Method of producing slow-release nitrogenous organic fertilizer from biomass

Abstract: A process for making organic slow release nitrogenous fertilizers from pyrolysis products obtained from the pyrolysis of biomass uses a chemical reaction to combine a nitrogen compound containing the -NH 2 group with the pyrolysis products to form a mixture. The mixture is heated to form organic nitrogen compounds. Various sources of biomass can be used. The mixture can be heated to remove water and to cause polymerization and solidification to occur. The mixture can also be combined with an absorbent. Previously, nitrogenous fertilizers had been produced using an ammoxidation process requiring long reaction times of up to several hours.

Description: This invention relates to the production of organic slow-release nitrogenous fertilizers (O-SRNF) by reacting ammonia or related compounds like urea with liquids, vapours and optionally solids obtained by pyrolysis of biomass substrates. It has long been known that nitrogenous organic fertilizers can be produced by reaction between ammonia and humic acids naturally present in peat or lignite. In a process known as ammoxidation, coal or other carbonaceous material is subjected to a mild oxidation, usually with air, in order to increase its humic acid content and subsequently or simultaneously exposed to ammonia. The earliest patented process for production of nitrogenous organic fertilizers by the ammoxidation process was disclosed by N. Caro and A.R. Frank in British Patent Numbers 347641 (1929) and 349001 (1931). This pioneering work was soon followed by several related inventions, for instance Walton and Gardiner, U.S. Patent Number 1,858,230 (1932). Applications to woody biomass [M.I. Chudakov, et al., USSR Patent Number 223,823 (1968); Y.K. Kim, et al., Ind. Eng. Chem. Prod. Res. Dev., 23 (1984) 620] and to technical lignin residues from pulping processes [W.J. Detroit, U.S. Patent Number 4,846,871 (1989); D. Meier, et al., Proc. Second Brazilian Symposium on the Chemistry of Lignins and other Wood Components, (FAPESP) Sao Paulo, 1992, p. 178]. The principal feature of such fertilizers is that they combine the soil conditioning properties of organic manures and the nitrogen releasing properties of inorganic fertilizers. It would be desirable furthermore that the nitrogen be bound chemically in a form suitable for slow release by soil microorganisms since typically more than 50% of the input nitrogen in typical inorganic fertilizers based on ammonium, urea or nitrate is lost in run-off water. This not only represents a source of inefficiency but is also a major contributor to ground water pollution. The reactions between ammonia and humic acids appear to consist principally in the formation of ammonium phenolates and carboxylates, collectively designated as ammonium humates. On heating, these are converted first to the corresponding amides and subsequently to more stable amidine and iso-indole forms [K. Guruz, Fuel, 59 (1980) 772]. Unfortunately, while the nitrogen content of ammoxidated coals increases with temperature, so do the latter forms of nitrogen and these have been shown to be incapable of releasing the nitrogen into the soil [N. Berkowitz, et al., Soil Sci. 110 (1970) 211]. A further disadvantage of the ammoxidation process is the requirement for long reaction times, typically up to several hours, and substantial oxygen pressures, typically up to 4 MPa. It is known that some of the chemical problems can be solved by first oxidizing the carbonaceous substrate with nitric acid and then reacting it subsequently with ammonia [J. Coca, et al., Ind. Eng. Chem. Prod. Res. Dev., 23 (1984) 620]. In this case, much more nitrogen becomes available but the processing costs are higher. GB-A-2156329 discloses a method for producing fertilizer from softwood bark or tree waste in which the starting material is decomposed at 70-140°C and ash is added at high pressure together with urea and optionally phosphorus. US-A-4,002,457 discloses the production of a nitrogen-containing, water insoluble soil conditioner and fertilizer by heating spent sulfite liquor from wood pulp products at 170 to 260°C, for 30 minutes to 12 hours, to form a partially pyrolysed water-insoluble material which is then reacted with ammonia. At present, most slow-release fertilizers are in the form of urea formaldehyde products (R.M. Schmidlkofer, Chemtech, May 1994, p. 54). Sulfur coated urea and condensation products of urea and aldehydes have made more limited progress due to high costs. Nevertheless, these formulations establish that the products of the reactions between carbonyl compounds, aldehydes in particular and ammonia or urea contain nitrogen in suitable form for slow release of nitrogen to soil. Presumably, the nitrogen is substantially present in the form of imines and higher molecular weight products derived from them. The present invention consists in a process for making organic nitrogenous fertilizers from at least one starting material selected from ligno-cellulosic materials and starch-containing materials, said process comprising: (a) subjecting said starting material to fast pyrolysis, in a non-oxidising atmosphere to a final temperature in excess of 350°C with a vapour residence time of less than 3 seconds, to yield pyrolysis products including products which are liquids or vapours condensible to liquids; (b) chemically reacting a nitrogen compound containing the -NH 2 group with said pyrolysis products to form organic nitrogen compounds and recovering the organic nitrogen compounds so formed. There can thus be provided a method for converting biomass to nitrogenous organic fertilizers (0-SRNF) without oxidation. The fertilizers may be stabilized by combination with a suitable absorbent such as peat, moss pyrolytic char, charcoal, lignin, manure and finely divided ligno-cellulosic biomass. A further advantage of this invention is that it enhances the economic viability of fast pyrolysis processes, especially as an integral part of a "bio-refinery", by providing a method for utilization of part or all of the liquid and solid products of such processes for the production of high value organic slow release nitrogen fertilizers and further to eliminate or reduce waste streams. By means of this invention biomass can be recycled in an efficient manner by converting wastes to organic fertilizers which can be returned to the soil. The starting material is preferably in the form of biomass selected from agricultural waste, forestry waste, municipal solid waste, wood, grasses, algae, peat, lignite, food processing waste and beverage processing waste. The invention further provides an organic nitrogen compound suitable for use as a fertilizer comprising a chemical reaction product of a nitrogen compound containing the -NH 2 group with liquid and/or condensible vapour products of the fast pyrolysis, in a non-oxidising atmosphere to a final temperature in excess of 350°C with a vapour residence time of less than 3 seconds, of ligno-cellulosic and/or starch containing materials. The nitrogen compound containing the -NH 2 group which is reacted with the pyrolysis products in accordance with the invention is preferably in the form of urea, an aqueous solution of urea, an aqueous ammonia solution, an amine, an amino acid, a protein or an ammonium salt. Ligno-cellulosic biomass already contains about 35 to 44 wt% of oxygen. It is desirable for the production of an organic slow-release nitrogen fertiliser (O-SRNF) to maintain the oxygen content at these levels but converted into functional groups, aldehydes in particular, suitable for reaction with appropriate nitrogenous compounds. This goal can be achieved by pyrolysis of biomass. Fast or flash pyrolysis involves the rapid heating of a substrate in a non-oxidizing atmosphere. When biomass is pyrolyzed at heating rates of the order of 1000°C per second or greater to final temperatures in excess of 350°C and vapour residence times are kept short (i.e. less than three seconds), high yields of liquids can be obtained by condensation of the pyrolysis vapours. The other products of pyrolysis consist of a solid char and permanent gases like carbon monoxide, carbon dioxide and methane. The liquid product is referred to variously as the pyrolysate, pyrolytic tar or pyrolytic oil. It is possible to attain the desired heating rates in a variety of apparatus. These include fluidized beds, entrained beds, vortex reactors, pyrolytic mills, ablative pyrolysis reactors and "rapid thermal processing" reactors, circulating fluid beds, among other embodiments. Lower heating rates can be tolerated if vapour residence times are kept sufficiently small as obtained in vacuum pyrolysis processes. These various biomass pyrolysis technologies have been reviewed by A.V. Bridgwater and S.A. Bridge in "Biomass Pyrolysis Liquids Upgrading and Utilisation", A.V. Bridgwater and G. Grassi (eds.), Elsevier, London, 1991. While the data provided in the subsequent description were obtained by flash pyrolysis in a fluidized bed, similar liquid and char pyrolysates can be obtained from all reactor systems which are characterized by high temperature and/or short residence times as pointed out by G. Underwood and R.G. Graham in U.S. Patent Number 4,994,297 (1991). For example, Table 5 of this reference shows that the results obtained by fluidized bed pyrolysis and reported earlier by D.S. Scott, [D.S. Scott and J. Piskorz in Bioenergy 84, Vol. III, H. Egneus and A. Ellegard (eds.), Elsevier, London, 1985] are comparab to those from the rapid thermal processing process. Some typical yields obtained by fast pyrolysis of various biomass in a fluidized bed are shown in Table 1 below: Yields, Wt % of moisture-free Feed (mf) Feedstock Poplar-Aspen Wood Wheat Chaff Hog Fuel Sulfite Pulp Mill waste Bleached Cardboard Sorghum Bagasse Peat Moss Gas 10.8 15.9 13.1 9.3 20.5 11.7 16.2 Char 7.7 17.6 31.8 19.5 3.8 13.4 26.3 Water 12.2 15.7 12.1 20.3 16.4 10.6 8.2 Organic Liquid 65.8 51.0 46.6 46.8 55.3 58.8 49.1 This invention is based on the discovery that the liquids produced by flash or fast pyrolysis of biomass react readily with ammonia, urea and related compounds to form organic nitrogen compounds and that furthermore, these compounds polymerize and solidify on heating to give stable products which give demonstrable release of nitrogen in greenhouse tests. These products therefore function as organic slow-release nitrogen fertilizers. Chemical analysis shows that the pyrolysis liquids contain high concentrations of carbonyl, carboxyl and phenolic functional groups and it is likely that these groups are largely responsible for the reactions with ammonia. The pyrolysates also contain a substantial amount of lignin degradation products and are therefore likely to be good sources of humic material and hence to have useful soil conditioning properties. The pyrolysis products are preferably reacted with the nitrogen compound containing the -NH 2 group by adding the nitrogen compound during pyrolysis, or to the liquid or vapour pyrolysis products shortly after they are produced. The nitrogen compound can also be added prior to pyrolysis. The mixture is then heated to form organic nitrogen compounds. Preferably, the mixing and heating is carried out in a temperature range of approximately 150°C to approximately 180°C. Several pyrolysis liquids obtained by fluidized bed flash pyrolysis of different feedstocks at different temperatures were analysed for functional group content with the results shown in the following Table 2: Feedstock Pyrolysis Temperature (°C) Moles Functional Groups /kg Organic Liquid Carboxyl Carbonyl Hydroxyl Phenolic Methoxyl Maple 480 2.1 5.7 0.92 2.8 2.1 Wheat Straw 500 1.4 5.3 1.40 3.0 1.1 Poplar-Aspen 450 2.1 6.2 0.77 2.8 1.6 " 500 1.6 6.9 0.87 2.8 1.5 " 550 1.7 6.6 0.77 2.8 1.2 Peat Moss 520 1.2 3.0 1.30 1.8 0.7 These results show that, depending on the feedstock, a total of between 6 and 11 moles of carboxyl, carbonyl and phenolic groups are available. If indeed these are the groups responsible for reaction with ammonia, urea or amino compounds in general, then complete reaction would therefore result in the incorporation of between 10 and 17 wt% of nitrogen/kg of organic liquid product. These expectations are reasonable because it is the teaching of organic chemistry (e.g. see J. March, "Advanced Organic Chemistry", 3rd ed., Wiley, N.Y., 1985, Chapter 6) that aldehydes and ketones react with primary amino compounds to give imines which may subsequently polymerize. Furthermore, in the presence of an acid or base catalyst, Mannich type reactions may occur in which ammonia or one of its salts undergoes condensation with an aldehyde and a compound containing an active hydrogen to give Mannich bases. The latter may subsequently condense with additional aldehydes or active compound. Such reactions would be desirable for the purposes of this invention as they would be expected to promote cross-linking and therefore stabilization of the product. A further type of reaction which may occur is that between carboxylic acids and ammonia or amines to give salts, which may subsequently decompose thermally to amides. It was determined that in many instances, a large fraction of the carbonyl groups consist of only a few simple aldehydes, namely hydroxyacetaldehyde, glyoxal, methyl glyoxal, formaldehyde and acetaldehyde. This is significant since aldehydes are more reactive towards ammonia than ketones. Similarly, only a few simple carboxylic acids, especially formic and acetic acids, appear to be the principal contributors to the carboxyl group content. Some typical concentrations of some of these compounds in biomass pyrolysates obtained by pyrolysis at around 500°C of a range of biomass feedstocks including wood, agricultural wastes, forest residues and industrial biomass wastes are shown in Table 3 below: Wt % of Organic Liquid Product Feedstock Poplar-Aspen Wood Wheat Chaff Hog Fuel Bleached Cardboard Sorghum Bagasse Sulfite Pulp Mill waste Peat Moss Hydroxyacetaldehyde 15.2 12.8 8.0 19.3 12.2 17.0 1.4 Glyoxal 3.3 1.4 1.1 2.6 0.6 1.4 n.d. Formaldehyde 1.8 2.6 1.8 6.6 6.1 n.d. n.d. Formic Acid 4.7 n.d. 2.3 n.d. n.d. 3.6 15.5 Acetic Acid 8.3 12.0 5.6 n.d. 4.3 n.d. 4.5 "Pyrolytic Lignin" 24.6 29.6 59.4 4.0 30.6 6.4 49.2 It is apparent that in the case of poplar wood, for instance, the simple aldehydes listed can contribute in excess of 50% of the carbonyl groups present while formic and acetic acids can constitute nearly all the carboxyl groups. Nevertheless, the identities of many of the carbonyl compounds remain unknown in most cases. It has also been determined that the pyrolysis liquids from ligno-cellulosic biomass typically contain between 20 and 50 wt% of largely lignin-derived material which may be readily precipitated by adding water. This material, which has been referred to as "pyrolytic lignin", has been shown by NMR analysis to be chemically very similar to "virgin lignin", [D. Radlein, et al., J. Anal. Appl. Pyrol., 12 (1987) 51]. Most of the phenolic groups in the pyrolysis liquids are believed to be associated primarily with this fraction. Besides its nitrogen capacity, this fraction is also beneficial in that lignin plays an important role in the formation of organic matter in soil where it is slowly biodegraded to give humic matter. The pyrolytic lignin fraction is shown in the preceding Table 3 for various feedstocks. The following examples are intended to illustrate the various aspects of the present invention without limiting the invention in any way. Example 1: A sample of pyrolysis tar obtained by the flash pyrolysis of eucalyptus wood was used to prepare a nitrogen enriched fertilizer. The sample contained 17.2% water. The analysis of this tar for some of the aldehydic and carboxylic acid components was as follows: Wt % of Organic Fraction of Eucalyptus Tar Hydroxyacetaldehyde 7.1 Glyoxal 1.4 Formaldehyde/Formic Acid 3.1 Acetic Acid 3.8 "Pyrolytic Lignin" 36.4 This tar therefore contains only about 50% as much of these key components as does a poplar-aspen tar and the nitrogen uptake may be expected to be correspondingly low. Fifty grams of the tar were mixed with 12 g of urea and the mixture heated with stirring at 150°C. The viscosity gradually increased and the urea was completely dissolved. After thirty minutes, the mixture had become a solid mass with a liquid crystalline appearance. On cooling, it became hard and brittle and was ground to give a dark brown hygroscopic powder. The weight loss of the mixture was 27 wt% which exceeds that expected on the basis of the water content of the tar. It is likely that, at the reaction temperature, some dehydration reactions took place and some volatiles were lost from the tar. The amount of urea added was equivalent to 8 moles of functional groups/kg of pyrolysis tar. This result is near the expected lower limit of the reactive functional group content of the tar, including carbonyl, carboxyl and phenolic groups. Urea is well known to react readily with aldehydes to form resins (Merck Index, 1983). On account of its difunctional nature, it is an excellent cross-linker. Example 2: A sample of fertilizer, designated PNU1 was prepared according to the method of Example 1. Sixteen pots each of maize and beans were germinated on a nutrient free artificial soil, Turfase®. After germination, the plants were thinned to four per pot. Four groups of four pots each were treated as follows: Group A No fertilizer. Group B 0.25 g of PNU1 initially and again after four weeks. Group C Two treatments per week of 250 ml. of a solution containing 100 ppm of a standard 20-20-20 fertilizer. Group D Combination of treatments of Groups B and C. The plants were watered daily and grown for eight weeks in a greenhouse. At the end of this time, the whole plants, including roots, were harvested and dried at 120°C. The average weight of the plants in each group were found to be as follows: Beans A 0.47 g Beans B 0.67 g Beans C 1.24 g Beans D 1.50 g Maize A 1.08 g Maize B 1.74 g Maize C 5.91 g Maize D 5.95 g. Therefore, the beans and maize treated with PNU1 alone gained 42.5% and 61.1% more weight respectively than the unfertilized plants. The beans and maize that received both the standard fertilizer and PNU1 gained 21.0% and 0.7% more weight respectively than those that received only the standard fertilizer. It is concluded that the organic fertilizer described herein is capable of releasing available nitrogen to the soil and is non-toxic to plants. Example 3: 2.67 g of a pyrolysis tar were combined with 2.00 g of ground sphagnum high moor peat (which had a moisture content of 33.5 wt%) and 3.0 g of a 29 wt% aqueous ammonia solution. The mixture was heated at 60°C for thirty minutes and then at 105°C for one hour in an open vessel. The resulting solid, which had the appearance of the original peat, was dry and non-hygroscopic with a final weight of 3.41 g. This sample was designated PTN1. The expected final mass, assuming ony loss of physically bound water, was 3.54 g. It should be noted that reaction of ammonia with a carbonyl compound to give an imine takes place with negligible change in mass: R-CO-R' + NH 3 → R-C=NH-R' + H 2 O. Therefore, there was some weight loss of volatile components from the tar. It is noted that, since imines are readily re-hydrolysed to the parent carbonyl compound, it is important to carry out the amination reaction under conditions under which water can be removed. This will prevent reversal of the reaction as well as promote subsequent polymerization. A portion of sample PTN1 was thoroughly extracted with water and then dried at 105°C. This was designated as sample PTN2. Elemental analyses were carried out on the various samples with the following results: Sample Wt %, moisture free C H N O (by difference) Typical Hardwoood Pyrolysis Oil 51-59 5-7 0.05-0.5 Premier Peat 51.55 5.49 1.11 41.8 PTN1 54.82 5.80 5.06 34.3 PTN2 56.52 5.76 4.31 33.4 These results show that the total nitrogen content was 8.1 wt% on the basis of moisture-free pyrolysate incorporated into the formulation, while the insoluble nitrogen content was 6.9 wt% on the same basis. Furthermore, the results demonstrate that the pyrolysis tar can be combined with a suitable absorbent (peat in this example), to give a friable non-hygroscopic product. Example 4: Experiments were conducted to determine whether absorbents other than peat could be used for stabilization of the fertilizer and to reduce hygroscopicity. The pyrolytic char, which is a by-product of the pyrolysis process, has a high content of oxygenated functional groups and in fact represents a partially activated carbon. It may therefore serve not only as an absorbent, but may also bind nitrogen directly by reaction with -NH 2 groups. Accordingly, the capacity of pyrolytic char for stabilization of the fertilizer product was investigated. Fertilizers were prepared by combining varying amounts of pyrolysis tar with 1.0 g of pyrolytic char in the same manner as that described for peat in Example 3. The ratios of tar to char varied from 0.5:1 through to 2.42:1. In all cases, the weight loss after drying at 105°C was about 30%. In all cases, the product was a friable non-hygroscopic solid. It is concluded that activated carbons, including pyrolytic chars, are suitable absorbents for stabilization of the nitrogenous fertilizers described herein. Example 5: Sawdust from Alberta Poplar wood was impregnated with an aqueous solution of urea and then dried to a moisture content of 2%. The urea content of the impregnated sawdust was 16.4 wt% on the basis of the moisture-free wood. The impregnated wood was pyrolyzed in a fluidized bed at 500°C at a vapour residence time of 0.36 seconds (Run #302). The condensed pyrolysate had an organic content of 76.5 wt% on the basis of the urea and moisture-free wood. The yield of carbon dioxide was 10.0 wt% on the same basis. This is much higher than the expected yield of 5 to 6 wt% from untreated wood under the same pyrolysis conditions and indicates that the urea had been hydrolyzed to liberate ammonia according to the reaction: NH 2 CONH 2 + H 2 O → CO 2 + 2 NH 3 The overall mass balance was 114,5% on the basis of urea-free wood, which indicated that there was substantial nitrogen uptake. The liquid pyrolysis product contained no urea or ammonia. Elemental analysis of this product gave the following results in wt%: Carbon Hydrogen Nitrogen 48.54 6.95 10.30. If all of the nitrogen contained in the urea had been incorporated into the liquid pyrolysate, its nitrogen content would be expected to be 10.0%. Therefore, it may be concluded that essentially all the nitrogen added as urea was incorporated into the liquid product. Furthermore, the result implies that free ammonia or any compound which will liberate ammonia under the pyrolysis conditions can equally well be reacted directly with the hot vapours in the pyrolysis reactor. Such compounds include ammonium salts since these are known to react directly with aldehydes and which may also decompose or be hydrolysed to liberate ammonia at pyrolysis temperatures.

Claims: A process for making organic nitrogenous fertilizers from at least one starting material selected from ligno-cellulosic materials and starch-containing materials, said process comprising: (a) subjecting said starting material to fast pyrolysis, in a non-oxidising atmosphere to a final temperature in excess of 350°C with a vapour residence time of less than 3 seconds, to yield pyrolysis products including products which are liquids or vapours condensible to liquids; (b) chemically reacting a nitrogen compound containing the -NH 2 group with said pyrolysis products to form organic nitrogen compounds and recovering the organic nitrogen compounds so formed. A process as claimed in claim 1 including the steps of combining said nitrogen compound containing the -NH 2 group with said pyrolysis products to form a mixture and mixing and heating said mixture to form said organic nitrogen compounds. A process as claimed in claim 2 wherein said mixing and heating are carried out at a temperature of 150 to 180°C. A process as claimed in any preceding claim wherein the starting material is biomass selected from agricultural waste, forestry waste, municipal solid waste, wood, grasses, algae, peat, lignite, food processing waste and beverage processing waste. A process as claimed in any preceding claim including the step of adding the nitrogen compound during the pyrolysis process. A process as claimed in any one of claims 1 to 4 including the step of adding the nitrogen compound prior to pyrolysis. A process as claimed in any one of claims 1 to 4 including the step of adding nitrogen compound to the said liquid or vapour pyrolysis products. A process as claimed in any one of claims 1 to 4 or 7 including the step of adding the nitrogen compound shortly after producing the pyrolysis products. A process as claimed in any preceding claim wherein the nitrogen compound is in the form of urea, an aqueous solution of urea, an aqueous ammonia solution, ammonia, an amine, an amino-acid, a protein or an ammonium salt. A process as claimed in any preceding claim including the step of combining the organic nitrogen compound with an absorbent selected from peat, moss, pyrolytic char, charcoal, lignin, manure and finely divided ligno-cellulosic biomass. A process as claimed in any preceding claim including the step of heating the organic nitrogen compounds following their formation to remove water. A process as claimed in any preceding claim including the step of heating the organic nitrogen compounds to a sufficient temperature to cause polymerization to occur. A process as claimed in any preceding claim including the step of heating the organic nitrogen compounds to a sufficient temperature to cause solidification to occur. A process as claimed in any preceding claim wherein the pyrolysis portion of the process is carried out with a vapour residence time of less than three seconds. A process as claimed in any preceding claim wherein the pyrolysis part of the process is carried out at a heating rate of at least 1000°C per second to a temperature of at least 350°C. An organic nitrogen compound suitable for use as a fertilizer comprising a chemical reaction product of a nitrogen compound containing the -NH 2 group with liquid and/or condensible vapour products of the fast pyrolysis, in a non-oxidising atmosphere to a final temperature in excess of 350°C with a vapour residence time of less than 3 seconds, of ligno-cellulosic and/or starch containing materials. A compound as claimed in claim 16 wherein the pyrolysis products are formed from biomass selected from agricultural waste, forestry waste, municipal solid waste, wood grasses, algae, peat, lignite, food processing waste and beverage processing waste. A compound as claimed in any one of claims 16 or 17 wherein the compound is a solid. A compound as claimed in any one of claims 16 or 17 wherein the mixture is combined with an absorbent selected from the group consisting of peat, moss, pyrolytic char, charcoal, lignin, manure and finely divided ligno-cellulosic biomass.

Inventors: MAJERSKI PIOTR A, PISKORZ JAN K, RADLEIN DESMOND ST A G, MAJERSKI, PIOTR A., PISKORZ, JAN K., RADLEIN, DESMOND ST. A.G.
Applicants: MAJERSKI PIOTR A, PISKORZ JAN K, RADLEIN DESMOND ST A G, MAJERSKI, PIOTR A., PISKORZ, JAN K., RADLEIN, DESMOND ST. A.G.
Application year: 1995
Main classification: C05C3
IPC codes: C05C3, C05C9, C05F11