Patent Application
20160318798
Flue gas desulfurization (FGD) is a process used in coal-fired power plants to remove sulfur dioxide (SO2) from coal combustion flue-gas. In the wet FGD process, the SO2 is removed by contacting the flue-gas with an aqueous solution or slurry containing either lime (Ca[OH]2), or limestone (CaCO3). The soluble calcium cation reacts with the gaseous SO2 to form calcium sulfite or calcium sulfate (gypsum) solids which are removed from the scrubber slurry by filtration. Along with SO2, the FGD process also captures other flue gas constituents such as chlorides (in the form of HCl and metal chlorides), selenium, and arsenic. Chlorides concentration in particular can be quite high in FGD slurry and solutions depending on the type of coal being burned.
After filtering the sulfur byproduct solids (calcium sulfite and calcium sulfate) from the FGD slurry, the vast majority of the scrubbed constituents end up in the FGD wastewater (FGDW). Until now, power plants have been able to comply with EPA regulations by disposing of the FGDW by combining it with other (much less concentrated) wastewater streams from different processes within the power plant, then holding it in onsite detention basins, allowing solids to settle, and subsequently releasing the diluted, combined wastewater back into natural wasters. New EPA regulations now require the treatment of individual wastewater streams before they are diluted and released into the environment. These new regulations require Power Plants to either dispose of the FGDW without releasing it into the environment, or to reduce the contaminant concentrations to appropriate levels before the FGDW is combined with other wastewater from the plant. Concentrating the FGDW into a brine and evaporating its residual water would result in a hygroscopic calcium chloride that would adsorb ambient moisture and becomes a difficult to handle slime. The disposal of the concentrated brine or the unstable calcium chloride is very challenging.
In one exemplary embodiment of the invention, a cementitious mixture is provided wherein the mixture comprises: a) precipitate calcium carbonate (PCC) and b) a hydraulic cement. The PCC is obtained as precipitate product from reaction of flue gas desulfurization wastewater (FGDW) and sodium carbonate.
In certain exemplary embodiments, the hydraulic cement comprises Portland Cement (PC) clinker. In some embodiments, the hydraulic cement comprises a pozzolanic material with the PCC being present in an amount of 1-35 wt % based on the weight of PCC and hydraulic cement. In certain aspects of the invention, the pozzolanic material may comprise fly ash.
In further aspects of the invention, the cementitious mixture of PCC and hydraulic cement is hydrated via the addition of water thereto. The water c) may be present in an amount of c): 0.15-1.5x, wherein x is the combined weight of PCC and hydraulic cement. In further embodiments, the PCC has a particle size ranging from 1-100 μm, and in other instances, the median particle size of the PCC may be in the range of about 10-20 μm or even within the range of about 10-15 μm.
Other aspects of the invention pertain to a calcium carbonate product that is adapted for use in a cementitious mixture. The calcium carbonate is a reaction product of FGDW and soda ash. The calcium carbonate product may have a particle size of about 1-100 μm and a median particle size of about 10-20 μm.
The calcium carbonate product may be in combination with fly ash wherein the calcium carbonate is present in an amount of 1-99 wt % based on the combined weight of the calcium carbonate product and the fly ash. The fly ash may be present in an amount of 99 wt % -1 wt % based upon the combined weight of the calcium carbonate and fly ash.
In other embodiments of the invention, methods are provided for making cementitious mixtures comprising mixing precipitate calcium carbonate (PCC) and a hydraulic cement to form a mix. The PCC is obtained as a precipitate product from reaction of flue gas desulfurization wastewater (FGDW) and sodium carbonate. The hydraulic cement may, for instance, comprise Portland Cement clinker. Water is added to the mix, and in some instances, fly ash is also added to the mix. In other exemplary embodiments, aggregate is added to the PCC/hydraulic cement mix.
The invention will be further described in the appended drawings and following detailed description. In the drawings:
In one exemplary embodiment, a process is disclosed whereby value added industrial products can be recovered from FGDW, and make it easier to dispose of or reuse the remaining water. The basic chemical principle of this process is to convert the unstable calcium chloride into a valuable calcium carbonate mineral product. The FGDW, which contains high levels of chlorides (primarily CaCl2) is reacted with sodium carbonate (in the form of soda ash) to Precipitate Calcium Carbonate (PCC). (See Equ 1. below).
CaCl2 aqueous+Na2CO3 solid→CaCO3 solid30 2NaClaqueous Equ 1.
The precipitated CaCO3 is collected by a filtration process, the liquid filtrate can then be concentrated and dried to produce non-hygroscopic sodium chloride (NaCl). Table 1 shows the chemistry of actual FGDW from a power plant burning Illinois Basin bituminous coal, as well as the soda ash treated and filtered FGDW at the laboratory scale.
Chemical compositions of the two solid products (CaCO3 and NaCl) from this FGD brine treatment process are summarized in Table 2. This process allows for the beneficial use of these two recovered materials and the reuse of treated water.
Table 3 summarizes some of the potential applications for the recovered CaCO3 and NaCl generated from FGDW in this conversion. Of particular interest is the use of CaCO3 precipitate (PCC) as a replacement for mined and milled limestone in Portland Limestone Cement.
Conventional Portland Limestone Cement (PLC) is manufactured by co-grinding mined limestone with cement clinker. Typically, in PLC processes from about 6-35% limestone is co-ground with the clinker. Co-grinding these two dissimilar materials has been challenging for the cement industry thereby limiting the potential limestone content of PLC. Using precipitated calcium carbonate from the disclosed processed will eliminate the need to co-grind the raw limestone with the clinker and allow for the optimization of limestone Portland Cement.
PLC has the potential to significantly improve concrete sustainability with lower carbon footprint and lower energy requirement, due to the decreased clinker content, and similar performance characteristics as compared to Ordinary Portland Cement (OPC). PLC can be used as a direct substitution for OPC in concrete mixtures. The use CaCO3 precipitate recovered from FGDW using the disclosed process can further improve the value proposition. There are measurable physical and chemical benefits from using limestone in PLC that improve setting and strength characteristics, especially when supplementary cementitious materials (SCMs) like fly ash are also included in the concrete mixture.
The physical benefits result from the fineness of the PCC which provides better particle packing and higher paste density due to the enhanced overall cement particle size distribution. The smaller PCC particles in suspension between larger PC particles provide nucleation sites that improve hydration reaction efficiency. These nucleation sites are essentially intermediate sites for calcium silicate hydrate (CSH) growth.
Precipitated CaCO3 from FGDW provides the same physical benefits to concrete owing to the fine precipitate grade particle size.
Chemically, limestone contributes calcium compounds that dissolve quickly and become available for hydration interaction. Calcium carbonate reacts with aluminate compounds to produce durable mono- and hemi-carboaluminate hydrate crystals.
Reference Numeral 501=Control
Reference Numeral 502=10% PPC (CaCO3)/PC
Reference Numeral 503=15% PPC(CaCO3)/PC
Reference Numeral 504=20% PPC (CaCO3)/PC
Other than in cement and concrete, there is a wide range of industrial and agricultural applications for powdered or precipitated CaCO3. Such applications include: paints, plastics, rubber, ceramic and paper. CaCO3 is also used as a filler material in carpet backing, which provides weight to the carpet and allows it to lay flat. In all these applications, CaCO3 is used as chemically inert filler.
Applications for NaCl from Treated FGDW
NaCl is extensively used in tanning leather, whereby animal hides are cured with salt so as to remove all the excess moisture and water from it. The salt draws water out of the leather hides and helps in protecting hides from bacterial growth.
NaCl is spread on roadways to help reduce the accumulation of ice or to melt existing ice, it works by reducing the melting or freezing point of ice or freezing rain.
NaCl is used to extinguish class D fires that are caused by the burning of metals like aluminum, magnesium potassium, etc. NaCl is spread on the fire creating a crust which smothers the fire.
NaCl is widely used for the production of chlorine. The process of electrolysis is carried out wherein electric current is passed through the solution of sodium chloride to prepare the element chlorine. This element is used extensively for making PVC and pesticides.
It is thus apparent then, that in certain embodiments, the present invention pertains to a cementitious mixture which comprises precipitate calcium carbonate (PCC) in combination with hydraulic cement. The PCC is obtained as precipitate product from reaction of flue gas desulfurization wastewater (FGDW) and sodium carbonate. In some instances, the hydraulic cement may comprise Portland Cement clinker. As is traditional in the industry, Portland Cement clinker is known to comprise alite, belite, tricalcium aluminate, and tetracalcium aluminate ferrite.
The weight ratio of PCC:hydraulic cement may be on the order of about 1-15 wt % PCC:combined Cement PCC (PLC).
In some embodiments, the hydraulic cement comprises a pozzolanic material. The pozzolan may comprise a natural pozzolan such as volcanic ash or diatomite or it may comprise an artificial pozzolan such as fly ash, calcined diatomite or calcined clay.
In certain embodiments, hardenable cementitious mixtures are made from:
Aggregate such as sand, gravel, crushed stone, crushed rock, blast furnace slag, combustion slag, etc., may also be added to the cementitious mixtures, and accelerators or retardants can be added as needed. Generally, water added to the dry components (i.e., PCC, hydraulic cement, pozzolans, aggregate) should be on the order of about 0.15-1.5 times the weight of the dry components.
As is apparent from the above, the PCC serves as a limestone substitute or source in the cementitious compositions, providing CaCO3. Preferably, the PCC has a particle size of about 1-100 μm and a median particle size of about 10-20 μm, preferably 10-15 μm.
As presently envisioned, the PCC can be supplied to concrete producers who will mix it with the appropriate hydraulic cement and optional aggregate, etc. Water will be added at the work location to provide a hardenable composition.
In other aspects, the PCC may be combined with fly ash and provided to the concrete producer as a dry mix that will be combined with hydraulic cement, optional aggregate, etc. Such dry mixes, as presently envisioned, may comprise about 1-99% PCC and 99-1 wt % fly ash. At the work location, the dry mix containing PCC, hydraulic cement, optional aggregate, etc., is mixed with water.
While the present invention has been described with respect to particular examples, it is apparent that numerous other forms and modifications of the invention will be obvious to those skilled in the art. The appended claims and this invention should be construed to cover all such obvious forms and modifications which are within the spirit and scope of the present invention.
This application claims the priority benefit of U.S. Provisional Patent Application Ser. No. 62/154,237 filed Apr. 29, 2015.
| Number | Date | Country | |
|---|---|---|---|
| 62154237 | Apr 2015 | US |
