Title of Invention	PHOTOCATALYTIC COMPOSITES CONTAINING TITANIUM AND LIMESTONE FREE FROM TITANIUM DIOXIDE
Abstract	New photocatalytic product comprising compounds of titanium integrated with limestone. The product is obtained by reacting limestone with a suitable precursor of titanium dioxide in a basic solution, recovering the product in particular condi- tions, drying it and calcining it. By operating in presence of sodium, a composite is obtained substantially free from titanium dioxide, containing limestone and calcium titanate. The composite thus obtained, used as such or in mixture with other components, has shown an unexpectedly high photocatalytic activity.

Title of Invention

PHOTOCATALYTIC COMPOSITES CONTAINING TITANIUM AND LIMESTONE FREE FROM TITANIUM DIOXIDE

Abstract

New photocatalytic product comprising compounds of titanium integrated with limestone. The product is obtained by reacting limestone with a suitable precursor of titanium dioxide in a basic solution, recovering the product in particular condi- tions, drying it and calcining it. By operating in presence of sodium, a composite is obtained substantially free from titanium dioxide, containing limestone and calcium titanate. The composite thus obtained, used as such or in mixture with other components, has shown an unexpectedly high photocatalytic activity.

Full Text	Title: "Photocatalytic composites containing titanium and limestone free from titanium dioxide" DESCRIPTION Field of the invention The present invention concerns the field of photocatalytic materials used for decontamination from environmental pollutants, and for preserving the original colour of articles of manufacture exposed to said pollutants, with application in particular in the field of cement. State of the art The use of titanium dioxide in the form of anatase as photocatalyst in cement compositions is widely known. The resulting compositions are exploited to make various construction elements and articles of manufacture endowed with photocatalytic properties, capable of decomposing environmental pollutants in presence of light and oxygen. In these compositions titanium dioxide can be dispersed in bulk with the remaining components (WO-A-9805601, to the Applicant); alternatively, firstly a cement base free from titanium dioxide is formed, and then it is externally coated with titanium dioxide, optionally mixed with binders and/or adhesives of various types. In all these cases the titanium-containing photocatalyst is present in the form of a mere physical mixture with the mineral components of the cement composition. The interaction that is established in these cases is of the mechanical or weakly electrostatic kind, and thus there is no adequate continuity between photocatalyst and rest of the mixture. This can lead to various problems linked to inadequate interpenetration of the photocatalytic components and of those constituting the inert material. The close interaction between photocatalyst and mineral elements of the cement is however important for an effective photocatalytic action: indeed, in photocatalytic cements the cement component is known to simultaneously absorb atmospheric pollutants through a process of rapid dynamic equilibrium with the environment (adsorption/desorption): the pollutant temporarily adsorbed is then decomposed by the photocatalyst. However, in known products the adsorbent part and the photocatalytic part are clearly distinct: in this situation a part of the adsorbed pollutant can be desorbed before the photocatalyst is able to act sufficiently, with the consequence of an insufficient level of photocatalysis. In an attempt to improve the degree of interaction between photocatalytic part and inert part, some materials have been proposed in which the titanium dioxide is supported on mineral components. An example of these products is titanium dioxide supported on metakaolin, described in patent application MI2007A002387, to the Applicant. However, as also highlighted in the aforementioned application in reference to various supports, the reactivity of the titanium dioxide varies greatly depending on the support, and the properties of the resulting product are extremely variable and often unsatisfactory. A high-performance photocatalytic is particularly desirable in the case of cement materials, characterised by a very low cost/weight ratio: for these materials, any increase in production costs linked to the addition of fine additives reflects greatly on said ratio, risking to make the end product unmarketable. In particular, titanium dioxide has a significantly high cost. It may therefore be useful to have composite materials that are free from titanium dioxide, and that despite this have a photocatalytic effect equal to or greater than that provided by titanium dioxide. Currently the need for photocatalytic composites that meet the aforementioned requirements is largely unfulfilled. Calcium titanate is a material with properties of refractoriness, chemical resistance and of a semi-conductor. It is found in nature in various forms (e.g. perovskite) characterised by a mixture of phases with different ratios between calcium and titanium, e.g. CaTiO3, Ca3Ti2O7, Ca4Ti3O10, CaTi4O9, Ca3Ti2O5, Ca2TiO4, CaTi204(OH)2, etc. It can be prepared via dry or wet route. Dry preparation is generally carried out by reacting titanium oxide and calcium carbonate at temperatures greater than 1300°C. (Izv. Akad. Nauk USSR-Neorg. Mater., 11 (1975) 1622). Wet preparation can be carried out in different ways, e.g. hydrothermically by heating an aqueous suspension of titanyl oxalate and a hydrated titanium gel to 150-200°C in an autoclave (T.R.N. Kutty and R. Vivekanandam, Mater. Lett., 5 (1987) 79-83). It is also known to obtain calcium titanate via peroxide route by treating an aqueous calcium chloride and titanium chloride solution with hydrogen peroxide and ammonia, and subsequently calcining the precipitate obtained. (Pfaff, J.Eur.Ceram.Soc.,9,1992,293-299). Mixtures of cement and titanates have occasionally been described. For example JP20002 26248 describes cement mixtures with good flame and acid resistance containing a ceramic powder that includes potassium titanate and titanium dioxide. SUMMARY A new photocatalytic composite has now been identified in which the titanium is tightly and stably integrated with a mineral currently used in the field of cement, which is limestone. The composite is obtained by reacting a precursor of titanium dioxide with limestone in basic solution, recovering the product in particular conditions, drying it and calcining the solid obtained. The composite, obtained by operating in presence of sodium, contains limestone and calcium titanate, the latter characterised by two crystalline phases not known until now (herein characterised and referred to as CT2 and CT5). The composite thus obtained, which can be used as such or in mixture with other components, has shown an unexpectedly high photocatalytic activity. DESCRIPTION OF THE FIGURES Fig. 1: Diffractogram of the composite STCA 02 Fig. 2: Diffractogram of the acid residue of the composite STCA02 Fig. 3,4: Images in bright field TEM of a calcite crystal and of the micro- nanocrystalline aggregates (scale 0.5 μm) Fig. 5: Image in bright field TEM of the crystals of the phases CT2 (hl, o1, 11, ml) and CT5 (g1 and n1) (scale 100 nm) Fig. 6: Image in bright field TEM of the crystals of phases CT2 (e1) and CT5 (al, bl, cl, dl) (scale 50 nm) Fig. 7: Abatement of NO on CEN mortar according to the type of photocatalyst. As such: CEN mortar with only Italbianco cement. As such CA-01: CEN mortar with Italbianco cement and limestone. Fig. 8: Abatement of NOx on CEN mortar by the composite STCA02 with respect to the cement. DETAILED DESCRIPTION The photocatalytic composite object of the invention comprises limestone and calcium titanate; the latter is present in part in the known form of perovskite (traces) and in part in the form of two new crystalline phases, herein identified here and characterised for the first time, referred to as CT2 and CT5. For the purposes of the present invention by calcium titanate in crystalline phase CT2 it is meant a crystalline chemical compound containing calcium and titanium, present in molar ratio 1:2, having empirical formula CaTi20s, identified by the characteristic diffraction peaks: (002) d(interplanar distance)=4,959; (210-202) d=2,890; (013) d=2,762 and (310-122) d=2,138. These peaks are indexed with an orthorhombic cell having the following reticular parameters: a=7.1 A, b=5.0 A, c=9.9 A. For the purposes of the present invention by calcium titanate in crystalline phase CT5 it is meant a crystalline chemical compound containing calcium and titanium, present in molar ratio 1:5, having empirical formula CaTi5011, identified by the characteristic diffraction peaks: (002) d=8,845; (023) d=4,217; (110) d=3,611 and (006) d=2,948. These peaks are indexed with an orthorhombic cell having the following reticular parameters: a=3.8 A, b=12.1 A, c=17.7A. For the purposes of the present application the crystallographic parameters for phases CT2 and CT5 herein indicated and claimed are meant to be variable within a range of about ± 0.5 A for the parameters of the cell a,b,c, and within a range of about ± 0.05 for the interplanar distances d; similarly, the calcium: titanium molar ratios indicated above are meant to be variable by about ± 10%. The microstructural characteristics of phases CT2 and CT5 are widely illustrated in the experimental part. In the composites object of the invention, the amounts of calcium titanate in CT2 phase and in CT5 phase are widely variable: preferably they are present in similar amounts. In an embodiment of the invention the calcium titanate is present exclusively in CT2 phase or exclusively in CT5 phase. The aforementioned calcium titanate in the CT2 and/or CT5 phase represents per se constitutes a particular embodiment of the present invention. The limestone used to form the composite is the commercially available one, preferably in finely divided form, also commercially available (example source: cava di Tinella (Fasano, Brindisi)) The BET surface area of the composite generally ranges from 1 to 150 m2/g, with preferred values between 2 and 20 m2/g, e.g. between 5 and 10 m2/g. The process for obtaining the composites described here constitutes a further aspect of the invention. It generally comprises reacting limestone and a precursor of titanium dioxide in a basic solution containing sodium ions. The reactants can be added into the reactor in indifferent order; preferably the limestone is contacted first with the basic solution and then with the precursor. The precursor used is preferably titanyl sulphate. The basic solution containing sodium ions is preferably an aqueous NaOH solution. In the process conditions the precursor converts totally into calcium titanate. Preferably, an amount of precursor is used corresponding to a theoretical content of Ti02 (i.e. calculated considering a total conversion of the precursor into Ti02 ) of about 20% by weight with respect to the limestone. The reaction goes on for a time of between 45 and 90 minutes, at a temperature ranging from 20 and 80 °C. At the end of the reaction, the resulting solid product is recovered from the solution, optionally washed, then dried and calcined. The washing generally takes place with water; it must in any case be partial, in order not to completely eliminate the sodium residues coming from the basic solution used. Alternatively, the solid can be completely washed (or else a basic solution not containing sodium can be used) and then a sufficient amount of sodium can be introduced, e.g. by dispersing the solid a suitable aqueous solution having an adequate concentration of sodium ions. Indeed, it has been observed that in presence of sodium (at least 0.05% by weight, expressed as Na20 over the dry product), the precursor of Ti02 used does not convert into Ti02, but it obtains substantially exclusively calcium titanate; the composite is thus substantially free from titanium dioxide. By "substantially free from" it is meant a composite in which the titanium dioxide is absent, or else it is present in amounts not greater than 2% by weight. The presence of sodium at the end of the washing can be tested through methods known in the field, e.g. via flame test, X-ray fluorescence and atomic absorption, etc. In case it is opted not to wash the reaction solid, the presence of substantial amounts of sodium in the product (deriving from the initial basic solution) is in any case ensured and does not need to be tested analytically. The calcining preferably takes place at a temperature ranging from 300 and 800°C, e.g. between 450 and 700 °C; particularly effective photocatalytic composites have been obtained by calcining at about 650°C. Heat treatments below 525°C are less preferable since they need long times (over 24 hours) for the formation of the desired calcium titanates. The reaction speed at temperatures of between 550 and 6506C is high. Temperatures of over 700°C are preferably to be avoided because they cause the start of limestone decarbonatation.. A further object of the present invention is the photocatalytic composite obtained through the process described above. From the point of view of the elemental composition (as detectable by X-ray fluorescence and atomic absorption), the composites according to the invention can be further characterised as follows: The elemental composition given in the tables refers to the composite as a whole: such a composite comprises, in addition to calcium titanate, limestone and residues of the reactants used for the titanate-forming reaction.. In particular, the analysis confirms the presence of non-negligible amounts of sodium in the composite, responsible for the complete conversion of the TIO2 precursor into calcium titanate. Indeed, it has been observed that composites obtained in a similar way, but carefully washing the reaction solid until substantially all traces of sodium have been eliminated (sodium residue below 0.05% by weight, expressed as Na20 over the dry product), contained substantial amounts of titanium dioxide in mixture with the calcium titanate: both products derived from the conversion of the TiOaprecursor ; the group of composites thus obtained has specific application advantages and is the object of a co-pending application to the Applicant. As highlighted by the electron microscopy observations contained in the experimental part, the calcium titanate in the present composites is in the form of crystalline grains of a size of about 10-150 microns, closely connected to limestone grains. There is thus clearly a strong aggregative link between the photocatalytic portion of the composite (calcium titanate) and the mineral support component (limestone); within these aggregates, the calcium titanate crystals in phase CT2 are generally rounded, whereas those in phase CT5 generally have a characteristic rod shape. The present invention represents a successful example of composite material in which the calcium titanate is closely and stably linked to a support material (limestone) able to be used in the cement field.. The close interconnection between the photocatalytic and non-photocatalytic parts of the composite obtains a substantial continuity between absorption sites of the pollutants and decomposition sites thereof, with the advantage of high photocatalytic efficiency. Such efficiency has been highlighted by abatement tests of N-oxides (NOx) and VOC (aromatic hydrocarbons), using the composite of the invention either as such, or incorporated in bulk in a cement matrix. With the present invention a highly integrated multi-phase composite material has been obtained, free from titanium dioxide, having high photocatalytic activity, particularly suitable for being incorporated in cement matrices. Despite the lack of TiC>2, the "absolute" photocatalytic activity of the composite (expressed as amount of NO abated) proved unexpectedly similar to that of equivalent commercial products containing the best known photocatalyst (anatase titanium dioxide, PC-105, Millenium). The "relative photocatalytic activity (expressed as ratio between the amount of NO abated and the total weight of titanium present in the composite) proved to be even greater than that of similar composites containing the same calcium titanate and titanium dioxide: there is thus, for the calcium titanate of the invention and its composites, an intrinsically greater photocatalytic activity than that of titanium dioxide, the latter up to now considered the photocatalyst of choice. A further object of the invention is the use of the photocatalytic composite described earlier as photocatalytic product as such, or in the preparation of cements and cement articles of manufacture endowed with photocatalytic activity. The article of manufacture can contain the composite dispersed in bulk, or layered on its outer surfaces, as coating: in the latter case the photocatalytic composite is preferably mixed with suitable tackifiers, used to promote suitable cohesion between article of manufacture and coating layer. In any case, the composite is used in amounts such as to obtain a concentration of composite in bulk preferably ranging from 1% to 15 %, more preferably between 2% and 10%. The methods for the dispersion in bulk or for the outer coating are per se widely known in the field in question. An aspect of the invention thus concerns photocatalytic composition, in particular of the cementitious type, comprising the composite described above. The further elements of the cement composition are those commonly known, in particular: various hydraulic binders, optional aggregates and additives used in the cement field. The hydraulic binders and the aggregates (defined for example by standards UNI ENV 197.1 and UNI 8520) are products widely known in the field. The compositions according to the invention can be provided in fluid state, or else mixed with water (to form mortars or concretes, depending upon the granule size of the aggregates used), or else they can be provided in the corresponding forms free from water (dry premixes). These compositions are used to form photocatalytic articles of manufacture through suitable casting in moulds and similar technologies; the resulting articles of manufacture contain the composite of the invention dispersed in bulk. Alternatively, they can be used as coating formulations of pre-existing articles of manufacture, preferably co- formulated with suitable tackifiers. The invention is illustrated hereafter not for limiting purposes through the following examples. EXPERIMENTAL PART EXAMPLE 1 Preparation of the composite (STCA02) 280 g of a commercial calcareous filler (origin: cava Tinella di Brindisi) were stirred, suspended in 700 ml of a NaOH solution (200g/l in distilled water), and an aqueous solution of 700 ml of TiOS04 (100g/l di Ti02), so as to have a theoretical Ti02 content equal to about 20% by weight, was dripped. The powder obtained was filtered and partially washed with distilled water, thus keeping a part of the sodium deriving from the NaOH in the solid. The powder was then dried at 105°C in a ventilated oven. Before performing the calcining heat treatment at 650 °C for 2 hours, the product was broken up so as to obtain a powder. EXAMPLE 2 Alternative for the preparation of the composite (STCA02) 280 g of a commercial calcareous filler (origin: cava Tinella di Brindisi) were stirred, suspended in a 2M aqueous solution of NH4HCO3 (slightly in excess with respect to the titanyl sulphate), and an aqueous solution of 700 ml of TiOSOt (100g/l of TiCte), so as to have a theoretical content of TIO2 equal to about 20% by weight, was dripped. The powder obtained was filtered and completely washed with distilled water. The powder was then dried at 105°C in a ventilated oven. The solid product was then again dispersed in an aqueous solution at a known concentration of NaOH (the concentration is such as to introduce the desired amount of Na, expressed as Na20, over the solid), and kept agitated until the solution is completely dry. Before performing the calcining heat treatment at 650 °C for 2 hours, the product was broken up so as to obtain a powder. EXAMPLE 3 Micro-structural characterisation. The composite STCA 02 obtained in example 1, subjected to diffractometric analysis (diffractometer BRUKER D8 Advance and CuKa (Acu= 1.545 A) radiation, proved to be a polyphase mixture consisting of calcite, traces of perovskite, and calcium titanate in different crystalline phases. In particular, the diffraction profile showed the presence of a series of peaks not attributable to known crystalline phases, which can be referred to two different phases (CT2 and CT5) that proved to be calcium titanate-containing compounds with ratios of Ca:Ti 1:2 and 1:5 respectively (see Fig. 1). The peaks attributable to the two phases are of similar intensity, indicating that they are present in the composite in comparable amounts. The accurate position of the peaks of the new crystalline phases was determined through diffractometric analysis of the sample after elimination of the calcite by treatment in diluted HC1 (1:10) and subsequent drying at 60°C (Fig. 2). The observed interplanar distances (d) of the two phases are shown in the following tables, wherein h,k,l indicate the Miller indices, and °26 indicate the diffraction angle. Microscope analysis. In order to better understand the nature of the sample, both the sample as such and the acid residue were subjected to analysis by transmission electron microscopy (TEM). The observations allowed to establish that the sample consisted of a mixture of crystals of a few microns of calcium carbonate and of crystalline micro-nano aggregates (grains) of calcium titanate and carbonate having variable size from 50 to 300 nm (see Figs. 3 and 4). Through microanalysis with EDS detector it has been possible to identify two families of crystals containing both Ca and Ti, one with a characteristic rounded shape, the other with an elongated shape (Fig. 5, 6). The semiquantitative analyses made by focussing the electron beam on different crystals of the first phase have allowed to establish that the Ca:Ti ratio in this phase, here referred to as CT2, is about 1:2 High-resolution images were carried out on some crystals of this phase with the corresponding Fourier transforms, from which it has been possible to extract information on the cell parameters for the CT2 phase: Orthorhombic: a=7.1 A, b=5.0 A, c=9.9 A. The extinction conditions observed are the following: Okl k+l=2n hhl no cond (1) 2hhl no cond hOO h=2n OkO k=2n (2) By adding the extinctions (1) and (2) one obtains as possible space group Pna21 (Herman Mauguin Symbol), corresponding to the space group 33 shown in International Tables of Crystallography, vol. A, "Space Groups Symmetry", V ed., Kluver Acad. Publ. 2002) Possible monoclinic distortions can exist and the TEM data obtained cannot exclude them. The software used for simultaneously indexing such patterns was QED (Belletti D., Calestani G., Gemmi M, Migliori A. - QED V 1.0: a software package for quantitative electron diffraction data treatment Ultramicroscopy, 81 (2000) pp 57-65). In light of the information obtained on the cell of this new phase it was possible to assign some of the peaks not identified in the diffractogram of the sample STCA06 to the CT2 phase. The remaining peaks are attributable to a different phase (CT5, see later). The cell parameters of the CT2 phase have been further refined through fitting of the calculated diffractometric profile with the real one. Through microanalyses with EDS detector it has been confirmed that the family of rounded crystals is conform with CT2 phase, found in the sample of photocatalytic composite. Other crystals of characteristic elongated form were found to contain Ca, Ti and small amounts of Na. This new crystalline phase, characterised by a Ca:Ti ratio of about 1:5, is referred to here as CT5. Similarly to what was done for CT2, some high-resolution images were taken, with the corresponding Fourier transforms from which it has been possible to extract information on the cell parameters. The main characteristic of this phase is a periodicity of 17.6 A. From the simultaneous indexing of such patterns via QED software (Belletti et al., op.cit.) it has been possible to derive a possible cell for the compound in question. The cell was orthorhombic C centred: a=3.8 (10) A, b=12.1 (20) A, c=17.7 (2) A (decimal error) Possible monoclinic distortions can exist and the TEM data obtained cannot exclude them. The extinction conditions observed are: hkl h+k=2n hkO h+k=2n Okl not able to be determined hOl h,l=2n hOO h=2n OkO k=2n 001 l=2n These extinctions are compatible with the following possible space groups: type C-c-: Cmc21, C2cm, Cmcm (corresponding to the space group 63, cf. International Tables of Crystallography, vol. A, "Space Groups Symmetry", V ed., Kluver Acad. Publ. 2002) in the case of extinction Okl k=2n; type Ccc-:Ccc2, Cccm in the case of extinction Okl k,l=2n. The cell parameters of the CT5 phase have been further refined through fitting of the calculated diffractometric profile with the real one. EXAMPLE 5 Analysis of specific BET surface and microporosity. The values measured during the analysis of the new photocatalytic composite STCA 02 shown in the table show an increase in the specific surface of the heat treated product (650'C), with respect to the limestone as such, with an increase in the non-microporous fraction. By working at different temperatures it is also observed that the surface area generally tends to decrease as the calcining temperature increases. EXAMPLE 6 Photocatalytic activity on cement: NOx abatement measurements. The composite STCA02 was mixed with white cement (Italbianco 52.5 di Rezzato) so as to obtain photocatalytic cements with percentage by weight of photocatalyst within the range 2.0 - 8.5%. NOx abatement analyses were carried out on cement mortars made with normalised sand CEN (according to UNI 196-1) by preparing tests in Petri dishes of diameter 8 cm and surface of about 60 cm2. The results obtained show an excellent behaviour of such cements, comparable to that of cement containing commercial anatase (Fig. 7). The abatement values measured on the mortars CEN containing the composite STCA02 at different concentrations on cement have shown very good NOx abatement values already at percentages of around 2.5% by weight. (See Fig. 7) The photocatalytic activity tends to increase as the calcining temperature of the sample increases. EXAMPLE 7 Photocatalytic activity on cement: VOC abatement measurements. The evaluation of the abatement capability of aromatic hydrocarbons was carried out using the pure photocatalytic products (not mixed with cement) under UV radiation. Ethylbenzene was used as organic substance, using a flow apparatus typical of tests on catalysts (oxidation of ethylbenzene in air). In this way the intrinsic activity of the material is determined, disregarding the diffusive phenomena. The results obtained show an excellent level of 5 abatement activity of the product. It is greater than the best commercial Ti02 (Fig. 8). CLAIMS 1. Photocatalytic composite substantially free from titanium dioxide, comprising limestone, and calcium titanate in the crystalline phases CT2 and/or CT5 characterised by the following diffraction peaks: CT2: (002) d=4,959; (210-202)d=2,890; (013) d=2,762 and (310- 122)d=2,138; CT5: (002) d=8,845; (023) d=4,217; (110) d=3,611 and (006) d=2,948, wherein the calcivm titapote inCT2 phase has empiriesl formulaCaTi2O5, and tha calcivm titanate in CTS phase has ompirical formulaCaTi5O11, 2. Composite according to claim 1, wherein said peaks of the CT2 phase are indexed with an orthorhombic cell having the following reticular parameters: a=7.1 A, b=5.0 A, c=9.9 A. 3. Composite according to claim 1, wherein said peaks of the CT5 phase are indexed with an orthorhombic cell having the following reticular parameters: a=3.8 A, b=12.1 A, c=17.7 A. 4. Composite according to claims 1-3 wherein the CT2 phase is present in amount equal or similar to the CT5 phase. 5. Composite according to claims 1-4 having specific BET surface ranging from 1 to 150 m2/g. 6. Composite according to claim 5, having specific BET surface ranging from 2 to 20 m2/g. 7. Composite according to claim 6, having specific BET surface ranging from 5 to 10 m2/g. 8. Calcium titanate with high photocatalytic activity, characterised by the presence of the crystalline phases CT2 and/or CT5, as described in claims 1- 9. Process to obtain the composite described in claims 1-7, comprising reacting limestone and a precursor of titanium dioxide in presence of a basic solution, recovering the solid product thus obtained, optionally washing it, then drying and calcining it wherein: (a) said basic solution contains sodium ions, and said washing is performed in a way not totally eliminating the sodium present, (a) or said basic solution contains sodium ions, said washing totally eliminates the sodium present, and the product to be calcined is supplemented with a sodium-containing compound or said basic solution does not contain sodium ions and said optionally washed, dried solid product is added with a sodium containing compound,and then calcined. 10. Process according to claim 9, wherein the product to be calcined contains a residual amount of sodium of at least 0.05% by weight. 11. Process according to claim 9, wherein the precursor is titanyl sulphate, la basic solution contains NaOH, and the solid product is calcined at a temperature ranging from 300 to 8000C. Process according to claim 11, wherein the solid product is calcined at a temperature ranging from 450 to 700°C 13.. Use of a composite as described in claims 1-7, in preparing an article of manufacture having photocatalytic activity. 14. Use according to claim 13, wherein the article of manufacture contains the composite dispersed in bulk. 15. Use according to claim 13, wherein the article of manufacture contains the composite layered on at least part of its external surface, as a coating element. 16. Cement composition comprising the photocatalytic composite described in claims 1-7, water, a hydraulic binder, and optionally aggregates. 17. Dry premix comprising the photocatalytic composite described in claims 1-7, a ft hydraulic binder, and optionally aggregates. Photocatalytic article of manufacture comprising, dispersed in bulk or New photocatalytic product comprising compounds of titanium integrated with limestone. The product is obtained by reacting limestone with a suitable precursor of titanium dioxide in a basic solution, recovering the product in particular condi- tions, drying it and calcining it. By operating in presence of sodium, a composite is obtained substantially free from titanium dioxide, containing limestone and calcium titanate. The composite thus obtained, used as such or in mixture with other components, has shown an unexpectedly high photocatalytic activity.

Full Text

Title: "Photocatalytic composites containing titanium and limestone free from
titanium dioxide"
DESCRIPTION
Field of the invention
The present invention concerns the field of photocatalytic materials used for
decontamination from environmental pollutants, and for preserving the
original colour of articles of manufacture exposed to said pollutants, with
application in particular in the field of cement.
State of the art
The use of titanium dioxide in the form of anatase as photocatalyst in
cement compositions is widely known. The resulting compositions are
exploited to make various construction elements and articles of manufacture
endowed with photocatalytic properties, capable of decomposing
environmental pollutants in presence of light and oxygen. In these
compositions titanium dioxide can be dispersed in bulk with the remaining
components (WO-A-9805601, to the Applicant); alternatively, firstly a cement
base free from titanium dioxide is formed, and then it is externally coated
with titanium dioxide, optionally mixed with binders and/or adhesives of
various types. In all these cases the titanium-containing photocatalyst is
present in the form of a mere physical mixture with the mineral components
of the cement composition. The interaction that is established in these cases
is of the mechanical or weakly electrostatic kind, and thus there is no
adequate continuity between photocatalyst and rest of the mixture. This can
lead to various problems linked to inadequate interpenetration of the
photocatalytic components and of those constituting the inert material. The
close interaction between photocatalyst and mineral elements of the cement
is however important for an effective photocatalytic action: indeed, in
photocatalytic cements the cement component is known to simultaneously
absorb atmospheric pollutants through a process of rapid dynamic
equilibrium with the environment (adsorption/desorption): the pollutant
temporarily adsorbed is then decomposed by the photocatalyst. However, in
known products the adsorbent part and the photocatalytic part are clearly
distinct: in this situation a part of the adsorbed pollutant can be desorbed

before the photocatalyst is able to act sufficiently, with the consequence of
an insufficient level of photocatalysis.
In an attempt to improve the degree of interaction between photocatalytic
part and inert part, some materials have been proposed in which the
titanium dioxide is supported on mineral components. An example of these
products is titanium dioxide supported on metakaolin, described in patent
application MI2007A002387, to the Applicant. However, as also highlighted
in the aforementioned application in reference to various supports, the
reactivity of the titanium dioxide varies greatly depending on the support,
and the properties of the resulting product are extremely variable and often
unsatisfactory.
A high-performance photocatalytic is particularly desirable in the case of
cement materials, characterised by a very low cost/weight ratio: for these
materials, any increase in production costs linked to the addition of fine
additives reflects greatly on said ratio, risking to make the end product
unmarketable.
In particular, titanium dioxide has a significantly high cost. It may therefore
be useful to have composite materials that are free from titanium dioxide,
and that despite this have a photocatalytic effect equal to or greater than
that provided by titanium dioxide.
Currently the need for photocatalytic composites that meet the
aforementioned requirements is largely unfulfilled.
Calcium titanate is a material with properties of refractoriness, chemical
resistance and of a semi-conductor. It is found in nature in various forms
(e.g. perovskite) characterised by a mixture of phases with different ratios
between calcium and titanium, e.g. CaTiO3, Ca3Ti2O7, Ca4Ti3O10, CaTi4O9,
Ca3Ti2O5, Ca2TiO4, CaTi204(OH)2, etc. It can be prepared via dry or wet route.
Dry preparation is generally carried out by reacting titanium oxide and
calcium carbonate at temperatures greater than 1300°C. (Izv. Akad. Nauk
USSR-Neorg. Mater., 11 (1975) 1622). Wet preparation can be carried out in
different ways, e.g. hydrothermically by heating an aqueous suspension of
titanyl oxalate and a hydrated titanium gel to 150-200°C in an autoclave
(T.R.N. Kutty and R. Vivekanandam, Mater. Lett., 5 (1987) 79-83). It is also

known to obtain calcium titanate via peroxide route by treating an aqueous
calcium chloride and titanium chloride solution with hydrogen peroxide and
ammonia, and subsequently calcining the precipitate obtained. (Pfaff,
J.Eur.Ceram.Soc.,9,1992,293-299).
Mixtures of cement and titanates have occasionally been described. For
example JP20002 26248 describes cement mixtures with good flame and acid
resistance containing a ceramic powder that includes potassium titanate
and titanium dioxide.
SUMMARY
A new photocatalytic composite has now been identified in which the
titanium is tightly and stably integrated with a mineral currently used in the
field of cement, which is limestone. The composite is obtained by reacting a
precursor of titanium dioxide with limestone in basic solution, recovering the
product in particular conditions, drying it and calcining the solid obtained.
The composite, obtained by operating in presence of sodium, contains
limestone and calcium titanate, the latter characterised by two crystalline
phases not known until now (herein characterised and referred to as CT2
and CT5). The composite thus obtained, which can be used as such or in
mixture with other components, has shown an unexpectedly high
photocatalytic activity.
DESCRIPTION OF THE FIGURES
Fig. 1: Diffractogram of the composite STCA 02
Fig. 2: Diffractogram of the acid residue of the composite STCA02
Fig. 3,4: Images in bright field TEM of a calcite crystal and of the micro-
nanocrystalline aggregates (scale 0.5 μm)
Fig. 5: Image in bright field TEM of the crystals of the phases CT2 (hl, o1, 11,
ml) and CT5 (g1 and n1) (scale 100 nm)
Fig. 6: Image in bright field TEM of the crystals of phases CT2 (e1) and CT5
(al, bl, cl, dl) (scale 50 nm)
Fig. 7: Abatement of NO on CEN mortar according to the type of

photocatalyst. As such: CEN mortar with only Italbianco cement. As such
CA-01: CEN mortar with Italbianco cement and limestone.
Fig. 8: Abatement of NOx on CEN mortar by the composite STCA02 with
respect to the cement.
DETAILED DESCRIPTION
The photocatalytic composite object of the invention comprises limestone
and calcium titanate; the latter is present in part in the known form of
perovskite (traces) and in part in the form of two new crystalline phases,
herein identified here and characterised for the first time, referred to as CT2
and CT5.
For the purposes of the present invention by calcium titanate in crystalline
phase CT2 it is meant a crystalline chemical compound containing calcium
and titanium, present in molar ratio 1:2, having empirical formula CaTi20s,
identified by the characteristic diffraction peaks: (002) d(interplanar
distance)=4,959; (210-202) d=2,890; (013) d=2,762 and (310-122) d=2,138.
These peaks are indexed with an orthorhombic cell having the following
reticular parameters: a=7.1 A, b=5.0 A, c=9.9 A.
For the purposes of the present invention by calcium titanate in crystalline
phase CT5 it is meant a crystalline chemical compound containing calcium
and titanium, present in molar ratio 1:5, having empirical formula
CaTi5011, identified by the characteristic diffraction peaks: (002) d=8,845;
(023) d=4,217; (110) d=3,611 and (006) d=2,948. These peaks are indexed
with an orthorhombic cell having the following reticular parameters: a=3.8 A,
b=12.1 A, c=17.7A.
For the purposes of the present application the crystallographic parameters
for phases CT2 and CT5 herein indicated and claimed are meant to be
variable within a range of about ± 0.5 A for the parameters of the cell a,b,c,
and within a range of about ± 0.05 for the interplanar distances d; similarly,
the calcium: titanium molar ratios indicated above are meant to be variable
by about ± 10%.
The microstructural characteristics of phases CT2 and CT5 are widely
illustrated in the experimental part.

In the composites object of the invention, the amounts of calcium titanate in
CT2 phase and in CT5 phase are widely variable: preferably they are present
in similar amounts. In an embodiment of the invention the calcium titanate
is present exclusively in CT2 phase or exclusively in CT5 phase.
The aforementioned calcium titanate in the CT2 and/or CT5 phase
represents per se constitutes a particular embodiment of the present
invention. The limestone used to form the composite is the commercially
available one, preferably in finely divided form, also commercially available
(example source: cava di Tinella (Fasano, Brindisi))
The BET surface area of the composite generally ranges from 1 to 150 m2/g,
with preferred values between 2 and 20 m2/g, e.g. between 5 and 10 m2/g.
The process for obtaining the composites described here constitutes a
further aspect of the invention. It generally comprises reacting limestone and
a precursor of titanium dioxide in a basic solution containing sodium ions.
The reactants can be added into the reactor in indifferent order; preferably
the limestone is contacted first with the basic solution and then with the
precursor. The precursor used is preferably titanyl sulphate. The basic
solution containing sodium ions is preferably an aqueous NaOH solution. In
the process conditions the precursor converts totally into calcium titanate.
Preferably, an amount of precursor is used corresponding to a theoretical
content of Ti02 (i.e. calculated considering a total conversion of the precursor
into Ti02 ) of about 20% by weight with respect to the limestone. The
reaction goes on for a time of between 45 and 90 minutes, at a temperature
ranging from 20 and 80 °C. At the end of the reaction, the resulting solid
product is recovered from the solution, optionally washed, then dried and
calcined. The washing generally takes place with water; it must in any case
be partial, in order not to completely eliminate the sodium residues coming
from the basic solution used. Alternatively, the solid can be completely
washed (or else a basic solution not containing sodium can be used) and
then a sufficient amount of sodium can be introduced, e.g. by dispersing the
solid a suitable aqueous solution having an adequate concentration of
sodium ions. Indeed, it has been observed that in presence of sodium (at
least 0.05% by weight, expressed as Na20 over the dry product), the
precursor of Ti02 used does not convert into Ti02, but it obtains
substantially exclusively calcium titanate; the composite is thus

substantially free from titanium dioxide. By "substantially free from" it is
meant a composite in which the titanium dioxide is absent, or else it is
present in amounts not greater than 2% by weight.
The presence of sodium at the end of the washing can be tested through
methods known in the field, e.g. via flame test, X-ray fluorescence and
atomic absorption, etc. In case it is opted not to wash the reaction solid, the
presence of substantial amounts of sodium in the product (deriving from the
initial basic solution) is in any case ensured and does not need to be tested
analytically.
The calcining preferably takes place at a temperature ranging from 300 and
800°C, e.g. between 450 and 700 °C; particularly effective photocatalytic
composites have been obtained by calcining at about 650°C.
Heat treatments below 525°C are less preferable since they need long times
(over 24 hours) for the formation of the desired calcium titanates. The
reaction speed at temperatures of between 550 and 6506C is high.
Temperatures of over 700°C are preferably to be avoided because they cause
the start of limestone decarbonatation..
A further object of the present invention is the photocatalytic composite
obtained through the process described above.
From the point of view of the elemental composition (as detectable by X-ray
fluorescence and atomic absorption), the composites according to the
invention can be further characterised as follows:

The elemental composition given in the tables refers to the composite as a
whole: such a composite comprises, in addition to calcium titanate,
limestone and residues of the reactants used for the titanate-forming
reaction.. In particular, the analysis confirms the presence of non-negligible
amounts of sodium in the composite, responsible for the complete
conversion of the TIO2 precursor into calcium titanate. Indeed, it has been
observed that composites obtained in a similar way, but carefully washing
the reaction solid until substantially all traces of sodium have been
eliminated (sodium residue below 0.05% by weight, expressed as Na20 over
the dry product), contained substantial amounts of titanium dioxide in
mixture with the calcium titanate: both products derived from the
conversion of the TiOaprecursor ; the group of composites thus obtained has
specific application advantages and is the object of a co-pending application
to the Applicant.
As highlighted by the electron microscopy observations contained in the
experimental part, the calcium titanate in the present composites is in the
form of crystalline grains of a size of about 10-150 microns, closely
connected to limestone grains. There is thus clearly a strong aggregative link
between the photocatalytic portion of the composite (calcium titanate) and
the mineral support component (limestone); within these aggregates, the
calcium titanate crystals in phase CT2 are generally rounded, whereas those
in phase CT5 generally have a characteristic rod shape.
The present invention represents a successful example of composite material
in which the calcium titanate is closely and stably linked to a support

material (limestone) able to be used in the cement field.. The close
interconnection between the photocatalytic and non-photocatalytic parts of
the composite obtains a substantial continuity between absorption sites of
the pollutants and decomposition sites thereof, with the advantage of high
photocatalytic efficiency. Such efficiency has been highlighted by abatement
tests of N-oxides (NOx) and VOC (aromatic hydrocarbons), using the
composite of the invention either as such, or incorporated in bulk in a
cement matrix.
With the present invention a highly integrated multi-phase composite
material has been obtained, free from titanium dioxide, having high
photocatalytic activity, particularly suitable for being incorporated in cement
matrices.
Despite the lack of TiC>2, the "absolute" photocatalytic activity of the
composite (expressed as amount of NO abated) proved unexpectedly similar
to that of equivalent commercial products containing the best known
photocatalyst (anatase titanium dioxide, PC-105, Millenium). The "relative
photocatalytic activity (expressed as ratio between the amount of NO abated
and the total weight of titanium present in the composite) proved to be even
greater than that of similar composites containing the same calcium titanate
and titanium dioxide: there is thus, for the calcium titanate of the invention
and its composites, an intrinsically greater photocatalytic activity than that
of titanium dioxide, the latter up to now considered the photocatalyst of
choice.
A further object of the invention is the use of the photocatalytic composite
described earlier as photocatalytic product as such, or in the preparation of
cements and cement articles of manufacture endowed with photocatalytic
activity. The article of manufacture can contain the composite dispersed in
bulk, or layered on its outer surfaces, as coating: in the latter case the
photocatalytic composite is preferably mixed with suitable tackifiers, used to
promote suitable cohesion between article of manufacture and coating layer.
In any case, the composite is used in amounts such as to obtain a
concentration of composite in bulk preferably ranging from 1% to 15 %,
more preferably between 2% and 10%. The methods for the dispersion in
bulk or for the outer coating are per se widely known in the field in question.

An aspect of the invention thus concerns photocatalytic composition, in
particular of the cementitious type, comprising the composite described
above. The further elements of the cement composition are those commonly
known, in particular: various hydraulic binders, optional aggregates and
additives used in the cement field. The hydraulic binders and the aggregates
(defined for example by standards UNI ENV 197.1 and UNI 8520) are
products widely known in the field. The compositions according to the
invention can be provided in fluid state, or else mixed with water (to form
mortars or concretes, depending upon the granule size of the aggregates
used), or else they can be provided in the corresponding forms free from
water (dry premixes). These compositions are used to form photocatalytic
articles of manufacture through suitable casting in moulds and similar
technologies; the resulting articles of manufacture contain the composite of
the invention dispersed in bulk. Alternatively, they can be used as coating
formulations of pre-existing articles of manufacture, preferably co-
formulated with suitable tackifiers.
The invention is illustrated hereafter not for limiting purposes through the
following examples.
EXPERIMENTAL PART
EXAMPLE 1
Preparation of the composite (STCA02)
280 g of a commercial calcareous filler (origin: cava Tinella di Brindisi) were
stirred, suspended in 700 ml of a NaOH solution (200g/l in distilled water),
and an aqueous solution of 700 ml of TiOS04 (100g/l di Ti02), so as to have
a theoretical Ti02 content equal to about 20% by weight, was dripped. The
powder obtained was filtered and partially washed with distilled water, thus
keeping a part of the sodium deriving from the NaOH in the solid. The
powder was then dried at 105°C in a ventilated oven. Before performing the
calcining heat treatment at 650 °C for 2 hours, the product was broken up
so as to obtain a powder.
EXAMPLE 2
Alternative for the preparation of the composite (STCA02)

280 g of a commercial calcareous filler (origin: cava Tinella di Brindisi) were
stirred, suspended in a 2M aqueous solution of NH4HCO3 (slightly in excess
with respect to the titanyl sulphate), and an aqueous solution of 700 ml of
TiOSOt (100g/l of TiCte), so as to have a theoretical content of TIO2 equal to
about 20% by weight, was dripped. The powder obtained was filtered and
completely washed with distilled water. The powder was then dried at 105°C
in a ventilated oven. The solid product was then again dispersed in an
aqueous solution at a known concentration of NaOH (the concentration is
such as to introduce the desired amount of Na, expressed as Na20, over the
solid), and kept agitated until the solution is completely dry. Before
performing the calcining heat treatment at 650 °C for 2 hours, the product
was broken up so as to obtain a powder.
EXAMPLE 3
Micro-structural characterisation.
The composite STCA 02 obtained in example 1, subjected to diffractometric
analysis (diffractometer BRUKER D8 Advance and CuKa (Acu= 1.545 A)
radiation, proved to be a polyphase mixture consisting of calcite, traces of
perovskite, and calcium titanate in different crystalline phases. In particular,
the diffraction profile showed the presence of a series of peaks not
attributable to known crystalline phases, which can be referred to two
different phases (CT2 and CT5) that proved to be calcium titanate-containing
compounds with ratios of Ca:Ti 1:2 and 1:5 respectively (see Fig. 1). The
peaks attributable to the two phases are of similar intensity, indicating that
they are present in the composite in comparable amounts.
The accurate position of the peaks of the new crystalline phases was
determined through diffractometric analysis of the sample after elimination
of the calcite by treatment in diluted HC1 (1:10) and subsequent drying at
60°C (Fig. 2).
The observed interplanar distances (d) of the two phases are shown in the
following tables, wherein h,k,l indicate the Miller indices, and °26 indicate
the diffraction angle.

Microscope analysis.
In order to better understand the nature of the sample, both the sample as
such and the acid residue were subjected to analysis by transmission
electron microscopy (TEM). The observations allowed to establish that the
sample consisted of a mixture of crystals of a few microns of calcium
carbonate and of crystalline micro-nano aggregates (grains) of calcium
titanate and carbonate having variable size from 50 to 300 nm (see Figs. 3
and 4).
Through microanalysis with EDS detector it has been possible to identify two
families of crystals containing both Ca and Ti, one with a characteristic
rounded shape, the other with an elongated shape (Fig. 5, 6). The
semiquantitative analyses made by focussing the electron beam on different
crystals of the first phase have allowed to establish that the Ca:Ti ratio in
this phase, here referred to as CT2, is about 1:2
High-resolution images were carried out on some crystals of this phase with
the corresponding Fourier transforms, from which it has been possible to
extract information on the cell parameters for the CT2 phase:
Orthorhombic: a=7.1 A, b=5.0 A, c=9.9 A.
The extinction conditions observed are the following:
Okl k+l=2n
hhl no cond (1)
2hhl no cond
hOO h=2n
OkO k=2n (2)

By adding the extinctions (1) and (2) one obtains as possible space group
Pna21 (Herman Mauguin Symbol), corresponding to the space group 33
shown in International Tables of Crystallography, vol. A, "Space Groups
Symmetry", V ed., Kluver Acad. Publ. 2002)
Possible monoclinic distortions can exist and the TEM data obtained cannot
exclude them.
The software used for simultaneously indexing such patterns was QED
(Belletti D., Calestani G., Gemmi M, Migliori A. - QED V 1.0: a software
package for quantitative electron diffraction data treatment
Ultramicroscopy, 81 (2000) pp 57-65).
In light of the information obtained on the cell of this new phase it was
possible to assign some of the peaks not identified in the diffractogram of the
sample STCA06 to the CT2 phase.
The remaining peaks are attributable to a different phase (CT5, see later).
The cell parameters of the CT2 phase have been further refined through
fitting of the calculated diffractometric profile with the real one.
Through microanalyses with EDS detector it has been confirmed that the
family of rounded crystals is conform with CT2 phase, found in the sample of
photocatalytic composite.
Other crystals of characteristic elongated form were found to contain Ca, Ti
and small amounts of Na. This new crystalline phase, characterised by a
Ca:Ti ratio of about 1:5, is referred to here as CT5. Similarly to what was
done for CT2, some high-resolution images were taken, with the
corresponding Fourier transforms from which it has been possible to extract
information on the cell parameters.
The main characteristic of this phase is a periodicity of 17.6 A.
From the simultaneous indexing of such patterns via QED software (Belletti
et al., op.cit.) it has been possible to derive a possible cell for the compound
in question. The cell was orthorhombic C centred:
a=3.8 (10) A, b=12.1 (20) A, c=17.7 (2) A (decimal error)

Possible monoclinic distortions can exist and the TEM data obtained cannot
exclude them.
The extinction conditions observed are:
hkl h+k=2n
hkO h+k=2n
Okl not able to be determined
hOl h,l=2n
hOO h=2n
OkO k=2n
001 l=2n
These extinctions are compatible with the following possible space groups:
type C-c-: Cmc21, C2cm, Cmcm (corresponding to the space group 63, cf.
International Tables of Crystallography, vol. A, "Space Groups Symmetry", V
ed., Kluver Acad. Publ. 2002) in the case of extinction Okl k=2n;
type Ccc-:Ccc2, Cccm in the case of extinction Okl k,l=2n.
The cell parameters of the CT5 phase have been further refined through
fitting of the calculated diffractometric profile with the real one.
EXAMPLE 5
Analysis of specific BET surface and microporosity.
The values measured during the analysis of the new photocatalytic
composite STCA 02 shown in the table show an increase in the specific
surface of the heat treated product (650'C), with respect to the limestone as
such, with an increase in the non-microporous fraction.

By working at different temperatures it is also observed that the surface area
generally tends to decrease as the calcining temperature increases.
EXAMPLE 6
Photocatalytic activity on cement: NOx abatement measurements.
The composite STCA02 was mixed with white cement (Italbianco 52.5 di
Rezzato) so as to obtain photocatalytic cements with percentage by weight of
photocatalyst within the range 2.0 - 8.5%. NOx abatement analyses were
carried out on cement mortars made with normalised sand CEN (according
to UNI 196-1) by preparing tests in Petri dishes of diameter 8 cm and surface
of about 60 cm2. The results obtained show an excellent behaviour of such
cements, comparable to that of cement containing commercial anatase (Fig.
7).
The abatement values measured on the mortars CEN containing the
composite STCA02 at different concentrations on cement have shown very
good NOx abatement values already at percentages of around 2.5% by
weight. (See Fig. 7)
The photocatalytic activity tends to increase as the calcining temperature of
the sample increases.
EXAMPLE 7
Photocatalytic activity on cement: VOC abatement measurements.
The evaluation of the abatement capability of aromatic hydrocarbons was
carried out using the pure photocatalytic products (not mixed with cement)

under UV radiation. Ethylbenzene was used as organic substance, using a
flow apparatus typical of tests on catalysts (oxidation of ethylbenzene in air).
In this way the intrinsic activity of the material is determined, disregarding
the diffusive phenomena. The results obtained show an excellent level of
5 abatement activity of the product. It is greater than the best commercial Ti02
(Fig. 8).

CLAIMS
1. Photocatalytic composite substantially free from titanium dioxide,
comprising limestone, and calcium titanate in the crystalline phases CT2
and/or CT5 characterised by the following diffraction peaks:
CT2: (002) d=4,959; (210-202)d=2,890; (013) d=2,762 and (310-
122)d=2,138;
CT5: (002) d=8,845; (023) d=4,217; (110) d=3,611 and (006)
d=2,948, wherein the calcivm titapote inCT2 phase has empiriesl formulaCaTi2O5,
and tha calcivm titanate in CTS phase has ompirical formulaCaTi5O11,
2. Composite according to claim 1, wherein said peaks of the CT2 phase
are indexed with an orthorhombic cell having the following reticular
parameters: a=7.1 A, b=5.0 A, c=9.9 A.
3. Composite according to claim 1, wherein said peaks of the CT5 phase
are indexed with an orthorhombic cell having the following reticular
parameters: a=3.8 A, b=12.1 A, c=17.7 A.
4. Composite according to claims 1-3 wherein the CT2 phase is present
in amount equal or similar to the CT5 phase.
5. Composite according to claims 1-4 having specific BET surface
ranging from 1 to 150 m2/g.
6. Composite according to claim 5, having specific BET surface ranging
from 2 to 20 m2/g.
7. Composite according to claim 6, having specific BET surface ranging
from 5 to 10 m2/g.
8. Calcium titanate with high photocatalytic activity, characterised by the
presence of the crystalline phases CT2 and/or CT5, as described in claims 1-

9. Process to obtain the composite described in claims 1-7, comprising reacting
limestone and a precursor of titanium dioxide in presence of a basic solution,
recovering the solid product thus obtained, optionally washing it, then drying
and calcining it wherein:
(a) said basic solution contains sodium ions, and said washing is performed in a
way not totally eliminating the sodium present,
(a) or said basic solution contains sodium ions, said washing totally eliminates
the sodium present, and the product to be calcined is supplemented with a
sodium-containing compound
or said basic solution does not contain sodium ions and said optionally
washed, dried solid product is added with a sodium containing compound,and
then calcined.
10. Process according to claim 9, wherein the product to be calcined
contains a residual amount of sodium of at least 0.05% by weight.
11. Process according to claim 9, wherein the precursor is titanyl
sulphate, la basic solution contains NaOH, and the solid product is calcined
at a temperature ranging from 300 to 8000C.
Process according to claim 11, wherein the solid product is calcined at
a temperature ranging from 450 to 700°C
13.. Use of a composite as described in claims 1-7, in preparing an article
of manufacture having photocatalytic activity.
14. Use according to claim 13, wherein the article of manufacture contains
the composite dispersed in bulk.
15. Use according to claim 13, wherein the article of manufacture contains
the composite layered on at least part of its external surface, as a coating
element.

16. Cement composition comprising the photocatalytic composite
described in claims 1-7, water, a hydraulic binder, and optionally
aggregates.
17. Dry premix comprising the photocatalytic composite described in
claims 1-7, a ft hydraulic binder, and optionally aggregates.
Photocatalytic article of manufacture comprising, dispersed in bulk or

New photocatalytic product comprising compounds of titanium integrated with limestone. The product is obtained
by reacting limestone with a suitable precursor of titanium dioxide in a basic solution, recovering the product in particular condi-
tions, drying it and calcining it. By operating in presence of sodium, a composite is obtained substantially free from titanium dioxide, containing limestone and calcium titanate. The composite thus obtained, used as such or in mixture with other components,
has shown an unexpectedly high photocatalytic activity.

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Patent Number

278994

Indian Patent Application Number

460/KOLNP/2011

PG Journal Number

02/2017

Publication Date

13-Jan-2017

Grant Date

06-Jan-2017

Date of Filing

31-Jan-2011

Name of Patentee

ITALCEMENTI S.P.A.

Applicant Address

VIA GABRIELE CAMOZZI, 124, I-24121 BERGAMO, ITALY

Inventors:

#	Inventor's Name	Inventor's Address
1	BORSA, MASSIMO	VIA GUGLIELMO MATTIOLI 59, I-24129 BERGAMO, ITALY
2	ANCORA, RENATO	C/O ITALCEMENTI S.P.A., VIA GABRIELE CAMOZZI, 124, I-24121 BERGAMO, ITALY
3	ILER MARCHI, MAURIZIO	VIA ALDO MORO, 6, I-20066 MELZO (MILANO), ITALY

PCT International Classification Number

B01J 35/00

PCT International Application Number

PCT/EP2009/005572

PCT International Filing date

2009-07-31

PCT Conventions:

#	PCT Application Number	Date of Convention	Priority Country
1	MI2008A001447	2008-08-01	Italy