Process and System for Converting Waste to Energy Without Burning

Abstract

This invention relates to a power recovery process in waste steam/CO2 reformers whereby a waste stream can be made to release energy without having to burn the waste or the syngas. This invention does not make use of fuel cells as its critical component but makes use of highly exothermic chemical reactors using syngas to produce large amounts of heat, such as Fischer-Tropsch. It also relates to control or elimination of the emissions of greenhouse gases in the power recovery process of this invention with the goal of producing energy in the future carbonless world economy. A New Concept for a duplex kiln was developed that has the combined functionality of steam/CO2 reforming, heat transfer, solids removal, filtration, and heat recovery. New methods of carbon-sequestering where the syngas produced by steam/CO2 reforming can be used in Fischer-Tropsch processes that make high-carbon content compounds while recycling the methane and lighter hydrocarbons back to the reformer to further produce syngas at a higher H2/CO ratio.

Description

FIELD OF THE INVENTION

The invention relates to a process and system in which a waste stream can be made to release energy without having to burn the waste or the syngas and consume oxygen and have large carbon dioxide emissions. At the same time the waste can be converted into a carbon-containing fertilizer, hydrogen fuel, and a carbon-sequestering, high-carbon content product of important commercial value, such as unsaturated, high-density paraffin.

BACKGROUND OF THE INVENTION

The process and system for carrying out the steam/CO₂ reforming chemistry to accomplish this has been patented by the author (U.S. Pat. No. 6,187,465, issued Feb. 13, 2001 and CIP U.S. Pat. No. 7,132,183, issued Nov. 7, 2006, filed Jun. 23, 2003) and deals with waste steam/CO₂ reformers interfacing to fuel cells. And CIP of patent application Ser. No. 10/719,504 (examined by Ryan/Lewis) filed Nov. 21, 2003 deals with cleaning the syngas produced in waste steam/CO₂ reformers interfacing to fuel cells to produce energy without poisoning their sensitive catalysts.

There is a great need to destroy a wide range of waste streams generated around the world and at the same time to convert this carbonaceous waste into useful hydrogen-rich syngas by two methods: (1) to drive a fuel cell and (2) to feed a Fischer-Tropsch unit—both to produce clean energy.

The challenge and problem with fuel cells has been their extreme sensitivity to various unknown chemical poisons at parts per million levels coming from the waste streams from harming the electrochemical catalysts of the high temperature fuel cells. By comparison Flory-Huggins catalysts in Fischer-Tropsch reactors (such as supported iron and cobalt catalysts) are much less sensitive to poisons than fuel cells and are highly exothermic.

CO+2H₂→1/n(—CH₂—)_n(l)+H₂O(l) ΔH°₂₉₈=−231.1 kJ/mol

Conversion of syngas to methanol using copper catalysts in the gas phase or liquid-phase catalysts are exothermic and also less sensitive to poisons.

CO+2H₂CH₃OH(l) ΔH°₂₉₈=−128.2 kJ/mol

There is syngas methanation that is highly exothermic:

2CO+2H₂→CH₄+CO₂ ΔH°₂₉₈=−247.3 kJ/mol

And there are many other highly exothermic reactions that can use syngas and preferably produce useful high-carbon content chemicals of commercial use.

This thermochemistry is well known (R. F. Probstein & R. E. Hicks, “Synthetic Fuels,” McGraw-Hill, N.Y., 1982, 490 pp.). And all of these highly exothermic reactors produce high-grade useful energy. So they all can convert syngas with enough exothermicity to make large amounts of electricity, steam and heat. Importantly, these exothermic reactors can substitute very well for fuel cells. Thus, it is the purpose of this patent to cover methods and process systems to convert waste to energy without burning the waste but to sequester the carbon of the waste so carbon gases are not released

The composition of the syngas was determined in detail by the author in a recently completed gas test using the Bear Creek Pilot plant where solid waste was steam/CO₂ reformed to make syngas. The syngas composition is shown in Table 1 below.

TABLE 1
Results from Pilot Plant Gas Test By Steam/CO2 Reforming Of Solid
Waste
H2	Hydrogen	62.71	vol %
CO	Carbon Monoxide	18.57
CO2	Carbon Dioxide	10.67
CH4	Methane	7.58
C2H6	Ethane	0.48
C3 TO C6	Propane through hexane	<0.01
C6H6	Benzene	<17	ppm
COS	Carbonyl Sulfide	4	ppm
CS2	Carbon Disulfide	0.05	ppm
H2S	Hydrogen Sulfide	<5	ppm
C10H8	Naphthalene	2.6	ppb
C10H7CH3	2-Methylnaphthalene	~0.6	ppb
C12H8	Acenaphthalene	~0.4	ppb
C12H8O	Dibenzofuran	0.36	ppb
PCDF + PCDD	Polychlorinated-	0.0041	ppt TEQ
	dibenzofurans + Dioxins

The pilot process configuration used to conduct these tests is described in a recent publication (T. R. Galloway, F. H. Schwartz and J. Waidl, “Hydrogen from Steam/CO₂ Reforming of Waste,” Nat'l Hydrogen Assoc., Annual Hydrogen Conference 2006, Long Beach, Calif. Mar. 12-16, 2006).

What has been found experimentally was that the syngas was very rich in hydrogen and carbon monoxide and also quite pure. For fuel cells the key poisons, such as carbonyl sulfide, hydrogen sulfide, carbon disulfide, hydrogen chloride, and polychlorinated organics were identified. For Fischer-Tropsch, methanol synthesis, methanation, etc., this syngas is very acceptable.

Another important part of power recovery is to reduce the energy losses of the waste-reforming kiln. Previously covered was a process interface involving a conventional kiln, followed by a desulfurizer and a high temperature filter in the CIP of patent application Ser. No. 10/719,504 (examined by Ryan/Lewis) filed Nov. 21, 2003. The problem is that the kiln was operated at a high temperature, followed by an even higher temperature steam/CO₂ reformer which is then followed by the desulfurizer and high temperature filter—all energy-inefficient from heat losses from the process units themselves and from the complex of hot process piping. Also this was expensive, as well.

Regarding Fischer-Tropsch, the challenge was to develop a process train where the Fischer-Tropsch unit could produce enough high carbon product, such as high density, unsaturated paraffin wax containing little hydrogen, so that the carbon in the waste feed would be sequestered in this product, without significant carbon emissions leaving the process anywhere else. The Fischer-Tropsch train also had to produce steam for a steam-turbo-generator to make enough electricity to drive the process plant.

SUMMARY OF THE INVENTION

This invention relates to a power recovery process in waste steam/CO₂ reformers whereby a waste stream can be made to release energy without having to burn the waste or the syngas and consume oxygen and have large carbon dioxide emissions. This invention does not make use of fuel cells as its critical component but makes use of highly exothermic chemical reactors using syngas to produce large amounts of heat, such as Fischer-Tropsch. It also relates to control or elimination of the emissions of greenhouse gases in the power recovery process of this invention with the goal of producing energy in the future carbonless world economy.

The significant improvement in this process train for power recovery is an improved duplex kiln that combines the functions of the conventional kiln, steam/CO₂ reformer, and the high temperature filter into a single unit. The desulfurizer/getter bed can operate at a lower temperature and can follow the duplex kiln.

Further improvements that involve using the above duplex kiln and getter bed in a process train that includes a heat exchanger/steam superheater are disclosed that will rapidly quench-cool the syngas down from 300 to 500° C. (600 to 900° F.) temperature range of the desulfurizer to 150° C. (300° F.). The concept here is to rapidly quench the syngas so that the undesirable heavy hydrocarbon recombination reactions (i.e. “De-Novo”) that make dioxins and furans do not have time to form, since they are kinetically limited. These recombination reactions involve multi-step polymerization &/or ring formation and are slowed as the temperatures are lowered.

Next, the Brayton cycle turbine is used to recover energy from the high temperature gas, while cooling it for feeding to both the Fischer-Tropsch unit to produce the high-carbon content product for sequestering the carbon and the shift converter and pressure-swing absorber to produce hydrogen fuel.

As an alternative, a conventional indirectly fired, calcining kiln can be used where the very hot syngas exiting from the steam reformer can heat carbon dioxide gas or air to supply the indirect heat to the kiln to take over from the natural gas burners commonly used.

The Fischer-Tropsch reactor, as discussed above, is highly exothermic and produces vast quantities of high quality steam for operating a conventional steam turbo-generator system for powering the plant.

So what has been accomplished in this invention is the conversion of a waste stream by steam/CO₂ reforming to produce a syngas that is used in a Fischer-Tropsch reactor to produce energy and sequester the carbon of the waste at the same time.

It will be obvious for those skilled in the art, to replace the Fischer-Tropsch reactor with other highly exothermic reactors that produce a high-carbon content product for sequestering carbon and produce large amounts of energy. Also interchanging the syngas cleaning process units around while keeping the same functionality are covered under this invention. All such generalizations are covered by this invention.

BRIEF DESCRIPTION OF THE DRAWINGS

In FIG. 1, there is shown the improved duplex kiln that combines the functions of the conventional kiln, steam/CO₂ reformer, and the high temperature filter into a single unit.

In FIG. 2, is shown how the new concept of a duplex kiln can be followed by a desulfurizer/getter bed, quench heat exchanger for provided superheated steam for the duplex kiln, and the Brayton turbine for generating power by cooling the syngas, which is then fed to both a Fischer-Tropsch reactor and Shift/Pressure Swing Absorption System.

In FIG. 3 is shown the advantage of using a Fischer-Tropsch process consisting only of two units that simply makes the high-carbon product, makes steam and accomplishes sequestration carbon balance in capturing nearly all of the carbon dioxide emissions.

FIG. 4 shows the spiral heat exchange Fischer-Tropsch Reactor.

In FIG. 5 is shown how the Fischer-Tropsch process that makes paraffin wax product for carbon sequestration accomplishes recycling the light hydrocarbons consisting of methane, ethane, ethylene, propane, etc. to avoid their emissions as powerful greenhouse gases (i.e. methane) and also recycling the lighter hydrocarbons to help maintain a higher H₂/CO ratio of the syngas. It also describes how a waste stream can be made to release energy without having to burn the waste or the syngas. At the same time the waste can be converted into use carbon-containing fertilizer, hydrogen fuel, and a carbon-sequestering, high-carbon content product of important commercial value, such as unsaturated, high-density paraffin wax.

FIG. 6 shows the use of a conventional indirectly fired, calcining kiln where the very hot syngas exiting from the steam reformer can heat carbon dioxide gas or air to supply the indirect heat to the kiln to take over from the natural gas burners commonly used. The process flowsheet layout is given in FIG. 7.

DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS

In FIG. 1, the functionality of the preferred embodiment of FIG. 1 is combined into a single kiln to increase the thermal efficiency and reduce the cost. This design is referred to as the Duplex Kiln. This new kiln concept combines all the high temperature process components of the embodiment shown in FIG. 1 into a single unit, greatly reducing heat loss and thus achieving very much higher thermal efficiency.

Referring to FIG. 1, the waste stream 100 is fed through a sealed lockhopper 102 down into the kiln 103. The lockhopper is of novel design in that these two sliding port rectangular knife gate valves are spaced apart so that the top valve opens and a column of waste is dropped down through this valve, at which point it is then closed, cutting through the column of waste. Then the knife gate valve below is opened dropping the portion of waste captured between these valves is dropped down into the kiln. Next, the bottom valve is closed and the top valve opened, thus repeating the cycling. What is novel is that these sliding port rectangular knife gates have hardened sliding gate edges driven by powerful hydraulic actuators that are capable of cutting through a column of waste, such as municipal solid waste. This is important since the column of waste will be produced by intermittent loading from external sources and will be of varying height depending on how quickly this waste is added to the column. In this way a very intermittent waste stream is converted to a steady stream of regular pulses of fixed amounts of waste are fed into the kiln, making the kiln operation, for all practical measures, a continuous process.

Referring to FIG. 1, once the waste 100 enters the kiln 104, the hollow flight auger 106 moves this portion of waste admitted by the knife gate lockhopper slowly along the kiln from left to right. This waste is heated by very hot gas passing inside of these screw auger flights 106. The outside of the kiln in this region is heated by electrical heat tracing 108 to reduce heat loss. The kiln body 110 itself in this example is 48″ in diameter and 22 ft long with the wall made of high temperature alloy, such as Incoloy 800H. The waste is being steam/CO₂ reformed in the region 103 of the screw between these hollow flights 106 where the temperatures range from around 200° F. in the feed end at the left to around 900° F. leaving the last screw flight on the right, at which point the solids remaining after reforming drop out at the solids exit, 112.

Referring to FIG. 1, after the syngas leaves the screw flights moving to the right, they enter the annular regions 114 and 116 which are separated by a perforated heavy wall cylinder 118 of Incoloy 800 HT which is heated inductively by the outside coils 120. This syngas moves to the right through this double annular region where it is heated from 480-1050° C. (900 to 1900° F.). Within this annular region are located spiral flights to swirl the gas in a gas cyclone operation for removal of entrained solids. At its highest temperature this very hot syngas passes through a porous alumina filter 122 on which any fine particulate entrained material is deposited. As the solids build up on this porous filter they can be removed by pulsing an external steam source 124 entering through conduit 126 through rotary seal 128. As the solids deposited on this filter 122 are blown off, they are moved to the left by spiral flights 130 to remove these fine solids out the exit pipe 112. The syngas, which is now cleaned of fines, passes through large ports 132 in the central shaft 134. Inside this shaft there are swirl vanes 136 that thorough mix the steam 124 added to this region with the syngas to complete the reforming chemistry. This finished syngas passes through this swirl vane region 138 from right to the left inside the central shaft 134. As this finished syngas leaves the swirl vane region it is blocked by plug 140 at which point the finished syngas passes through large ports 142 in the central to enter into the internal region of the hollow flights 144. This very hot finished syngas at about 1000° C. (1800° F.) is now rapidly cooled as it gives up its sensible heat to the incoming solid waste 100 passing countercurrently in the region 103 outside of these hollow flights 106. Once this finished syngas is cooled to about 150-480° C. (300-900° F.) it passes from the internal volume of the last hollow flight 146 through large ports 148 into the inside of the central shaft 150. This shaft 150 is fitted with a rotary seal 152 so the finished cooled syngas passes out of the kiln via conduit 154. The outer shell of the kiln 110 is egg-shaped in cross section 156 to allow ample regions for the syngas to pass outside the hollow flights. This kiln shell is fitted with flanges 158 at both ends that includes bearings 160 through which the internal central shaft 134 rotates. There is a motor drive and gear assembly 162 that rotates the central shaft 134 around which are the hollow flights 106, the annular heated cylinder 118 and its spiral flights 130.

Now referring to FIG. 2, the above kiln 104 is shown interfaced to the shift/PSA unit using its exhaust recycle 236 and the Fischer-Tropsch process 220 recycling the methane and light hydrocarbon gases via 222 back to the steam/CO₂ reforming kiln. These streams involving the waste 100, the fuel cell anode exhaust 210 and the Fischer-Tropsch overhead stream 222 are combined with the proper amount of steam 224 to carryout the steam/CO₂ reforming inside the kiln 104. Particularly important to note is that these two recycle steams both involve greenhouse gases, CO₂ and CH₄, which would otherwise be released to the atmosphere. For example, we find a long forgotten reaction, that has not been commercially exploited, can be accomplished. It is:

CH₄+CO₂→2H₂+2CO

In our improved process these problem gases are not released to environment but profitably utilized.

This reaction equilibrium favors the H₂ and CO at temperatures around or above 700° C. (1300° F.) so that when the syngas moves from the hollow flight section of kiln 104 in FIG. 2 into the double annular regions 114, and 116, which involves temperatures around 1050° C. (1900° F.), so that this reaction is almost 100% completed. Note that this consumes CO₂ and produces more syngas that can be used in the fuel cell as well as in Fischer-Tropsch. This reaction is favored at the high temperatures of our steam/CO₂ reformer wherein the syngas of H₂/CO ratio around 1.0 is produced. Also using our '465 patent and its continuation, the reaction:

CH₄+H₂O→3H₂+CO

can be accomplished in our steam/CO₂ reformer to produce a syngas of H₂/CO=3, so again we can adjust the H₂/CO ratio to whatever Fischer-Tropsch needs (i.e. say 0.7 to 1.4). So recycling this combination of CO₂ and CH₄ as well as other light hydrocarbons is of significant advantage.

Here, using the empirical formula for typical municipal solid waste, we show two reactions: first the conventional steam reforming using a stoichiometric amount of steam to make just CO and H₂.

Example #1

Stoichiometric Steam

C₁H_1.67O_0.47+0.53H₂O→CO+1.36H₂

In this case 1 kg of waste will yield 1.45 kg of syngas.

Example #2

Superstoichiometric in CO₂ and C₂H₄

By contrast, here is the improved reforming reaction which involves a substoichiometric amount of steam but has the light hydrocarbon Fischer-Tropsch and shift/PSA overhead represented for simplicity by C₂H₄, plus CO₂ and H₂, added.

C₁₁H_1.67O_0.47+0.55C₂H₄+0.69H₂+1.5CO₂+0.04H₂O→3.68CO+2.67H₂  [1]

In this case, 1 kg of waste will yield 5.11 kg of syngas, which is a very significant 350% increase in the mass of syngas product formed from a given mass of waste.

This achieves the formation only of CO and H₂, and thus is stoichiometric which respect to the combination of steam plus CO₂ plus C₂H₄. Thus, less steam (i.e. sub-stoichiometric) is required and greenhouse-problematic light hydrocarbons and CO₂ can be used in large amounts to achieve overall the stoichiometric conversion to syngas desired with a preferred H₂/CO ratio around 0.73. CH₄, C₃H₈ or other light hydrocarbons are actually involved in the real world in combination with C₂H₄ shown in the reaction. In a typical Fischer-Tropsch process all of these light hydrocarbons are formed and would be in the recycle. Thus, the use of Fischer-Tropsch is simplified. The CH₄ is produced as the major part of the waste light gases coming off the tops of the Fischer-Tropsch gravity separator. No distillation is required. Any other light gases that are also carried along with the waste CH₄ can go back to the steam reformer as well.

We believe that it could even be economic to recycle 100% of the CO₂ and whatever optimum amount of CH₄ from Fischer-Tropsch to make the whole system balance, sequestering all of the CO₂ while making useful paraffin wax that is high in carbon content, high in commercial value, and not burned in its lifecycle. So in FIG. 2 the Improved Carbon Sequestration can be accomplished as shown by the carbon balance. Thus, by adjusting the carbon in the Shift/PSA recycle 236 plus the carbon in the Fischer-Tropsch overhead recycle 222, the carbon in the waste 100 is made to just equal the carbon in the Fischer-Tropsch product, paraffin wax 224. So what could be accomplished is the total sequestration of the carbon in the waste by the formation of the high carbon content paraffin wax. It will be obvious to one skilled in the art to identify other Fischer-Tropsch products that can be selected that will accomplish this total carbon sequestration. Commercially, there may be an economic optimum situation where one may not want to sequester all of the carbon in the waste, but this example shows that this is theoretically possible with our new concept.

FIG. 3 shows how simplified the Fischer-Tropsch process can become in this new steam/CO₂ reforming process of waste conversion with recycle streams. Referring to FIG. 3, the cleaned and warm syngas 154 from the kiln 104 shown in FIG. 2 is passed into an air cooler 300 where it is temperature-controlled to about 180° C. (350° F.) at the exit of the air cooler 301. This stream 301 is then fed to the compressor 302 where the pressure is increased from around one atmosphere (15 psig) to 3.5 MPa (468 psig) at its outlet 303 which feeds the Fischer-Tropsch reactor 305 containing a Fischer-Tropsch catalyst 304 within its vertical tubes. This reactor carries out the synthesis reactions making a range of hydrocarbons from CH₄, light hydrocarbons up to heavy hydrocarbon paraffins while releasing a very substantial amount of heat.

The reaction below shows how the syngas produced in reaction [1] above can be used to make high carbon-content products such as high density, unsaturated paraffin wax as a means of sequestering carbon in a product that has significant commercial value. The other compounds formed can be recycled back into reaction [1] so that they are not released to the environment. Also there are some CO₂, H₂ and H₂O that can be recycled as well from the shift converters and PSA units. Again, C₂H₄ is being used to represent the large range of light hydrocarbon gases for simplicity of discussion.

3.68CO+2.67H₂→0.055C₂₀H₃₀+0.55C₂H₄+1.47CO₂+0.734H₂0  [2]

The temperature, pressure, H₂/CO ratio of the syngas, and the residence time together control the molecular range of the Fischer-Tropsch products 316 that is then fed into the separator 318. The mixture of hydrocarbons gravimetrically separates here into three fractions: water 320, paraffins 322 and light gases overhead 222. So it can be seen that this is a very simple process, not requiring complex distillation, crystallization, or boiling. And it is this interfacing with the steam/CO₂ reforming kiln and the fuel cell that makes such a simplification possible and novel.

It will be obvious to one skilled in the art to identify other Fischer-Tropsch reactor concepts different from the conventional catalyst-packed, multi-tube exothermic but isothermal reactor. Such a reactor consists of a spiral heat exchanger where the catalyst is placed in the spiral annular regions (made by Alfa-Laval, particularly common in Europe). Such a design is shown in FIG. 4 that shows the spiral heat exchange Fischer-Tropsch Reactor wherein the syngas feed 500 enters into the spiral annuli 512 that are packed with supported catalyst. The converted syngas consisting of the light gases and some unconverted syngas leaves from nozzle 502. These annuli are immersed in water 508 with its level controlled at the end of the annuli. The exothermic heat boils the water to make steam in disengaging bell 506 which leaves via 504 to feed a steam/turbo generator. The boiler feedwater enters via nozzle 514. At the bottom of the reactor the liquid paraffin wax forms within and drains out the exit of annuli at 518 leaves nozzle 516. Paraffin wax recycle from the separator 318 (shown in FIG. 3), enters the outer spiral annulus through nozzle 510.

Finally, FIG. 5 describes how a waste stream can be made to release energy without having to burn the waste or the syngas. At the same time the waste can be converted into use carbon-containing fertilizer, hydrogen fuel, and a carbon-sequestering, high-carbon content product of important commercial value, such as unsaturated, high-density paraffin wax.

Referring to FIG. 5, the waste stream enters the process as stream 100 into rotary kiln 104 where it is steam/CO₂ reformed via the chemistry in reaction [1] above to form a high-hydrogen content syngas stream 154 where its high temperature heat is used in boiler 416 to produce steam 418, as well as a high carbon content product steam 112 that contains glass and metal as well as a high NPK fertilizer solid particulate of commercial value. The reaction in kiln 104 uses light gases, CO₂, and steam recycled as 402 from downstream process units consisting of shift converter 458, pressure-swing absorber 456, Fischer-Tropsch reactor 452 and its paraffin product separator 454. This recycle stream 402 comes from the combined streams 400 made up of 222 and 306 plus stream 414 made up of streams 410 and 412. The syngas 154 produced in kiln 104 is split into two streams 303 and 404, with 303 feeding the Fischer-Tropsch units 452 and 454 producing paraffin product 322 and stream 404 feeding the Shift 458 and PSA 456 that produce hydrogen product 408 and optional CO₂ at 409. In addition, the Fischer-Tropsch unit 452 is highly exothermic and produces large amounts of steam 420 that can be used to drive a steam turbine to make electricity to run the plant and be exported for sale. Water streams 316 and 320 are used to make up boiler feedwater. So the net result of this linkage and interface of the three process blocks of steam-reforming of waste to the Shift/PSA and the Fischer-Tropsch is to convert the waste to hydrogen fuel and into high-carbon NPK fertilizer and carbon-sequestering paraffin with a huge release of heat. And this is done without burning the waste and without releasing the huge amounts of greenhouse gases typical of a combustion process. This patent teaches the way of the future of destroying waste and producing steam, heat and useful products in the carbonless economy of the future.

FIG. 6 shows the use of a conventional indirectly fired, calcining kiln where the very hot syngas exiting from the steam reformer can heat carbon dioxide gas or air to supply the indirect heat to the kiln to take over from the natural gas burners commonly used. Now referring to FIG. 6, the above kiln 104 is shown interfaced to the shift/PSA unit using its exhaust recycle 236 and the Fischer-Tropsch process 220 recycling the methane and light hydrocarbon gases via 222 back to the steam/CO₂ reforming kiln. These streams involving the waste 100, the fuel cell anode exhaust 210 and the Fischer-Tropsch overhead stream 222 are combined with the proper amount of steam 224 to carryout the steam/CO₂ reforming inside the kiln 104.

This reaction equilibrium favors the H₂ and CO at temperatures around or above 700° C. (1300° F.) so that when the syngas moves from the conventional calcining kiln 104 in FIG. 6 into the steam/CO₂ reformer, 600, which involves temperatures around 1050° C. (1900° F.), so that this reaction is almost 100% completed. Following this reactor, 600, stream 205 passes into heat exchanger 206 where in an inert gas, such as CO₂ produced elsewhere in the process, or outside air, 208 is heated by the very hot syngas in steam 205 to be fed via stream 602 into a series of multiple indirect burners 604 of the conventional kiln. These burners, conventionally used for natural gas, would be replaced with an injection jet that would supply the very hot gas directly into the oven-furnace area of the conventional kiln. The rest of the process is the same as in FIG. 2.

Example #3

CO₂ Enriched Syngas

A further improvement in the reforming reaction which involves a substoichiometric amount of steam but has the light hydrocarbon Fischer-Tropsch and shift/PSA overhead represented for simplicity by C₂H₄, plus CO₂ and H₂, added.

C₁H_1.67O_0.47+0.2567C₂H₄+0.2CO₂+1.434H₂O→1.123CO+0.591CO₂+3.029H₂

In this case, the reformation reaction is allowed to form CO₂ in the syngas, such that the stoichiometric ratio of (H₂−CO₂)/(CO+CO₂)=1.42 which is favorable for the Fischer-Tropsch reaction as follows:

1.123CO+0.591CO₂+3.029H₂→0.0757C₂₀H₃₀+0.2CO₂+1.904H₂O

This achieves an increase in the amount of paraffin formed and greenhouse-problematic light hydrocarbons and CO₂ are entirely recycle back into the reformer, with a small portion of the water condensed as product water. Thus, the use of Fischer-Tropsch is further simplified. As before, the CH₄ is produced as the major part of the waste light gases coming off the tops of the Fischer-Tropsch gravity separator. No distillation is required. Any other light gases that are also carried along with the waste CH₄ can go back to the steam reformer as well. The important result is that there are no CO₂ emissions since the CO₂ formation in the Fischer-Tropsch is entirely recycled back into the reformer.

So in FIG. 2 what has been achieved in this case is the entire elimination (i.e. stream 216 is zero) of the Shift/PSA process step at a capital savings. Likewise, in FIG. 5, stream 404 is zero. So what is accomplished in this case is the total sequestration of the carbon in the waste by the formation of the high carbon content paraffin wax. It will be obvious to one skilled in the art to identify other Fischer-Tropsch products that can be selected that will accomplish this total carbon sequestration. Commercially, there may be an economic optimum situation where one may not want to sequester all of the carbon in the waste, but this example shows that this is theoretically possible with our new concept.

Example #4

Process Flowsheet Mass Balance

The process flowsheet layout based on FIG. 5, but with all the process details, was completed and the mass balance done where the flow split of sending syngas to Shift/PSA system and to Fischer-Tropsch was varied. The chemistry within the steam reformer was given in reaction [1] above and in the Fischer-Tropsch unit in reaction [2] above. The results have been summarized in Table 2 below, showing how the products of the waste-to-energy plant, such as hydrogen, water, carbon dioxide and paraffin can be varied depending on the needs of the customer and the marketplace. The case is for wet waste with 15% water and a scale of 4 tonnes/day.

TABLE 2
The Process Choices Set the Products That Are Made
Shift	Fischer	H2					Net
PSA	Tropsch	Re-	H2	Water	CO2	Paraffin	Electricity
%	%	cycle	Kg/hr	Kg/hr	Kg/hr	Kg/hr	kWe
62	38	Low	490	−1547	6587	859	185
62	38	Hi	395	−922	5823	1093	235
50	50	Hi	254	0	4096	1441	310
38	62	Hi	232	229	4416	1526	328
19	81	Hi	46	1475	2888	1984	426
0	100	Low	0	2264	1928	2290	492
0	100	Hi	0	3842	0	2875	618
0	100	OptCO2	0	1594	0	3851	861

As the process option is shifted more toward Fischer-Tropsch, more paraffin, water, and electricity products are made and less hydrogen fuel produced. With all Fischer-Tropsch, no hydrogen and no carbon dioxide are produced and the amount of water, paraffins, and electricity are maximized. The electricity is a net number, after the internal electricity consumption within the plant is removed and used. The last line in Table 2 covers the case presented in Example #3, showing a great increase in Fischer-Tropsch product as well as electricity generated.

Example #5

Process Flowsheet Heat & Mass Balance for Maximum Hydrogen

The process flowsheet layout is given in FIG. 7.

The detailed heat and mass balance for the Process flowsheet for maximizing hydrogen production using a cellulose feed is given below:

STREAM SUMMARY - Cellulose
Stream Number		1	3	4
Stream Name		Strm 1	Strm 3	Strm 4
Thermo Method Option		GLOBAL	GLOBAL	GLOBAL
Vapor Fraction		0	1	0.2441006
Temperature	C.	25	50	23.97223
Pressure	kg/cm2	1.18822	18.30545	1.18822
Enthalpy	kcal/hr	−568658.428	5939.92631	−562718.501
Entropy	kcal/K/hr	−1601.801	−55.70444	−1562.611
Vapor Density	kg/m3		7.08434	0.5120275
Liquid 1 Density	kg/m3	1145.39015		1145.55729
Liquid 1 Specific Gravity	60 F@STP	1.14771		1.14767
Vapor Cp	kcal/kgmo/C.		7.00204	6.96086
Vapor Cv	kcal/kgmo/C.		4.97593	4.97023
Liquid 1 Cp	kcal/kgmo/C.	74.1567		73.88081
Vapor Viscosity	cP		0.012585	0.0115689
Liquid 1 Viscosity	cP	1.35416		1.3574
Vapor Thermal Conductivity	kcal/m/hr/C.		0.0869059	0.0769098
Liquid 1 Thermal Conductivity	kcal/m/hr/C.	0.0433377		0.0434341
Vapor Flowrate	m3v(NTP)/hr		382.50232	391.4952
Liquid 1 Flowrate	m3l(NTP)/hr	0.6580313		0.6579975
Liquid 2 Flowrate	m3l(NTP)/hr	249.06799		247.15388
Molecular Weight		31.1575	10.6878	26.2756
Molar Flowrate	kgmol/hr	54.4973	17.0678	71.5652
Mass Flowrate	kg/hr	1697.999625	182.4172328	1880.418569
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	2.20858	4.402E−15	2.20858
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	52.2888	0.043561	52.3323
48: CARBON MONOXIDE	kgmol/hr	0	5.66596	5.66596
1: HYDROGEN	kgmol/hr	0	11.3563	11.3563
2: METHANE	kgmol/hr	0	0.002054	0.002054
49: CARBON DIOXIDE	kgmol/hr	0	0	0
65: ACETYLENE	kgmol/hr	0	0	0
40: BENZENE	kgmol/hr	0	0	0
3: ETHANE	kgmol/hr	0	1.442E−10	1.442E−10
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	0	1.332E−09	1.332E−09
1088: PHENOL	kgmol/hr	0	0	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	0	9.511E−16	9.511E−16
6: N-BUTANE	kgmol/hr	0	0	0
5: I-BUTANE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
66: PROPYNE	kgmol/hr	0	1.797E−16	1.797E−16
3114: 2-BUTYNE	kgmol/hr	0	1.76E−09	1.76E−09
Total	kgmol/hr	54.4973	17.0678	71.5652
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	4.05264114	2.57913E−14	3.086108891
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	95.94750566	0.255223286	73.12534584
48: CARBON MONOXIDE	molar %	0	33.1967799	7.91719998
1: HYDROGEN	molar %	0	66.53640188	15.8684668
2: METHANE	molar %	0	0.012034357	0.00287011
49: CARBON DIOXIDE	molar %	0	0	0
65: ACETYLENE	molar %	0	0	0
40: BENZENE	molar %	0	0	0
3: ETHANE	molar %	0	8.44866E−10	2.01495E−10
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	0	7.80417E−09	1.86124E−09
1088: PHENOL	molar %	0	0	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	0	5.57248E−15	1.329E−15
6: N-BUTANE	molar %	0	0	0
5: I-BUTANE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
66: PROPYNE	molar %	0	1.05286E−15	2.511E−16
3114: 2-BUTYNE	molar %	0	1.03118E−08	2.4593E−09
Total	molar %	100	100	100
Stream Number		5	6	7
Stream Name		Strm 5	Strm 6	Strm 7
Thermo Method Option		GLOBAL	GLOBAL	GLOBAL
Vapor Fraction		1	1	1
Temperature	C.	500	500	500
Pressure	kg/cm2	1.15309	1.15309	1.15309
Enthalpy	kcal/hr	410945.746	433890.844	18334.3418
Entropy	kcal/K/hr	929.212	1113.85	34.89752
Vapor Density	kg/m3	0.4624083	0.351273	6.12671
Liquid 1 Density	kg/m3
Liquid 1 Specific Gravity	60 F@STP
Vapor Cp	kcal/kgmo/C.	13.60159	10.36102	167.62174
Vapor Cv	kcal/kgmo/C.	11.60822	8.37071	165.50288
Liquid 1 Cp	kcal/kgmo/C.
Vapor Viscosity	cP	0.026881	0.0258333	0.0166158
Liquid 1 Viscosity	cP
Vapor Thermal Conductivity	kcal/m/hr/C.	0.0914342	0.0974512	0.0383433
Liquid 1 Thermal Conductivit	kcal/m/hr/C.
Vapor Flowrate	m3v(NTP)/hr	1603.82705	2110.29555	7.07083
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr
Molecular Weight		26.2756	19.9695	342.3019
Molar Flowrate	kgmol/hr	71.5652	94.1646	0.315511
Mass Flowrate	kg/hr	1880.418569	1880.41998	108.0000148
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	2.20858	0.445562	0.315511
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	52.3323	42.2031	0
48: CARBON MONOXIDE	kgmol/hr	5.66596	2.08022	0
1: HYDROGEN	kgmol/hr	11.3563	24.9749	0
2: METHANE	kgmol/hr	0.002054	7.81226	0
49: CARBON DIOXIDE	kgmol/hr	0	16.5541	0
65: ACETYLENE	kgmol/hr	0	5.637E−12	0
40: BENZENE	kgmol/hr	0	5.338E−16	0
3: ETHANE	kgmol/hr	1.442E−10	0.00007558	0
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	1.332E−09	5.602E−07	0
1088: PHENOL	kgmol/hr	0	1.121E−15	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	9.511E−16	2.044E−10	0
6: N-BUTANE	kgmol/hr	0	7.099E−14	0
5: I-BUTANE	kgmol/hr	0	4.108E−14	0
27: I-BUTENE	kgmol/hr	0	1.714E−14	0
27: I-BUTENE	kgmol/hr	0	1.714E−14	0
66: PROPYNE	kgmol/hr	1.797E−16	7.64E−15	0
3114: 2-BUTYNE	kgmol/hr	1.76E−09	0.094368	0
Total	kgmol/hr	71.5652	94.1646	0.315511
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	3.086108891	0.473173571	100
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	73.12534584	44.81843495	0
48: CARBON MONOXIDE	molar %	7.91719998	2.209131669	0
1: HYDROGEN	molar %	15.8684668	26.52259979	0
2: METHANE	molar %	0.00287011	8.29638739	0
49: CARBON DIOXIDE	molar %	0	17.57996105	0
65: ACETYLENE	molar %	0	5.98633E−12	0
40: BENZENE	molar %	0	5.6688E−16	0
3: ETHANE	molar %	2.01495E−10	8.02637E−05	0
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	1.86124E−09	5.94916E−07	0
1088: PHENOL	molar %	0	1.19047E−15	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	1.329E−15	2.17067E−10	0
6: N-BUTANE	molar %	0	7.53893E−14	0
5: I-BUTANE	molar %	0	4.36257E−14	0
27: I-BUTENE	molar %	0	1.82022E−14	0
27: I-BUTENE	molar %	0	1.82022E−14	0
66: PROPYNE	molar %	2.511E−16	8.11345E−15	0
3114: 2-BUTYNE	molar %	2.4593E−09	0.100216005	0
Total	molar %	100	100	100
Stream Number		8	9	10
Stream Name		Strm 8	Strm 9	Strm 10
Thermo Method Option		GLOBAL	CHANGED	GLOBAL
Vapor Fraction		1	1	1
Temperature	C.	500	267	499.83311
Pressure	kg/cm2	1.15309	1.03323	1.03323
Enthalpy	kcal/hr	415533.433	121.05274	415654.486
Entropy	kcal/K/hr	1075.271	0.1986506	1096.144
Vapor Density	kg/m3	0.3322084	0.4077036	0.2977284
Liquid 1 Density	kg/m3
Liquid 1 Specific Gravity	60 F@STP
Vapor Cp	kcal/kgmo/C.	9.83285	8.59419	9.83058
Vapor Cv	kcal/kgmo/C.	7.84266	6.57159	7.84075
Liquid 1 Cp	kcal/kgmo/C.
Vapor Viscosity	cP	0.0253123	0.0189224	0.0253076
Liquid 1 Viscosity	cP
Vapor Thermal Conductivity	kcal/m/hr/C.	0.0985838	0.0343274	0.0985339
Liquid 1 Thermal Conductivity	kcal/m/hr/C.
Vapor Flowrate	m3v(NTP)/hr	2103.22472	1.24398	2104.4687
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr
Molecular Weight		18.8858	18.0153	18.8853
Molar Flowrate	kgmol/hr	93.849	0.055508	93.9046
Mass Flowrate	kg/hr	1772.413444	0.999993272	1773.416542
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	0.130051	0	0.130051
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	42.2031	0.055508	42.2586
48: CARBON MONOXIDE	kgmol/hr	2.08022	0	2.08022
1: HYDROGEN	kgmol/hr	24.9749	0	24.9749
2: METHANE	kgmol/hr	7.81226	0	7.81226
49: CARBON DIOXIDE	kgmol/hr	16.5541	0	16.5541
65: ACETYLENE	kgmol/hr	5.637E−12	0	5.637E−12
40: BENZENE	kgmol/hr	5.338E−16	0	5.338E−16
3: ETHANE	kgmol/hr	0.00007558	0	0.00007558
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	5.602E−07	0	5.602E−07
1088: PHENOL	kgmol/hr	1.121E−15	0	1.121E−15
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	2.044E−10	0	2.044E−10
6: N-BUTANE	kgmol/hr	7.099E−14	0	7.099E−14
5: I-BUTANE	kgmol/hr	4.108E−14	0	4.108E−14
27: I-BUTENE	kgmol/hr	1.714E−14	0	1.714E−14
27: I-BUTENE	kgmol/hr	1.714E−14	0	1.714E−14
66: PROPYNE	kgmol/hr	7.64E−15	0	7.64E−15
3114: 2-BUTYNE	kgmol/hr	0.094368	0	0.094368
Total	kgmol/hr	93.849	0.055508	93.9046
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	0.138574732	0	0.138492683
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	44.96915257	100	45.00162931
48: CARBON MONOXIDE	molar %	2.216560645	0	2.215248241
1: HYDROGEN	molar %	26.61179128	0	26.5960347
2: METHANE	molar %	8.324286886	0	8.319358157
49: CARBON DIOXIDE	molar %	17.6390798	0	17.62863587
65: ACETYLENE	molar %	6.00646E−12	0	6.0029E−12
40: BENZENE	molar %	5.68786E−16	0	5.68449E−16
3: ETHANE	molar %	8.05336E−05	0	8.04859E−05
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	5.96916E−07	0	5.96563E−07
1088: PHENOL	molar %	1.19447E−15	0	1.19376E−15
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	2.17797E−10	0	2.17668E−10
6: N-BUTANE	molar %	7.56428E−14	0	7.5598E−14
5: I-BUTANE	molar %	4.37724E−14	0	4.37465E−14
27: I-BUTENE	molar %	1.82634E−14	0	1.82526E−14
27: I-BUTENE	molar %	1.82634E−14	0	1.82526E−14
66: PROPYNE	molar %	8.14074E−15	0	8.13592E−15
3114: 2-BUTYNE	molar %	0.100553016	0	0.10049348
Total	molar %	100	100	100
Stream Number		11	12	14
Stream Name		Strm 11	Strm 12	Strm 14
Thermo Method Option		GLOBAL	GLOBAL	GLOBAL
Vapor Fraction		1	1	0.6603743
Temperature	C.	875	875	4.4
Pressure	kg/cm2	0.9981011	0.9981011	0.894778
Enthalpy	kcal/hr	784222.539	817911.152	−407395.817
Entropy	kcal/K/hr	1489.791	1599.197	−1013.643
Vapor Density	kg/m3	0.193587	0.1609311	0.551586
Liquid 1 Density	kg/m3			1037.15161
Liquid 1 Specific Gravity	60 F@STP			0.9999917
Vapor Cp	kcal/kgmo/C.	11.06725	9.15389	7.20069
Vapor Cv	kcal/kgmo/C.	9.07945	7.16653	5.2086
Liquid 1 Cp	kcal/kgmo/C.
Vapor Viscosity	cP	0.0335965	0.032694	0.0119112
Liquid 1 Viscosity	cP			1.54882
Vapor Thermal Conductivity	kcal/m/hr/C.	0.1559868	0.1819838	0.0642739
Liquid 1 Thermal Conductivit	kcal/m/hr/C.			0.4896245
Vapor Flowrate	m3v(NTP)/hr	2104.4687	2531.34933	1671.63813
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr			182.78458
Molecular Weight		18.8853	15.7005	15.7005
Molar Flowrate	kgmol/hr	93.9046	112.9526	112.9526
Mass Flowrate	kg/hr	1773.416542	1773.412296	1773.412296
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	0.130051	4.408E−15	4.408E−15
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	42.2586	39.0616	39.0616
48: CARBON MONOXIDE	kgmol/hr	2.08022	16.9496	16.9496
1: HYDROGEN	kgmol/hr	24.9749	45.5062	45.5062
2: METHANE	kgmol/hr	7.81226	0.002054	0.002054
49: CARBON DIOXIDE	kgmol/hr	16.5541	11.4332	11.4332
65: ACETYLENE	kgmol/hr	5.637E−12	1.176E−10	1.176E−10
40: BENZENE	kgmol/hr	5.338E−16	0	0
3: ETHANE	kgmol/hr	0.00007558	1.443E−10	1.443E−10
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	5.602E−07	1.334E−09	1.334E−09
1088: PHENOL	kgmol/hr	1.121E−15	0	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	2.044E−10	9.52E−16	9.52E−16
6: N-BUTANE	kgmol/hr	7.099E−14	0	0
5: I-BUTANE	kgmol/hr	4.108E−14	0	0
27: I-BUTENE	kgmol/hr	1.714E−14	0	0
27: I-BUTENE	kgmol/hr	1.714E−14	0	0
66: PROPYNE	kgmol/hr	7.64E−15	1.798E−16	1.798E−16
3114: 2-BUTYNE	kgmol/hr	0.094368	1.761E−09	1.761E−09
Total	kgmol/hr	93.9046	112.953	112.953
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	0.138492683	3.90251E−15	3.90251E−15
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	45.00162931	34.58217135	34.58217135
48: CARBON MONOXIDE	molar %	2.215248241	15.0058874	15.0058874
1: HYDROGEN	molar %	26.5960347	40.28773029	40.28773029
2: METHANE	molar %	8.319358157	0.001818455	0.001818455
49: CARBON DIOXIDE	molar %	17.62863587	10.12208618	10.12208618
65: ACETYLENE	molar %	6.0029E−12	1.04114E−10	1.04114E−10
40: BENZENE	molar %	5.68449E−16	0	0
3: ETHANE	molar %	8.04859E−05	1.27752E−10	1.27752E−10
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	5.96563E−07	1.18102E−09	1.18102E−09
1088: PHENOL	molar %	1.19376E−15	0	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	2.17668E−10	8.42828E−16	8.42828E−16
6: N-BUTANE	molar %	7.5598E−14	0	0
5: I-BUTANE	molar %	4.37465E−14	0	0
27: I-BUTENE	molar %	1.82526E−14	0	0
27: I-BUTENE	molar %	1.82526E−14	0	0
66: PROPYNE	molar %	8.13592E−15	1.59181E−16	1.59181E−16
3114: 2-BUTYNE	molar %	0.10049348	1.55906E−09	1.55906E−09
Total	molar %	100	100	100
Stream Number		15	16	17
Stream Name		Strm 15	Strm 16	Strm 17
Thermo Method Option		GLOBAL	CHANGED	GLOBAL
Vapor Fraction		1	0	1
Temperature	C.	3.8523	3.8523	3.8523
Pressure	kg/cm2	0.7914549	0.7914549	0.7914549
Enthalpy	kcal/hr	2003.49464	−409399.315	2003.49464
Entropy	kcal/K/hr	191.0706	−1186.391	191.0706
Vapor Density	kg/m3	0.4889622		0.4889622
Liquid 1 Density	kg/m3		1037.60562
Liquid 1 Specific Gravity	60 F@STP
Vapor Cp	kcal/kgmo/C.	7.1993		7.1993
Vapor Cv	kcal/kgmo/C.	5.20779		5.20779
Liquid 1 Cp	kcal/kgmo/C.		18.09128
Vapor Viscosity	cP	0.0118909		0.0118909
Liquid 1 Viscosity	cP		1.57615
Vapor Thermal Conductivity	kcal/m/hr/C.	0.0640952		0.0640952
Liquid 1 Thermal Conductivit	kcal/m/hr/C.		0.4887219
Vapor Flowrate	m3v(NTP)/hr	1673.04691		1673.04691
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr		182.47997
Molecular Weight		14.5114	18.0184	14.5114
Molar Flowrate	kgmol/hr	74.6539	38.2987	74.6539
Mass Flowrate	kg/hr	1083.332604	690.0812961	1083.332604
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	4.408E−15	1.431E−20	4.408E−15
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	0.76774	38.2936	0.76774
48: CARBON MONOXIDE	kgmol/hr	16.9495	0.000132	16.9495
1: HYDROGEN	kgmol/hr	45.5061	0.000297	45.5061
2: METHANE	kgmol/hr	0.002054	2.301E−08	0.002054
49: CARBON DIOXIDE	kgmol/hr	11.4285	0.004673	11.4285
65: ACETYLENE	kgmol/hr	1.176E−10	3.819E−16	0
40: BENZENE	kgmol/hr	0	0	0
3: ETHANE	kgmol/hr	1.443E−10	2.064E−15	1.443E−10
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	1.334E−09	5.218E−14	1.334E−09
1088: PHENOL	kgmol/hr	0	0	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	9.519E−16	6.283E−20	9.519E−16
6: N-BUTANE	kgmol/hr	0	0	0
5: I-BUTANE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
66: PROPYNE	kgmol/hr	1.798E−16	0	1.798E−16
3114: 2-BUTYNE	kgmol/hr	1.761E−09	5.718E−15	1.761E−09
Total	kgmol/hr	74.6539	38.2987	74.6539
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	5.90458E−15	3.73642E−20	5.90458E−15
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	1.028399052	99.98668362	1.028399052
48: CARBON MONOXIDE	molar %	22.70410521	0.000344659	22.70410521
1: HYDROGEN	molar %	60.95609205	0.000775483	60.95609205
2: METHANE	molar %	0.002751363	6.00804E−08	0.002751363
49: CARBON DIOXIDE	molar %	15.30864429	0.012201459	15.30864429
65: ACETYLENE	molar %	1.57527E−10	9.97162E−16	0
40: BENZENE	molar %	0	0	0
3: ETHANE	molar %	1.93292E−10	5.38922E−15	1.93292E−10
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	1.78691E−09	1.36245E−13	1.78691E−09
1088: PHENOL	molar %	0	0	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	1.27508E−15	1.64053E−19	1.27508E−15
6: N-BUTANE	molar %	0	0	0
5: I-BUTANE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
66: PROPYNE	molar %	2.40845E−16	0	2.40845E−16
3114: 2-BUTYNE	molar %	2.35889E−09	1.493E−14	2.35889E−09
Total	molar %	100	100	100
Stream Number		19	20	21
Stream Name		Strm 19	Strm 20	Strm 21
Thermo Method Option		GLOBAL	GLOBAL	CHANGED
Vapor Fraction		1	1	1
Temperature	C.	635.45059	260	260
Pressure	kg/cm2	21.09209	21.08505	21.09209
Enthalpy	kcal/hr	366570.079	144383.986	57054.8364
Entropy	kcal/K/hr	380.4712	65.87408	−92.54735
Vapor Density	kg/m3	3.95258	6.72517	9.07162
Liquid 1 Density	kg/m3
Liquid 1 Specific Gravity	60 F@STP
Vapor Cp	kcal/kgmo/C.	8.17398	7.68643	10.81732
Vapor Cv	kcal/kgmo/C.	6.18082	5.67534	7.68247
Liquid 1 Cp	kcal/kgmo/C.
Vapor Viscosity	cP	0.0314229	0.0197539	0.0183392
Liquid 1 Viscosity	cP
Vapor Thermal Conductivity	kcal/m/hr/C.	0.1824967	0.1109855	0.0380113
Liquid 1 Thermal Conductivit	kcal/m/hr/C.
Vapor Flowrate	m3v(NTP)/hr	1673.04691	1673.04691	702.22658
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr
Molecular Weight		14.5114	14.5114	18.0153
Molar Flowrate	kgmol/hr	74.6539	74.6539	31.3344
Mass Flowrate	kg/hr	1083.332604	1083.332604	564.4986163
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	4.408E−15	4.408E−15	0
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	0.76774	0.76774	31.3344
48: CARBON MONOXIDE	kgmol/hr	16.9495	16.9495	0
1: HYDROGEN	kgmol/hr	45.5061	45.5061	0
2: METHANE	kgmol/hr	0.002054	0.002054	0
49: CARBON DIOXIDE	kgmol/hr	11.4285	11.4285	0
65: ACETYLENE	kgmol/hr	0	0	0
40: BENZENE	kgmol/hr	0	0	0
3: ETHANE	kgmol/hr	1.443E−10	1.443E−10	0
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	1.334E−09	1.334E−09	0
1088: PHENOL	kgmol/hr	0	0	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	9.519E−16	9.519E−16	0
6: N-BUTANE	kgmol/hr	0	0	0
5: I-BUTANE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
66: PROPYNE	kgmol/hr	1.798E−16	1.798E−16	0
3114: 2-BUTYNE	kgmol/hr	1.761E−09	1.761E−09	0
Total	kgmol/hr	74.6539	74.6539	31.3344
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	5.90458E−15	5.90458E−15	0
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	1.028399052	1.028399052	100
48: CARBON MONOXIDE	molar %	22.70410521	22.70410521	0
1: HYDROGEN	molar %	60.95609205	60.95609205	0
2: METHANE	molar %	0.002751363	0.002751363	0
49: CARBON DIOXIDE	molar %	15.30864429	15.30864429	0
65: ACETYLENE	molar %	0	0	0
40: BENZENE	molar %	0	0	0
3: ETHANE	molar %	1.93292E−10	1.93292E−10	0
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	1.78691E−09	1.78691E−09	0
1088: PHENOL	molar %	0	0	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	1.27508E−15	1.27508E−15	0
6: N-BUTANE	molar %	0	0	0
5: I-BUTANE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
66: PROPYNE	molar %	2.40845E−16	2.40845E−16	0
3114: 2-BUTYNE	molar %	2.35889E−09	2.35889E−09	0
Total	molar %	100	100	100
Stream Number		22	23	24
Stream Name		Strm 22	Strm 23	Strm 24
Thermo Method Option		GLOBAL	GLOBAL	GLOBAL
Vapor Fraction		1	1	0.8030047
Temperature	C.	256.87599	375.08737	4.4
Pressure	kg/cm2	21.08505	18.62596	18.47098
Enthalpy	kcal/hr	201438.822	312069.389	−220645.816
Entropy	kcal/K/hr	155.5943	348.3435	−990.4445
Vapor Density	kg/m3	7.32523	5.26004	11.74154
Liquid 1 Density	kg/m3			1040.04221
Liquid 1 Specific Gravity	60 F@STP			0.9973416
Vapor Cp	kcal/kgmo/C.	8.16233	8.50312	7.5658
Vapor Cv	kcal/kgmo/C.	6.08656	6.48094	5.45328
Liquid 1 Cp	kcal/kgmo/C.
Vapor Viscosity	cP	0.018348	0.0209351	0.0117894
Liquid 1 Viscosity	cP			1.54603
Vapor Thermal Conductivity	kcal/m/hr/C.	0.085113	0.1137605	0.0701938
Liquid 1 Thermal Conductivity	kcal/m/hr/C.			0.4903894
Vapor Flowrate	m3v(NTP)/hr	2375.27349	2375.27349	1907.35568
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr			100.38398
Molecular Weight		15.5473	15.5473	15.5473
Molar Flowrate	kgmol/hr	105.9883	105.9883	105.9883
Mass Flowrate	kg/hr	1647.831897	1647.831897	1647.831897
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	4.408E−15	4.408E−15	4.408E−15
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	32.1021	20.821	20.8209
48: CARBON MONOXIDE	kgmol/hr	16.9495	5.66831	5.66831
1: HYDROGEN	kgmol/hr	45.5061	56.7872	56.7872
2: METHANE	kgmol/hr	0.002054	0.002054	0.002054
49: CARBON DIOXIDE	kgmol/hr	11.4285	22.7097	22.7097
65: ACETYLENE	kgmol/hr	0	0	0
40: BENZENE	kgmol/hr	0	0	0
3: ETHANE	kgmol/hr	1.443E−10	1.443E−10	1.443E−10
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	1.334E−09	1.334E−09	1.334E−09
1088: PHENOL	kgmol/hr	0	0	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	9.519E−16	9.519E−16	9.519E−16
6: N-BUTANE	kgmol/hr	0	0	0
5: I-BUTANE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
66: PROPYNE	kgmol/hr	1.798E−16	1.798E−16	1.798E−16
3114: 2-BUTYNE	kgmol/hr	1.761E−09	1.761E−09	1.761E−09
Total	kgmol/hr	105.988	105.988	105.988
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	4.15896E−15	4.15896E−15	4.15896E−15
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	30.28842888	19.64467676	19.64458241
48: CARBON MONOXIDE	molar %	15.99190474	5.348067706	5.348067706
1: HYDROGEN	molar %	42.9351436	53.57889572	53.57889572
2: METHANE	molar %	0.001937955	0.001937955	0.001937955
49: CARBON DIOXIDE	molar %	10.78282447	21.42667094	21.42667094
65: ACETYLENE	molar %	0	0	0
40: BENZENE	molar %	0	0	0
3: ETHANE	molar %	1.36147E−10	1.36147E−10	1.36147E−10
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	1.25863E−09	1.25863E−09	1.25863E−09
1088: PHENOL	molar %	0	0	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	8.98121E−16	8.98121E−16	8.98121E−16
6: N-BUTANE	molar %	0	0	0
5: I-BUTANE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
66: PROPYNE	molar %	1.69642E−16	1.69642E−16	1.69642E−16
3114: 2-BUTYNE	molar %	1.66151E−09	1.66151E−09	1.66151E−09
Total	molar %	100	100	100
Stream Number		25	26	27
Stream Name		Strm 25	Strm 26	Strm 27
Thermo Method Option		CHANGED	GLOBAL	GLOBAL
Vapor Fraction		0	1	1
Temperature	C.	4.39847	4.39847	4.39847
Pressure	kg/cm2	18.46043	18.46043	18.46043
Enthalpy	kcal/hr	−221779.766	1134.09787	1651.37154
Entropy	kcal/K/hr	−643.5034	−346.8443	−255.336
Vapor Density	kg/m3		11.7349	1.56295
Liquid 1 Density	kg/m3	1040.04201
Liquid 1 Specific Gravity	60 F@STP
Vapor Cp	kcal/kgmo/C.		7.56569	6.92733
Vapor Cv	kcal/kgmo/C.		5.45325	4.9238
Liquid 1 Cp	kcal/kgmo/C.	18.04647
Vapor Viscosity	cP		0.0117892	0.0086131
Liquid 1 Viscosity	cP	1.54611
Vapor Thermal Conductivity	kcal/m/hr/C.		0.0701924	0.1437823
Liquid 1 Thermal Conductivit	kcal/m/hr/C.	0.4903864
Vapor Flowrate	m3v(NTP)/hr		1907.35804	1018.04118
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr	100.383
Molecular Weight		18.1334	14.9129	2.0159
Molar Flowrate	kgmol/hr	20.8791	85.1092	45.4265
Mass Flowrate	kg/hr	378.6090719	1269.224989	91.57528135
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	1.596E−19	4.408E−15	0
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	20.7773	0.043565	0
48: CARBON MONOXIDE	kgmol/hr	0.00048	5.66783	0
1: HYDROGEN	kgmol/hr	0.004106	56.7832	45.4265
2: METHANE	kgmol/hr	2.447E−07	0.002054	0
49: CARBON DIOXIDE	kgmol/hr	0.09716	22.6126	0
65: ACETYLENE	kgmol/hr	0	0	0
40: BENZENE	kgmol/hr	0	0	0
3: ETHANE	kgmol/hr	2.097E−14	1.442E−10	0
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	5.284E−13	1.333E−09	0
1088: PHENOL	kgmol/hr	0	0	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	4.697E−19	9.515E−16	0
6: N-BUTANE	kgmol/hr	0	0	0
5: I-BUTANE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
66: PROPYNE	kgmol/hr	0	1.797E−16	0
3114: 2-BUTYNE	kgmol/hr	6.377E−14	1.761E−09	0
Total	kgmol/hr	20.8791	85.1092	45.4265
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	7.64401E−19	5.17923E−15	0
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	99.51243109	0.051187181	0
48: CARBON MONOXIDE	molar %	0.00229895	6.659479821	0
1: HYDROGEN	molar %	0.019665599	66.71805163	100
2: METHANE	molar %	1.17199E−06	0.00241337	0
49: CARBON DIOXIDE	molar %	0.465345729	26.56892557	0
65: ACETYLENE	molar %	0	0	0
40: BENZENE	molar %	0	0	0
3: ETHANE	molar %	1.00435E−13	1.69429E−10	0
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	2.53076E−12	1.56622E−09	0
1088: PHENOL	molar %	0	0	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	2.24962E−18	1.11798E−15	0
6: N-BUTANE	molar %	0	0	0
5: I-BUTANE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
66: PROPYNE	molar %	0	2.11141E−16	0
3114: 2-BUTYNE	molar %	3.05425E−13	2.06911E−09	0
Total	molar %	100	100	100
Stream Number		28	29	30
Stream Name		Strm 28	Strm 29	Strm 30
Thermo Method Option		GLOBAL	GLOBAL	GLOBAL
Vapor Fraction		0.9994618	1	0.9979077
Temperature	C.	4.39847	4.39847	4.39847
Pressure	kg/cm2	18.46043	18.46043	18.46043
Enthalpy	kcal/hr	−2251.94686	−4036.65963	114.87892
Entropy	kcal/K/hr	−156.1731	−138.7223	−75.53467
Vapor Density	kg/m3	24.30074	39.15895	8.31097
Liquid 1 Density	kg/m3	1043.39783		1036.9372
Liquid 1 Specific Gravity	60 F@STP	0.9949659		0.9997428
Vapor Cp	kcal/kgmo/C.	8.5313	10.31671	6.99413
Vapor Cv	kcal/kgmo/C.	6.12765	7.1849	4.95039
Liquid 1 Cp	kcal/kgmo/C.
Vapor Viscosity	cP	0.0150956	0.0144267	0.0112137
Liquid 1 Viscosity	cP	1.54611		1.54611
Vapor Thermal Conductivity	kcal/m/hr/C.	0.0353254	0.0165414	0.0772689
Liquid 1 Thermal Conductivit	kcal/m/hr/C.	0.4903864		0.4903864
Vapor Flowrate	m3v(NTP)/hr	888.83821	506.76397	381.75248
Liquid 1 Flowrate	m3l(NTP)/hr
Liquid 2 Flowrate	m3l(NTP)/hr	0.1036698		0.1701677
Molecular Weight		29.6766	44.0099	10.6895
Molar Flowrate	kgmol/hr	39.6827	22.6126	17.0701
Mass Flowrate	kg/hr	1177.647615	995.1782647	182.470834
Molar Flowrate By Component
200: D-Glucose	kgmol/hr	0	0	0
201: Cellubiose	kgmol/hr	4.408E−15	0	4.408E−15
1245: SODIUM CHLORIDE	kgmol/hr	0	0	0
62: WATER	kgmol/hr	0.043565	0	0.043565
48: CARBON MONOXIDE	kgmol/hr	5.66783	0	5.66783
1: HYDROGEN	kgmol/hr	11.3566	0	11.3566
2: METHANE	kgmol/hr	0.002054	0	0.002054
49: CARBON DIOXIDE	kgmol/hr	22.6126	22.6126	0
65: ACETYLENE	kgmol/hr	0	0	0
40: BENZENE	kgmol/hr	0	0	0
3: ETHANE	kgmol/hr	1.442E−10	0	1.442E−10
4: PROPANE	kgmol/hr	0	0	0
22: ETHYLENE	kgmol/hr	1.333E−09	0	1.333E−09
1088: PHENOL	kgmol/hr	0	0	0
45: ETHYLBENZENE	kgmol/hr	0	0	0
23: PROPYLENE	kgmol/hr	9.515E−16	0	9.515E−16
6: N-BUTANE	kgmol/hr	0	0	0
5: I-BUTANE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
27: I-BUTENE	kgmol/hr	0	0	0
66: PROPYNE	kgmol/hr	1.797E−16	0	1.797E−16
3114: 2-BUTYNE	kgmol/hr	1.761E−09	0	1.761E−09
Total	kgmol/hr	39.6827	22.6126	17.0701
Molar Composition By Component
200: D-Glucose	molar %	0	0	0
201: Cellubiose	molar %	1.11081E−14	0	2.58229E−14
1245: SODIUM CHLORIDE	molar %	0	0	0
62: WATER	molar %	0.109783356	0	0.25521233
48: CARBON MONOXIDE	molar %	14.2828739	0	33.20326184
1: HYDROGEN	molar %	28.61851638	0	66.52919432
2: METHANE	molar %	0.005176059	0	0.012032736
49: CARBON DIOXIDE	molar %	56.98352179	100	0
65: ACETYLENE	molar %	0	0	0
40: BENZENE	molar %	0	0	0
3: ETHANE	molar %	3.63383E−10	0	8.44752E−10
4: PROPANE	molar %	0	0	0
22: ETHYLENE	molar %	3.35915E−09	0	7.80898E−09
1088: PHENOL	molar %	0	0	0
45: ETHYLBENZENE	molar %	0	0	0
23: PROPYLENE	molar %	2.39777E−15	0	5.57407E−15
6: N-BUTANE	molar %	0	0	0
5: I-BUTANE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
27: I-BUTENE	molar %	0	0	0
66: PROPYNE	molar %	4.52842E−16	0	1.05272E−15
3114: 2-BUTYNE	molar %	4.4377E−09	0	1.03163E−08
Total	molar %	100	100	100
Note:
All Liquid 1 Phase calculations exclude Free Water
indicates data missing or illegible when filed

The purpose of this optimization was to maximize the hydrogen production, minimize the need for electric grid power to operate the plant, and produce dry ice (liquid carbonic) product. The feedstock in this example is the dimer of cellulose, called cellubiose. This dimer portion of the large cellulose chain is replicated some 25,000 to 250,000 times.

The biomass enters the rotary kiln steam reformer as a solid and/or liquid phase together with the recycle gases. Within the kiln this mixture is heated, volatiles are vaporized, solids are chemically broken and decomposed, and the mixture is further heated as it moves from left to right through the kiln. At the end of the kiln, solids are removed. These solids are about 15% (by mass) of the biomass feed. With an agricultural or forest biomass feedstock, this solid product stream is a valuable freely-flowing, gravel-like, slow-release form of phosphorus/potassium fertilizer. The gases generated inside the kiln react with the water that enters with the biomass and with any additional water that comes with the recycle stream. The steam/carbon dioxide reforming chemical reaction is endothermic (it requires supplying energy) and occurs as the key step in the process generating a syngas stream consisting of hydrogen, carbon monoxide, carbon dioxide, water and other light gases, such as methane, ethane, ethylene, etc.

The hot syngas leaving the rotary kiln is heated, mixed with hot superheated steam, and enters the vertical steam reformer where it is further heated to complete the steam/carbon dioxide reforming reaction producing the highest concentration of hydrogen with the least amount of other organic contaminants, such as higher hydrocarbons and aromatics.

Intellergy's system addresses biomass phase-change as a solid-to-vapor chemical decomposition. The biomass is decomposed into a vapor by breaking the chemical bonds. This process is not the classical solid-to-liquid transition (heat of melting), or the liquid-to-vapor transition (heat of vaporization).

As these molecular fragments move through the kiln, the temperature increases, causing further decomposition by the hydroxyl radical attacking and breaking the next stronger bond, such as carbon-carbon bonds. The last and toughest bonds to be attacked are the aromatic carbon-carbon bonds. This decomposition results in the aromatic ring coming apart which creates other organic gases such as ethane, ethylene and butyne. Small amounts of these gases can recombine to form other very stable aromatic compounds.

This very hot syngas leaving the steam reformer passes through heat exchangers to recover energy to supply heat to processing equipment or to generate steam for process use and/or power generation. The cool hydrogen-rich syngas is passed to the hydrogen purification section, shown in the on the right-hand portion of the graphic in FIG. 2, where the carbon monoxide is reacted with more superheated steam to form carbon dioxide and additional hydrogen as well as release of heat. This rich hydrogen gas mixture is purified in a commercial pressure swing adsorption unit yielding a high purity hydrogen stream ranging from 99.9% to 99.99% purity. The remaining carbon dioxide and other light gases pass overhead into the carbon dioxide recovery system. Here a clean carbon dioxide stream is produced that feeds a commercial carbon dioxide liquefaction plant where either liquid carbon dioxide (liquid carbonic) or dry ice is produced. The remaining light gases are recycled to the kiln.

Referring to FIG. 7 the simulation modules M-1, H-2, H-20, S-4, and R-3 model the commercial rotary kiln. M-1 mixes the feed biomass with the recycle gases adiabatically. The H-20 module preheats the recycle gas while the H-2 module adds enough heat to the material leaving M-1 to change its phase to a vapor and heat it to 400 to 500° C. Module S-4 removes the freely-flowing granular residue, 15% of the biomass on a dry basis, which is formed in the rotary kiln. This residue is high in carbon content. R-3 calculates the equilibrium vapor composition using Gibbs Free Energy minimization isothermally at 400 to 500° C. The heat added to the commercial kiln is supplied by recovered process heat and trimmed with electric heat to control the reaction temperature at 400° to 500° C.

Simulation modules M-5, H-6, and R-7 model the commercial steam reformer. M-5 mixes the product from the rotary kiln at 1 atmosphere with superheated steam added at 300 PSIA and 267° C. Module H-6 heats the steam reformer feed to around 875° C. The steam reformer, R-7, is modeled as an isothermal reactor. The heat added to the commercial steam reformer is supplied by recovered process heat and trimmed with electric heat to control the reaction temperature at around 875° C.

Module X-8 models a commercial heat exchanger cooling the steam reformer effluent while recovering energy to be returned to the process. Water is condensed and removed in module F-9 which models a commercial vapor liquid separator. The vapor leaving F-9 flows through module S-10, a commercial carbon bed adsorber, where small amounts of aromatic organic compounds are removed. The vapor leaving S-10 flows to C-11, a 3-stage compressor that increases the process pressure to 300 PSIA. Heat exchanger module X-14 removes the heat of compression cooling the vapor to 260° C. In practice, X-14 models the compressor first and second stage intercoolers and the 3 stage after-cooler.

M-12 mixes the vapor from C-11 with superheated steam and the combined flow enters the carbon monoxide shift converter, R-13. The shift converter is modeled as an adiabatic reactor. This reactor converts water and carbon monoxide to desired carbon dioxide and hydrogen products. Energy is recovered in heat exchanger, X-15. This energy is returned back to the process. The water that condenses in X-15 is removed in vapor-liquid separator F-16. The vapor from separator, F-16, flows to a pressure swing adsorption unit where 80% of the hydrogen leaving F-16 is recovered as product with 99.9% purity. The remaining vapor leaving the pressure swing adsorption unit flows to the carbon dioxide recovery system, module S-18. S-18 models the carbon dioxide recovery system as a simple separation device. In practice this equipment could be a membrane system or an amine system with a liquid carbonic and/or dry ice production unit. The vapor leaving S-18 flows to heater, H-20, preheating the vapor prior to feeding the rotary kiln.

A significant advantage of this process configuration with the major recycle loop carrying the unconverted hydrogen and other light gases from the PSA unit, is that these gases are further converted in the steam/CO₂ reforming units to make more hydrogen product, as required in the mass balance dictating that the hydrogen coming in with the feedstock must leave the process as the hydrogen product. Additional or higher conversion stages in the PSA unit are not needed when this recycle loop is used.

To validate the process simulation predictions, a biomass sample of grape pomace, available in huge quantity from the wine industry, was test-run in a pilot unit as illustrated in FIG. 2, less the hydrogen purification and liquid carbonic steps, to produce the syngas stream. This measured syngas stream was compared with WinSim's Design-2 process simulation prediction below in Table 1.

Comparison of Pomace Produced Syngas with Simulation Results

TABLE 1
Component	Test Results	Simulation Prediction
Hydrogen	59.4%	61.4%
Oxygen + Argon*	0%
Nitrogen*	0%
Carbon Monoxide	32.4%	31.3%
Carbon Dioxide	2.96%	6.2%
Methane	5.1%
Ethane, acetylene, ethylene	570 ppm	<940 ppm
Propane**	98 ppm
Butanes**	60 ppm
Benzene**	198.4 ppm	1 ppb
C7 and above**	380 ppm
Hydrogen Sulfide**	59.8 ppm
Carbonyl Sulfide**	1.74 ppm
Methyl Mercaptan**	16.6 ppm
Carbon Disulfide**	35.3 ppm
*Air leakage accounted for.
**In practice, these components will be removed by a zinc bed, carbon bed or are recycled to the kiln

The comparison of the test results and the simulation prediction of syngas is excellent. The kiln and steam/CO₂ reformer chemical reactors' process temperatures and steam content, in the simulation, match those of the pilot demonstration.

The energy balance was completed in order to identify where heat sources in the process can be used to provide the endothermic heat needed for the steam reforming chemistry discussed above. In the table below, it can be seen that the largest heat requirement is for the steam/CO₂ reforming kiln R-3 via heater H-2. The second stage steam/CO₂ reformer R-7 is supplied by induction heaters or by DC electrical resistance heat estimated at about 600 kW. For a 20 dry ton/day feedstock plant, this heat requirement is around 1200 kWt. This can be supplied by heat exchange-recovering heat in X-8 from the very hot syngas leaving the second stage steam/CO₂ reformer R-7, which is about 1200 kW. There is also heat available in X-15 from the exothermic CO shift unit that further enhances the hydrogen production where this heat can be used to drive a boiler to make the steam needed for the process. In this way, only a small amount of grid electricity around 560-760 kW is needed to drive the plant.

TABLE 5
Process Power Requirements Summary
	Cellobiose	Pomace
	Chemical Formula
	C12—H22—O11	C12—H16—O6
	KW	KW
Inputs
Rotary Kiln	1189.41	1268.32
Steam Reformer	601.36	628.71
Compressors	207.12	276.21
Boiler	392.84	531.78
Product Purification	18.64	18.64
Outputs
X-8	1292.01	1221.88
X-15	561.69	756.70
Total Power Load	555.67	745.07
Hydrogen Production, Kg/Hr	93.86	131.42
Carbon Dioxide Production, Kg/Hr	1020.22	1319.61
Power Demand, KW/Kg Hydrogen	5.92	5.67

The heat sources and heat demands are shown in Table 5 comparing cellulose (cellubiose dimer) and grape pomace winery waste. And they are very comparable.

Claims

1. A system consisting of an improved rotary kiln for carrying out steam/CO2 reforming, where the preferred features of waste volatilization, steam/CO2 reforming, gas heat exchange, filtration and solid separation are combined into a single duplex kiln that uses in the primary region a heated hollow flight screw to begin the endothermic steam/CO2 reforming of the biomass or waste feedstock, where the off-gases are carried into a second region where inductively-heated annular surfaces radiatively heat the gases to 800-1050° C. (1470-1920° F.) and particulate is removed so that these hot gases can pass now counter-currently through the central shaft and then through the hollow flight screw internal cavities to supply the reforming heat needed to do the endothermic chemistry and cool the syngas for kiln exit.

2. A system in 1 that includes spiral vanes to carryout a cyclonic separation of entrained solids so that the syngas produced has high quality so to avoid detrimental effects of fuel cell poisoning arising from undesirable constituents in the waste.

3. A system in 1 that includes an internal high-temperature porous ceramic or metal filter cartridge to further remove entrained solids so that the syngas produced has high quality so to avoid detrimental effects on downstream process units of catalyst poisoning arising from undesirable constituents in the waste.

4. A process that provides the interface between a steam/CO2 reforming waste conversion system generating syngas and a Fischer-Tropsch Unit that uses said syngas that makes paraffin wax product for carbon sequestration while recycling the light hydrocarbons off of the Fischer-Tropsch Unit, consisting of hydrogen, CO, CO2, methane, ethane, propane, etc. to avoid their emissions as powerful greenhouse gases and also recycling the lighter hydrocarbons to help maintain a higher H2/CO ratio of the syngas. The Fischer-Tropsch unit, which is exothermic, produces a large steam flow for turbine-generation of electricity and, thus, replaces the need for a fuel cell. This process method destroys the waste stream while at the same time the syngas is made to release energy without having to burn the waste or the syngas.

5. A system of 1 where the kiln residue can be converted into carbon-containing fertilizer, and a carbon-sequestering, high-carbon content product of important commercial value.

6. System of 4 where a Fischer-Tropsch synthesis reactor system is used to produce a high carbon content compound that can be sold into markets where it is never burned in its life cycle and therefore serves as a carbon sequestering agent and where the Fischer-Tropsch overhead stream containing hydrogen, CO, CO2, methane, ethane and light paraffins are recycled back to the steam/CO2 reformer in order to make use of their high hydrogen content to achieve the more desirable H2/C0 ratio around 1.0.

7. A system of 4 where a Fischer-Tropsch unit combined with a parallel shift converter/pressure-swing absorption unit to accomplish the conversion of the syngas to commercially-marketable hydrogen fuel, ample steam to generate electrical power for the plant and for export, and a high-carbon content organic product paraffin that sequesters substantially the carbon in the waste stream—all without any burning of the waste or the syngas.

8. A system of 7 where the light gases from the Fischer-Tropsch unit are recycled back to the steam reformer for destruction and avoiding release to the environment.

9. A system of 7 where carbon dioxide and a portion of the hydrogen from the Shift and Pressure Swing Absorber units are recycled back to the steam reformer to adjust the H2/CO ratio for optimum utilization in the Fischer-Tropsch unit.

10. A system of 7 where small impurities in the syngas that could damage the sensitive catalysts in a high temperature fuel cell do not damage the more robust catalysts (i.e. iron or cobalt-based) in a Fischer-Tropsch unit.

11. A system of 4 where the best clean-up of syngas impurities involves a process where there are both a high temperature filtration step and a sulfur-, chlorine-, and nitrogen-containing compound removal step as well as a chilling and condensation step downstream which includes a HEPA filter and a guard bed to protect high temperature fuel cell electrochemical catalysts.

12. A system of 4 where the best clean-up of syngas impurities involves a process where there are both a high temperature filtration step and a sulfur-, chlorine-, and nitrogen-containing compound removal step as well as a chilling and condensation step downstream which includes a HEPA filter and a guard bed to protect Fischer-Tropsch catalysts.

13. A system of 4 where a Fischer-Tropsch unit that is greatly simplified because its many tail or overhead streams can be used as recycle to the steam/CO2 reforming process.

14. A system of 6 where a heat recovering exothermic reactor that contains a supported catalyst immersed in water to maintain the catalyst at a constant temperature by the boiling of the water to make steam that is used to generate power.

15. A system of 4 where a power recovery system that involve the combined use of a shift and PSA unit as well as the Fischer-Tropsch unit to make best use of recycle streams and waste heat.

16. A system of 14 where an exothermic reactor consists of a Fischer-Tropsch reactor.

17. A system of 14 where an exothermic reactor consists of a methanol synthesis reactor.

18. A system of 14 where an exothermic reactor consists of a methanation reactor.

19. A system of 1 where heat to the kiln sections doing endothermic steam/CO2 reforming is supplied by recycling the syngas through the holoflite screw to heat the waste and do reforming.

20. A system of 4 where hot syngas from a conventional kiln followed by the steam/CO2 reformer is heat exchanged with another inert gas, such as carbon dioxide or air, to heat the kiln by indirect heating in the oven surrounding rotary kiln tube by means of a series of injection jets, where gas burners are normally located.

21. A system of 1 where a recycle loop carrying the unconverted hydrogen and other light gases from the PSA unit back to the feed-end kiln, wherein these gases are further converted in the steam/CO2 reforming units to make more hydrogen product, as required in the mass balance dictating that the hydrogen coming in with the feedstock must leave the process as the hydrogen product; so that in this way, additional or higher conversion stages in the PSA unit are not needed when this recycle loop is used.