as identified in Joseph, et al.27
Fig. 4 13C NMR spectra of the TDO hydrocarbon product with regions as identified in Joseph, et al.27

Increasing the quantity of formic acid as a calcium formate salt improves the yield and deoxygenation of levulinic acid TDO products. The thermogravimetric analysis shown in Fig. 5 compares the decomposition rates of calcium formate, calcium levulinate and an equimolar mixture of the two salts. In all three cases, mass loss occurs predominantly within two temperature ranges: 1) a low temperature range from 400 °C to 500 °C and 2) a high temperature range from 600 °C to 800 °C. The mass losses at low temperature correspond to decomposition of the salts, and the high temperature mass loss corresponds to decomposition of CaCO3.28 Note that the low temperature decomposition rates for all three cases overlap. Also, note that the high temperature peak is very broad for calcium levulinate, probably because of the relatively large quantity of carbonaceous residue.


Thermogravimetric analysis of pure calcium formate, pure calcium levulinate and an equimolar mixture of formate and levulinate using a ramp rate of 10 °C min−1. The photographs of the TGA pans show that less carbon remains in the char from the formate/levulinate mixture.
Fig. 5 Thermogravimetric analysis of pure calcium formate, pure calcium levulinate and an equimolar mixture of formate and levulinate using a ramp rate of 10 °C min−1. The photographs of the TGA pans show that less carbon remains in the char from the formate/levulinate mixture.

There are two hypotheses which might account for the increased yield of oil when decomposing formate/levulinate mixtures. First, the formate might participate with levulinate in the initial “ketonization” mechanism to form an aldehyde intermediate thus changing the subsequent vapor phase reaction pathways. A second hypothesis is that hydrogen production in this molecularly-mixed system contributes to in situ hydrodeoxygenation. It is known that calcium formate thermally decomposes to a mixture of H2, CO, and CaCO3.29 Also, it is clear in Fig. 5 that the thermal decomposition temperatures of both salts significantly overlap. Therefore, this novel technology could be applied in a broad number of applications where deoxygenation is desired.

There has been debate over the use of formic acid as a hydrogen source because of its value as an industrial chemical. In this case, however, formic acid is a co-product of cellulose hydrolysis:

 
ugraphic, filename = c1gc15914c-t2.gif(3)

Further, separation and purification of the two acids would require extraction and multiple distillations, so use of the formic acid as a reagent without purification could potentially overcome the lost opportunity cost. To demonstrate this potential, TDO oils were made from unrefined levulinic acid feedstocks which were themselves produced by hydrolysis and dehydration of municipal solid wastes. These experiments demonstrated similar yields with no obvious negative effects of contaminants in the feedstock.

The current results demonstrate production of a hydrocarbon oil via a thermal pathway without the addition of hydrogen. However, the H/C ratio of this oil is only 1.3/1. It would therefore require 0.35 moles of hydrogen per mole of carbon in the product to increase the H/C ratio to 2/1 for comparison in Fig. 1.

Although this paper focuses on the use of calcium as a cation, we have used other alkali and alkali earth metals for TDO yielding similar results. The choice of metal ion might not significantly affect the yield and composition of oil, but it may affect the economics and energy requirement for the process. For instance, magnesium salts decompose at lower temperatures, which decreases the energy consumption for heating. Monovalent cations such as sodium were also employed successfully, providing evidence that both di- and mono-valent cations are useful for this method. Therefore, there may be opportunities to integrate TDO technology with existing manufacturing facilities, such as pulp mills, in which cation recovery cycles already exist.

Conclusion

Conversion of cellulosic feedstocks to hydrocarbon transportation fuels could be an important contribution to supplying future energy needs. The levulinic acid pathway, consisting of acid hydrolysis, neutralization, and TDO, is a relatively simple way which doesn't rely on heterogeneous catalysts and complex purification of feedstocks. Potential cellulosic feedstocks include forest residues, waste paper, municipal solid waste, etc. as well as traditional lignocellulosic sources such as wood and energy crops. Conversion of the five-carbon sugars to levulinic acid is also technologically feasible,30 so there is also the potential to utilize all of the carbohydrates in feedstocks if favorable economics can be demonstrated.

We have improved levulinic acid TDO by adding formic acid, resulting in the production of a hydrocarbon oil in high yields. Utilizing existing hydrocracking technology, the refined TDO oil could be a direct substitute for fossil fuels such as gasoline, diesel or jet fuel. Even without further upgrading, the oil is a complex mixture of hundreds of highly deoxygenated chemical compounds with a higher heating value in excess of 40 MJ kg−1. We have investigated the effects of changing the formic/levulinic acid ratio and how that ratio affected the yield, composition and quality of the oil produced. It seems likely that a 1/1 mole ratio, which provides the highest oil yield, would be both convenient and practical from a process standpoint. However, economics based on formic acid, levulinic acid, and furfural as a valuable coproducts of hydrocarbon oil production, might favor a lower ratio.

The TDO method has many of the same advantages of fast pyrolysis; the reaction occurs at atmospheric pressure and moderately high temperature in a simple reactor. However, the product has several traits that make it superior to typical pyrolysis oils. TDO oil is produced in high yield and can be easily separated from other products such as water and char. In addition, the oil has a neutral pH, high energy density, low viscosity and a hydrogen to carbon ratio of ∼1.3. The extent of deoxygenation during TDO decreases the downstream hydrotreating required to produce a drop-in transportation fuel. Furthermore, this process does not use a catalyst, making it tolerant to trace impurities that could poison or foul precious metal catalysts.

Experimental

Reactions were conducted by forming the acid salts in a stirred 300 mL Parr reactor along with stainless steel ball bearings to aid in heat transfer and material mixing. Except for the experiment using crude levulinic acid from the Biofine pilot plant in Gorham, ME, the acid salts were prepared by mixing levulinic acid (>99%), and formic acid (>95%) with 20% excess Ca(OH)2 (>98%) in the reactor. Nitrogen was continually fed to the reactor at a rate of 100 sccm as a sweep gas, and the products were continuously condensed in a water cooled condenser (10 °C), while non-condensable products were collected in bags. The reactor was heated at approximately 10 °C min−1 while stirring at 50 rpm. Water evolved between 100–200 °C as the salts dried. Vapors evolved predominately between 375 °C and 450 °C. The temperature was then maintained constant at 450 °C until no additional product evolution was observed. Combustion analysis for hydrogen and carbon content was performed by Galbraith Laboratories, Inc. Viscosity measurements were conducted using a Brookfield viscometer. Thermogravimetry used a TA Instruments Q500 TGA. 13C NMR spectra were recorded at 100 MHz on a Varian Unity 9.4 T instrument at 29 °C. A Shimadzu GCMS-2010 with a MS-5 column was used for liquid product identification. An SRI 8610C portable GC was used to identify non-condensable products.

Acknowledgements

The authors acknowledge Thomas Schwartz, Jincy Joseph, Scott Eaton, Saikrishna Mukkamala, Cody Newman, John Hessler, Nick Hill, Sedat Beis and Rachel Austin (Bates College Dept. of Chemistry) for their assistance with experiments and analyses. We also thank Steve Fitzpatrick for providing the crude levulinic acid which precipitated the current discovery, as well as Peter van Walsum, Brian Frederick, William DeSisto, and Hemant Pendse for many useful discussions. Funding for this work was provided by U.S. Dept. of Energy grant # DE-FG02-07ER46373.

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