Biocementation Methods and Systems

Abstract

The invention is directed to kits, compositions, tools and methods comprising a cyclic industrial process to form biocement. In particular, the invention is directed to materials and methods for decomposing calcium carbonate into calcium oxide and carbon dioxide at an elevated temperature, reacting calcium oxide with ammonium chloride to form calcium chloride, water, and ammonia gas; and reacting ammonia gas and carbon dioxide at high pressure to form urea and water, which are then utilized to form biocement. This cyclic process can be achieved by combining industrial processes with the resulting product as biocement. The process may involve retention of calcium carbonate currently utilized in the manufacture of Portland Cement.

Description

REFERENCE TO RELATED APPLICATIONS

This application is a continuation-in-part of U.S. application Ser. No. 16/153,362 filed Oct. 5, 2018, which issued as U.S. Pat. No. 11,008,591 on May 18, 20921, which claims priority to U.S. Provisional Application No. 62/568,533 filed Oct. 5, 2017, and U.S. Provisional Application No. 62/735,062 filed Sep. 22, 2018, the entirety of each of which is specifically and entirely incorporated by reference.

BACKGROUND

1. Field of the Invention

The invention is directed to kits, compositions, tools and methods comprising a cyclic industrial process for forming biocement. In particular, the invention is directed to materials and methods for decomposing calcium carbonate into calcium oxide and carbon dioxide at an elevated temperature, reacting calcium oxide with ammonium chloride to form calcium chloride, water, and ammonia gas; and reacting ammonia gas and carbon dioxide at high pressure to form urea and water, which are then utilized to form biocement.

2. Description of the Background

Global industrial production of ammonia in 2014 was 176 million tons, a 16% increase over the 2006 production of 152 million tons. Industrial ammonia production is responsible for 1.44% of global CO2 emissions. Ammonia production consumes 5% of global natural gas production, and consumes about 2% of global energy production.

The biocementation reaction (see FIG. 1) relies on the metabolic hydrolysis of urea, producing ammonium and carbonate ions in a solution containing calcium chloride.

2(NH₂)CO+CaCl₂+2H₂O2NH₄Cl+CaCO₃

Calcium cations react with the carbonate anions at the surface of the bacterial membrane, forming calcium carbonate of the polymorph calcite. Ammonium cations and chloride anions remain in balance in the process water.

Calcium chloride is produced by reacting calcium oxide with ammonium chloride to produce calcium chloride, water, and ammonia gas.

CaCO₂₊NH₄Cl→CaCl+H₂O+NH₄

The Solvay process or ammonia-soda process is an industrial process for the production of sodium carbonate, also referred to as soda ash, and calcium chloride. The chemical process can be written as:

2NaCl+CaCO₃→Na₂CO₃+CaCl₂

Ingredients for this process are readily available and include salt and limestone. Solvay-based chemical plants now produce roughly three-quarters of the world-wide supply, with the remainder provided from natural deposits.

Urea production, also called the Bosch-Meiser urea process after its discoverers, involves two main equilibrium reactions with incomplete conversion of the reactants. The first is carbamate formation: the fast exothermic reaction of liquid ammonia with gaseous carbon dioxide (CO₂) at high temperature and pressure to form ammonium carbamate:

2NH₃+CO₂H₂N—COONH₄

The second is urea conversion: the slower endothermic decomposition of ammonium carbamate into urea and water:

H₂N—COONH₄(NH₂)₂CO+H₂O

The overall conversion of NH₃ and CO₂ to urea is exothermic, the reaction heat from the first reaction driving the second. Like all chemical equilibria, these reactions behave according to Le Chatelier's principle, and the conditions that most favor carbamate formation have an unfavorable effect on the urea conversion equilibrium. Therefore, conventional process conditions involve a compromise: the ill-effect on the first reaction of the high temperature (around 190 C) needed for the second is compensated for by conducting the process under high pressure (140-175 bar), which favors the first reaction.

Although typically necessary to compress gaseous carbon dioxide to this pressure, the ammonia is available from the ammonia plant in liquid form, which can be economically pumped into the system. As urea conversion is incomplete, the product is separated from unchanged ammonium carbamate.

In urea production plants this was done by letting down the system pressure to atmospheric to let the carbamate decompose back to ammonia and carbon dioxide. Originally, because it was not economic to recompress the ammonia and carbon dioxide for recycle, the ammonia at least would be used for the manufacture of other products, for example ammonium nitrate or sulfate which vented the carbon dioxide as waste. Later process schemes made recycling unused ammonia and carbon dioxide practical. This was accomplished by depressurizing the reaction solution in stages (first to 18-25 bar and then to 2-5 bar) and passing it at each stage through a steam-heated carbamate decomposer, recombining the resultant carbon dioxide and ammonia in a falling-film carbamate condenser and pumping the carbamate solution into the previous stage.

SUMMARY OF THE INVENTION

The present invention overcomes problems and disadvantages associated with current strategies and designs, and provides new tools, compositions, and methods for the manufacture of ammonia, ammonium chloride, calcium chloride, urea, and/or calcium carbonate.

One embodiment of the invention is directed to methods of forming biocement comprising: decomposing calcium carbonate, preferably at an elevated temperature or with acid, to form calcium oxide and carbon dioxide; reacting calcium oxide with ammonium chloride to form calcium chloride and ammonia, reacting ammonia and carbon dioxide in a process to form urea and water; and reacting urea and calcium chloride in a process to form biocement. Preferably decomposing comprises treating calcium carbonate with elevated temperatures or an acid wherein the preferred elevated temperature is about 850° C. or more and the preferred acid comprises hydrochloric acid. Preferably the process comprises elevated pressure, corona discharge, or co-culture with urea-producing organisms. Preferably, calcium ions and dissolved carbon dioxide are obtained from seawater. Preferably, reacting urea with calcium chloride further forms ammonium chloride.

Another embodiment of the invention is directed to methods of forming biocement comprising: decomposing calcium carbonate, preferably at an elevated temperature or with acid, to form calcium oxide and carbon dioxide; reacting calcium dioxide with ammonium in a process to form urea and water; and reacting urea and calcium chloride to form biocement. Preferably decomposing comprises treating calcium carbonate with elevated temperatures or an acid wherein the preferred elevated temperature is about 850° C. or more and the preferred acid comprises hydrochloric acid. Preferably the process comprises elevated pressure, corona discharge, or co-culture with urea-producing organisms. Preferably reacting urea with calcium chloride further forms ammonium chloride. Preferably, ammonium chloride is further decomposing to form acid and ammonia.

Other embodiments and advantages of the invention are set forth in part in the description, which follows, and in part, may be obvious from this description, or may be learned from the practice of the invention.

DESCRIPTION OF THE FIGURES

FIG. 1 The urea-hydrolysis biocementation reaction.

FIG. 2 The urea-hydrolysis biocementation reaction as a closed loop industrial cyclic process.

FIG. 3 The urea-hydrolysis biocementation reaction as an industrial cyclic process where limestone calcium carbonate is converted into biocement.

FIG. 4 The urea-hydrolysis biocementation reaction represented at large-scale industrial production volumes.

FIG. 5 The urea-hydrolysis biocementation reaction.

FIG. 6 The urea-hydrolysis biocementation reaction where process water is recycled through the regeneration of calcium chloride, and the electrolysis of ammonia into hydrogen and nitrogen gases.

DESCRIPTION OF THE INVENTION

Biocementation involves the metabolic hydrolysis of urea, producing ammonium and carbonate ions in a solution containing calcium chloride. Calcium cations react with the carbonate anions at the surface of the bacterial membrane, forming calcium carbonate of the polymorph calcite. Ammonium cations and chloride anions remain in balance in the process water.

The invention is directed to the surprising discovery that this reaction can become cyclical. In one alternative, calcium carbonate is decomposed into calcium oxide and carbon dioxide at an elevated temperature. Calcium oxide reacts with ammonium chloride to form calcium chloride, water, and ammonia gas. The ammonia gas and carbon dioxide are reacted to synthesize urea and water which are then utilized in the biocementation process. In another alternative, calcium carbonate is decomposed, preferably at an elevated temperature or with acid, to form calcium oxide and carbon dioxide; reacting calcium dioxide with ammonium in a process to form urea and water; and reacting urea and calcium chloride to form biocement. Accordingly, depending on the precursor ingredients, the result can be the production of calcium carbonate, ammonia, ammonium chloride, calcium chloride, urea, and/or ammonia. Preferably reacting urea with calcium chloride further forms ammonium chloride. Preferably, ammonium chloride is further decomposing to form acid and ammonia.

The cyclic process can be achieved using existing industrial processes combined with biocementation technologies (see e.g., FIG. 2). As the resulting product can be for the formation of biocement as a building material, an equivalent input stream of calcium carbonate provides fuel to the process cycle (see FIG. 3). At a large industrial scale, an input source of calcium carbonate is mined limestone deposits, as are currently used in the manufacture of Portland Cement. Preferably decomposing comprises treating calcium carbonate with elevated temperatures or an acid wherein the preferred elevated temperature is about 600° C. or more, 700° C. or more, 800° C. or more, 850° C. or more, 900° C. or more, 1,000° C. or more, or even higher temperatures. The preferred acid comprises hydrochloric acid although a variety of acids may be utilized including, but not limited to mineral acids, organic acids, phosphoric acid, nitric acid, acetic acid and combinations thereof. Preferably the process comprises elevated pressure such as, for example, greater than 100 psig, greater than 200 psig, greater than 300 psig, greater than 400 psig, greater than 500 psig, or greater. Corona discharge may also be utilized or co-culture with urea-producing organisms. A corona discharge is an electrical discharge brought on by the ionization of a fluid such as air surrounding a conductor that is electrically charged. A corona will occur when the strength (potential gradient) of the electric field around a conductor is high enough to form a conductive region, but not high enough to cause electrical breakdown or arcing to nearby objects. It is often seen as a bluish (or other color) glow in the air adjacent to pointed metal conductors carrying high voltages, and emits light by the same property as a gas discharge lamp. This step can be performed in isolation for the production of bulk urea, or can be employed within the aggregate matrix for localized urea production, consumed at the time of biocementation.

Another embodiment is to co-culture with urea-producing organisms such as, for example, by the autotrophic metabolism of atmospheric nitrogen and carbon dioxide into urea or by the bacterial decomposition of organic matter. Urea-producing microrganisms include, for example, various species of Pseudomonas, Delaya avenusta, Thiosphaera pantotropha, Pseudomonas stutzeri, Fragilaria crotonensis, Pseudoalteromonas sp., Pseudoalteromonas haloplanktis, Halomonas venusta, Pseudomonas balearica, Pseudomonas stutzeri, Bacillus megaterium. Escherichia coli, Exiguobacterium aurantiacum, Pseudoalteromonas aliena, Pseudoalteromonas luteoviolacea, variants, serotypes, mutations, recombinant forms, or combinations thereof, and other organisms and microorganisms known to those of ordinary skill in the art.

Modern dry-process Portland Cement manufacturing utilizes a heat source of 1,850° C. to 2,000° C. for achieving a material sintering temperature of 1,450° C. within a rotary kiln. Early in the manufacturing process, calcium carbonate is decomposed into calcium oxide and carbon dioxide at a temperature of 850° C. in a preheater/calciner tower, where the required heat energy is provided through partial recovery of the rotary kiln exhaust. A calcium oxide digester, implemented as a side-chain process at a Portland Cement manufacturing plant, could be similarly fueled by the unused waste heat energy from the cement rotary kiln to process on-site calcium carbonate. The calcium oxide, reacted with ammonium chloride, produces calcium chloride, water, and ammonia gas. The ammonia gas then reacted with carbon dioxide released during the side-chain calcium oxide production produces urea and water as a carbon neutral materials recycling process. The inputs of this process are thereby ammonium chloride and calcium carbonate, with the output materials of calcium chloride and urea.

In this large scale model of the urea-hydrolysis biocementation reaction, industrial production volumes are indicated whereby limestone input material is converted into biocement products (see FIG. 4). The metabolic biocementation process is represented as a distributed model, where ammonium chloride, urea, and calcium chloride are used as stable, soluble materials for transport to and from an industrial materials recycling system whereby materials are centralized in a recycling plant that provides distributed biocement production facilities with urea and calcium chloride for the production of biocement construction materials using local aggregates. Ammonium chloride recovered from the distributed biocement production streams is returned to the centralized materials recycling plant. This closes the loop by reproducing and re-distributing fresh calcium chloride and urea. Calcium chloride and urea represent approximately 75% of the total direct material cost. This large scale model moves the supply chain of these important materials, where the direct costs are internally determined by operational costs of the centralized materials recycling plant, rather than market prices from a third party supplier.

Biocement production targets implementation of the full-recycle, large scale process models have been initially determined by current scales of industrial urea synthesis. Urea plants are most commonly coupled with ammonia production plants, where the carbon dioxide released during ammonia production is reacted with a fraction of the produced ammonia for the formation of urea. A small, modern urea plant produces approximately 350,000 tons of urea per year. Based on the biocement production input material ratio of 1 mol. urea (2NH₂CO):1 mol. calcium chloride (CaCl₂), a production of 350,000-tons urea requires a corresponding production of 326,791-tons calcium oxide (see Table 1). An efficient US Portland Cement manufacturing plant produces over 2,000,000-tons of cement per year, consuming more than 1,276,200-tons calcium oxide.

TABLE 1
Comparative mass of process materials in large-scale model.
Assumes an annual urea production of 350,000-tons.
Material	Molar Mass	Molar Ratio	Production Mass
Urea	60.06 g/mol	1	350,000 tons
Calcium Chloride	110.98 g/mol	1	646,737 tons
Calcium Carbonate	100.09 g/mol	1	583,257 tons
Calcium Oxide	56.08 g/mol	1	326,791 tons
Carbon Dioxide	44.01 g/mol	1	256,469 tons
Ammonium Chloride	53.49 g/mol	2	623,438 tons
Ammonia	17.03 g/mol	2	198,497 tons

Accordingly, the system can be designed for the large (or small scale) production of one or more of calcium carbonate, calcium oxide, calcium chloride, ammonium chloride, ammonia, and urea.

Another embodiment of the invention is directed to an industrial cyclic process. For example, the industrial cyclic process is preferably for the production of biocement material, where calcium ions and dissolved carbon dioxide/carbonates are provided by seawater, industrial waste streams, and/or naturally occurring brines. Co-culture organism group (1) produces urea from the carbon and a nitrogen substrate. Co-culture organism group (2) produces biocement using seawater calcium ions and organism group (1) produced urea. Organism group (2) produced ammonium is then used by organism group (1) as the nitrogen substrate for urea production.

The industrial process is also preferably for the production of urea and/or ammonia for use in agriculture, chemical, and manufacturing industries, where an organism or consortia of organisms produce urea from a nitrogen substrate and a carbon rich media. Produced urea can be separated and used in aqueous form, or dried into solids such as pellets, prills, or powders for downstream use. A subsequent step using a urease producing-bacteria can hydrolyze the urea into ammonium, which is separated as ammonia liquor or compressed ammonia gas for downstream use. Examples of urease-producing bacteria include, but are not limited to Sporosarcina spp. (e.g., S. pasteurii and S. ureae), Proteus spp. (e.g., P. vulgaris and P. mirabilis), Bacillus spp. (e.g., B. sphaericus and B. megaterium), Myxococcus spp (e.g., M. xanthus), Helicobacter spp. (e.g., H. pylori), or variants, serotypes, mutations, recombinant forms, or combinations thereof. Preferably the organism are vegetative cells, although spores can be utilized and converted to vegetative cells that produce urease, or the extracted urease enzyme may be used without the presence of the enzyme-producing organism. The nitrogen substrate for urea production comprises complex nitrogen sources, or gaseous atmospheric nitrogen depending on the specification of the consortia. Carbon can be supplied in any form and, for example, converted to a liquid as dissolved atmospheric carbon dioxide. The reaction may further comprise additional materials to be incorporated into the biocement such as, for example, organic or inorganic material, rock, glass, wood, paper, metal, plastic, polymers, fibers, minerals or combinations thereof

Engineered Living Marine Cement (ELMc)

Another embodiment of the invention is directed to tools, compositions, production methods, and structures for engineered living marine cement (ELMc). ELMc involves the development of a living biological concrete and/or concrete-like materials that is utilized for marine and other applications. ELMc materials have the capacity to self-heal (e.g., maintenance free), mitigating common structural degradations to traditional marine concretes that result in significant maintenance and/or replacement costs. A viable ELMc material preferably sources materials for biocement formation directly from the environment (e.g., seawater, mine environments).

Preferably, ELMc materials employ bacteria strains that are native to or adaptable to the environment in which the structure is produced. For example, in a marine environment, feedstock urea and calcium is sourced directly from seawater. While Calcium is plentiful in seawater as a mechanic of the oceanic carbon pump, urea is available in smaller amounts which may limit the rates of biocement formation. Oceanic urea as produced by zooplankton, marine life such as, for example, fish, and marine bacteria. For marine biocement structures, ELMc preferably involves a consortia of urea-producing and urease-producing bacteria. Over 300 strains of marine bacteria were screened for urea production and 24 were selected, which fell into seven distinct species. Strains were further developed by selection and/or genetic engineering resulting in a number of very high levels of ELMc production. Preferably, strains were developed for biocement formation in units during 7-day trials, using a synthetic seawater feedstock that includes no urea.

Preferred bacterial strains generate urea through two different metabolic pathways: (a) purine/pyrimidine metabolism and (b) cleavage of the amino acid L-arginine by the enzyme arginase. In the marine environment, these substrates remain a limiting factor, where synthetic approaches enable the use of more plentiful carbon sources. For example, metabolic pathways are genetically engineered for the industrial production of L-arginine from a glucose carbon source. Similar tools and processes enable the utilization of alternative carbon sources, including those produced directly from dissolved inorganic carbon.

A preferred ELMc production involves the local production of urea by bacterial generation at the nucleation site of cement formation. This approach eliminates the reliance on industrially produced urea and removes urea as a feedstock component. ELMc developed synthetic biology tools and methods involves two processes and application conditions for industrial biocement products.

Firstly, ELMc produces biocement as a maintenance activity relevant to a material service life of years, decades, and longer. In this methodology, maintenance involves a gradual deposition of material into structural damages and defects, but maintenance begins immediately. Preferably, maintenance is a continuous process. Secondly, ELMc involves sourcing necessary feedstock components directly from nitrogen-limited natural sources such as seawater, in native concentrations, along with any other impurities or variable factors. The ELMc produced materials are comprised of a consortia of bacteria that generates organic urea at the site of calcium carbonate formation. Feedstocks are limited by components and/or concentrations found in natural seawaters. Sustainable biocement development, according to the disclosures herein, provide both a carbon accounting and guide life-cycle analysis (LCA) to provide sustainable sources for feedstock carbon, while maintaining the performance and commercial viability of established products.

Another embodiment of the invention is directed to methods comprising: loading a solid object with urease-producing organisms and urea-producing organisms; placing the solid object into an environment containing one or more of carbon, nitrogen and calcium; and forming calcium carbonate within the solid object. Preferably loading with the urease-producing organisms and/or the urea-producing organisms comprises combining the solid object with dry organisms such that the organisms are retained within or on a surface of the solid object, or placing the solid object in a composition containing the urease-producing organisms and/or the urea-producing organisms. Preferably the solid object is loaded with spores and/or vegetative cells of the urease-producing organisms and/or the urea-producing organisms. Preferably the solid object comprises a natural or non-natural material, recycled or manufactured sand, ore, a brick, a block, masonry, a panel, tile, a board, rock, stone, crushed rock, crushed stone, minerals, crushed or fractured glass, wood, jute, ash, foam, basalt, fibers, mine tailings, paper, waste materials, waste from a manufacturing process, plastics, polymers, roughened materials, and/or combinations thereof, and also preferably, the solid object is permeable to microorganisms. Preferably, the solid object contains one or more of carbon, nitrogen and calcium, and more preferably the environment and the solid object contain sufficient quantities of carbon, nitrogen and calcium for forming calcium carbonate. Preferably, placing comprises immersing the solid object entirely within the environment. Preferably, the environment comprises an environment that promotes the proliferation of the urease-producing organisms and/or the urea-producing organisms a marine environment and more preferably is a marine environment. Preferably the urea-producing organisms comprise Pseudomonas, Delaya avenusta, Thiosphaera pantotropha, Pseudomonas stutzen, Fragilaria crotonensis, Pseudoalteromonas spp., Pseudoalteromonas haloplanktis, Halomonas venusta, Pseudomonas balearica, Pseudomonas stutzeri, Bacillus megaterium. Exiguobacterium aurantiacum, Pseudoalteromonas aliena, Pseudoalteromonas luteoviolacea, E. coli, and variants, serotypes, mutations, recombinant forms, and combinations thereof, and the urease-producing organisms comprise Sporosarcina spp., S. pasteurii, S. ureae, Proteus spp., P. vulgaris, P. mirabilis, Bacillus spp., B. sphaericus, B. megaterium, Myxococcus spp., M. xanthus, Helicobacter spp., H. pylori, and variants, serotypes, mutations, recombinant forms, and combinations thereof. Preferably the calcium carbonate is formed from a combination of urea produced by the urea-producing organisms that is acted upon by urease produced by the urease-producing organisms, and in the presence of carbon, nitrogen and calcium. Preferably the calcium carbonate is formed as a coating around the solid object (e.g, as a biofilm containing organisms and calcium carbonate), and/or is formed outside of the solid object. Preferably the solid object containing calcium carbonate is utilized for erosion control in the environment, as a solid support of a structure within the environment, wherein the structure comprises building material, an electronic device, and/or a container. Preferably calcium carbonate is formed within, around, and/or external to the solid object for a period of six months or more, for a period of one year or more, or for a period of 5 years or more, or the calcium carbonate is self-replicating or self-sustaining and perpetual for the life of the solid object. In addition, such solid objects are also self-repairing.

Another embodiment of the invention is directed to solid objects containing urease-producing organisms and urea-producing organisms, preferably containing calcium carbonate. Preferably the urease-producing organisms and the urea-producing organisms are viable, and preferably the urease-producing organisms produce urease and the urea-producing organisms produce urea. Preferably the urease and the urea in the presence of carbon, calcium and nitrogen form calcium carbonate. Preferably the solid object comprises a natural or non-natural material, recycled or manufactured sand, ore, a brick, a block, masonry, a panel, tile, a board, rock, stone, crushed rock, crushed stone, minerals, crushed or fractured glass, wood, jute, ash, foam, basalt, fibers, mine tailings, paper, waste materials, waste from a manufacturing process, plastics, polymers, roughened materials, and/or combinations thereof. Preferably the solid object further contains supplemental materials such as, for example, organic or inorganic material, rock, glass, wood, paper, metal, plastic, polymers, fibers, minerals or combinations thereof.

Another embodiment of the invention is directed to compositions comprising a viable mixture of urease-producing organisms and urea-producing organisms. Preferably the compositions contain the urease-producing organisms and the urea-producing organisms are in the form or spores and/or vegetative cells. Preferably the composition is aqueous or dry.

The following examples illustrate embodiments of the invention, but should not be viewed as limiting the scope of the invention.

Examples

Example 1 Platform Adaptability

Traditional Portland Cement manufacturing involves a 20th-Century centralized industrial model, where the production of cement is tied to capital and energy intensive processes (e.g., methane fired tunnel kiln). With changes in market demands, regulatory conditions, material resources, and global understanding of environmental impacts evolve, the adaptation of traditional cement plants, there is a need for a change of infrastructural for the next plant to be built. The production design disclosed and described herein, fills that need and also provided an adaptable platform.

The production of biocement according to the disclosures here, involves two interrelated systems: manufacturing equipment, and the biotechnology of biocement production. Manufacturing equipment includes equipment for materials handling (e.g., mixing, forming, and transit equipment), and solid-state fermentation (e.g., feedstocks and delivery), representing hard capital costs for manufacturing product. A large portion of materials and infrastructure production includes bacteria and feedstock materials for manufacturing and provided to production sites.

A plant of this disclosure provides for adapting the feedstock chemicals required for biocement production, without also requiring significant infrastructural or capital changes to the manufacturing systems, or the need for a costly carbon source such as methane. The processes of this disclosure increases sustainability, extend performance, work with local feedstock components, reduce production costs, and is rapidly deployable.

Other embodiments and uses of the invention will be apparent to those skilled in the art from consideration of the specification and practice of the invention disclosed herein. All references cited herein, including all publications, U.S. and foreign patents and patent applications, are specifically and entirely incorporated by reference. The term comprising, where ever used, is intended to include the terms consisting and consisting essentially of. Furthermore, the terms comprising, including, and containing are not intended to be limiting. It is intended that the specification and examples be considered exemplary only with the true scope and spirit of the invention indicated by the following claims.

Claims

1. A method of performing a cyclical reaction using calcium carbonate decomposition to form a biocement, the method comprising:

decomposing calcium carbonate forming calcium chloride and ammonia;

reacting the ammonia with carbon dioxide in a process to form urea; and

reacting urea with calcium chloride to form biocement.

2. The method of claim 1, wherein decomposing forms calcium oxide and carbon dioxide, and the calcium oxide is treated with ammonium chloride.

3. The method of claim 1, wherein decomposing comprises treating calcium carbonate with elevated temperatures.

4. The method of claim 3, wherein the elevated temperature about 850° C. or more.

5. The method of claim 1, wherein decomposing is performed with an acid.

6. The method of claim 5, wherein the acid comprises a mineral acid, an organic acid, hydrochloric acid, phosphoric acid, nitric acid and/or acetic acid.

7. The method of claim 1, wherein decomposing is performed by corona discharge.

8. The method of claim 1, wherein reacting urea with calcium chloride further forms ammonium chloride.

9. The method of claim 1, wherein reacting urea with calcium chloride further comprises treating with urease and/or urease-producing organisms.

10. The method of claim 9, wherein the urease-producing organisms comprise spores and/or vegetative cells.

11. The method of claim 10, wherein the urease-producing organisms comprise one or more of Sporosarcina spp., S. pasteurii, S. ureae, Proteus spp., P. vulgaris, P. mirabilis, Bacillus spp., B. sphaericus, B. megaterium, Myxococcus spp., M. xanthus, Helicobacter spp., H. pylori, and variants, serotypes, mutations, recombinant forms, and combinations thereof.

12. The method of claim 10, further comprising reacting urea with calcium chloride in the presence of urease-producing organisms and supplemental materials.

13. The method of claim 12, wherein the supplemental materials comprise organic or inorganic material, rock, glass, wood, paper, metal, plastic, polymers, fibers, minerals or combinations thereof.

14. A method comprising:

decomposing calcium carbonate to form calcium chloride and carbon dioxide, which react to form calcium dioxide;

reacting calcium dioxide with ammonium in a process to form urea; and

reacting calcium chloride with urea to form biocement.

15. The method of claim 14, wherein decomposing comprises treating calcium carbonate with elevated temperatures.

16. The method of claim 15, wherein the elevated temperature is about 850° C. or more.

17. The method of claim 14, wherein decomposing is performed with an acid.

18. The method of claim 17, wherein the acid comprises a mineral acid, an organic acid, hydrochloric acid, phosphoric acid, nitric acid and/or acetic acid.

19. The method of claim 14, wherein decomposing is performed by corona discharge.

20. The method of claim 14, wherein reacting calcium chloride with urea further comprises treatment with urease and/or urease-producing organisms.

21. The method of claim 20, wherein the urease-producing organisms comprise spores and/or vegetative cells.

22. The method of claim 21, wherein the urease-producing organisms comprise one or more of Sporosarcina spp., S. pasteurii, S. ureae, Proteus spp., P. vulgaris, P. mirabilis, Bacillus spp., B. sphaericus, B. megaterium, Myxococcus spp., M. xanthus, Helicobacter spp., H. pylori, and variants, serotypes, mutations, recombinant forms, and combinations thereof.

23. The method of claim 20, further comprising reacting urea with calcium chloride in the presence of urease-producing organisms and supplemental materials.

24. The method of claim 23, wherein the supplemental materials comprise organic or inorganic material, rock, glass, wood, paper, metal, plastic, polymers, fibers, minerals or combinations thereof.

25. A method comprising:

decomposing calcium carbonate to form calcium oxide and carbon dioxide, wherein the calcium oxide is treated with ammonium chloride to form calcium chloride; and

reacting calcium chloride with urea to form biocement.

26. The method of claim 25, wherein decomposing comprises treating calcium carbonate with elevated temperatures.

27. The method of claim 26, wherein the elevated temperature about 850° C. or more.

28. The method of claim 25, wherein decomposing is performed with an acid

29. The method of claim 28, wherein the acid comprises a mineral acid, an organic acid, hydrochloric acid, phosphoric acid, nitric acid and/or acetic acid.

30. The method of claim 25, wherein decomposing is performed by corona discharge.

31. The method of claim 25, wherein reacting urea with calcium chloride further comprises treatment with urease and/or urease-producing organisms.

32. The method of claim 31, wherein the urease-producing organisms comprise spores and/or vegetative cells.

33. The method of claim 32, wherein the urease-producing organisms comprise one or more of Sporosarcina spp., S. pasteurii, S. ureae, Proteus spp., P. vulgaris, P. mirabilis, Bacillus spp., B. sphaericus, B. megaterium, Myxococcus spp., M. xanthus, Helicobacter spp., H. pylori, and variants, serotypes, mutations, recombinant forms, and combinations thereof.

34. The method of claim 32, further comprising reacting urea with calcium chloride in the presence of urease-producing organisms and supplemental materials.

35. The method of claim 34, wherein the supplemental materials comprise organic or inorganic material, rock, glass, wood, paper, metal, plastic, polymers, fibers, minerals or combinations thereof.