Sterile Clay Pozzolans from Phosphate Mining

In the state of Minas Gerais, there is a large concentration of mining activities. The Meso-region of Alto Parnaíba and Triângulo Mineiro, has three mining companies: two phosphate extractors and a pyrochlore extractor. Phosphates have major applications in fertilizer production, whereas pyrochlore is utilized for the production of metallic niobium and its derivatives. Micro-region of Araxá has two mining complexes: Barreiro complex and Tapira complex. The Barreiro complex is located in the Araxá-MG municipality and currently has two mining companies. Tapira Mining Complex (TMC) is located in Tapira-MG municipality, which is about 35 km from Araxá city. According to Santos et al.1, the activities of the complex occupy an area of approximately 78 × 106 m2 with an annual production of concentrate (in terms of P2O5) around 1.6 × 106 tonnes / year. With the growth in fertilizers, the proportionate increase in production demand has increased environmental liabilities represented by materials considered waste or sterile, which are currently packed in sludge containment dams or in huge dams that increasingly require large areas for disposal. The Tapira Mining Complex industrial process generates waste at around 85% of the feed mass in the concentration plant1. Given the importance of cement to world development, concrete is the second most consumed product in the world and is second only to water. Portland cement-based products are known to have great potential for promoting economically viable solutions for the immobilization of industrial waste, thus contributing to the sustainable development of industrial activities. Therefore, this work will contribute to the study of an industrial waste, primarily consisting of clay. This work will investigate the possibility that these clays, when thermally activated, possess considerable pozzolanic potential to be used as raw materials to partially replace Portland cement.


Introduction
In the state of Minas Gerais, there is a large concentration of mining activities.The Meso-region of Alto Parnaíba and Triângulo Mineiro, has three mining companies: two phosphate extractors and a pyrochlore extractor.Phosphates have major applications in fertilizer production, whereas pyrochlore is utilized for the production of metallic niobium and its derivatives.
Micro-region of Araxá has two mining complexes: Barreiro complex and Tapira complex.The Barreiro complex is located in the Araxá-MG municipality and currently has two mining companies.Tapira Mining Complex (TMC) is located in Tapira-MG municipality, which is about 35 km from Araxá city.According to Santos et al. 1 , the activities of the complex occupy an area of approximately 78 × 10 6 m 2 with an annual production of concentrate (in terms of P 2 O 5 ) around 1.6 × 10 6 tonnes / year.
With the growth in fertilizers, the proportionate increase in production demand has increased environmental liabilities represented by materials considered waste or sterile, which are currently packed in sludge containment dams or in huge dams that increasingly require large areas for disposal.The Tapira Mining Complex industrial process generates waste at around 85% of the feed mass in the concentration plant 1 .
Given the importance of cement to world development, concrete is the second most consumed product in the world and is second only to water.Portland cement-based products are known to have great potential for promoting economically viable solutions for the immobilization of industrial waste, thus contributing to the sustainable development of industrial activities.
Therefore, this work will contribute to the study of an industrial waste, primarily consisting of clay.This work will investigate the possibility that these clays, when thermally activated, possess considerable pozzolanic potential to be used as raw materials to partially replace Portland cement.

Materials
The research material covered in this study was the sterile material generated in TMC.By analysing the process of this mining complex, which comprises an area of 35 km 2 with a large coverage usually with an average depth of 30 m predominantly of clay soil corresponding to sterile area, with different physical and textural characteristics, presenting a red and yellowish tint granular appearance 1 .The clays were collected at three different levels in the concentrated phosphatic extraction mine (TMC).The collection points were identified with the aid of a GPS (GARMIN -GPS 12) and are listed in   For manufacturing the cement composites, natural standardized sand was used as the fine aggregate.

Methods
The sterile clay was naturally collected in the TMC mine and stored in plastic bags containing approximately 50 kg of each material sample.In Figure 1, it is possible to observe the surface layers of the TMC mine.The reddish soil is called red clay (RC), and the yellow soil below the red clay is known as yellow clay (YC).Between the sterile zone (yellow-red soil) and the mineralization zone (grey soil), intermediate soil can be observed, which is known as intermediate clay (IC) in this work.
After collecting the material, the clay was dried and homogenized in laboratory.The material was divided into four parts to obtain a sufficient amount of the sample.The samples were prepared for the characterization tests, and the material was characterized through moisture tests, by particle size, and by determining the amount of liquid and plasticity.Then, the material underwent processing by grinding and screening through a sieve with an aperture of 0.075 mm.
The calcination was performed in a muffle-type electric oven with a controlled temperature up to 1200 °C.The heating chamber had internal dimensions of 200 × 150 × 150 mm 3 with 3.5-kW power and a 220-V power supply.The material was placed in porcelain crucibles and subjected to calcination temperature conditions at three different temperatures and at two different time intervals, as shown in Table 2.All tests occurred at a heating rate of 25 °C/min.
After processing, the materials were physic-chemically and morphologically characterized.Physical characterization of the processed clays was performed using specific mass tests and loss on ignition.Chemical characterization and the degree of crystallinity were determined by X-ray fluorescence spectroscopy testing (EDX) and X-ray diffraction (XRD).The morphology of the clays was analysed macroscopically using digital camera photographs and microscopically using scanning electron microscopy (SEM).The thermal behaviour of the processed clays was analysed through differential thermal analysis (DTA) and thermogravimetry (TGA) tests.
After characterizing the clays, their pozzolanic activity was assessed using electrical conductivity in saturated calcium hydroxide 2 , and the pozzolanic activity index with cement was determined according to NBR 5752 3 methods.

Results
Table 3 presents the results of the clay characterization.The moisture content of the clays may be associated with the hygroscopic moisture, acquired at different depths at the fresh sample collection points.This could explain why IC has the highest moisture in ambient conditions, given its deeper location in the excavation, which is close to the groundwater.On the other hand, RC has lower moisture content due to its location in more superficial layers.Correlating the moisture content results with the specific mass and the percentage of particles larger than 38 μm, the moisture in the clays showed a different behaviour than expected because dense materials with smaller particle sizes commonly have higher levels of humidity.
As to specific masses, one can assume with respect to the values found, these being proportional to particle sizes.In other words, smaller grain diameters have lower specific mass.Thus, in order of increasing specific mass, we find RC (2.727) < YC (2.871) < IC (3.046) in g/cm 3 .Regarding the fineness of the particles passing through sieve 0.038 (#400), we found that the percentage retained had the same order of magnitude of RC (4.4) < YC (8.6) < IC (16.25).
Of the tested clays, the different levels of loss to fire are primarily due to the loss of structurally bound water in the form of hydroxyl groups (OH) and due to the volatilization of organic matter.In the case of RC, the volatilization of organic matter presented a more significant number.
The results shown in Table 3 indicate that the YC-IC clays can be classified as moderately plastic (7 < PI < 15), while RC is considered to be highly plastic clay.It is noteworthy that all clays tested meet the established maximum liquid limit of 45% and exceed the established maximum of 18% for the plasticity index.The result of the retraction test showed no transverse cracks in the central portion of the sample that exceeded the threshold of 2.0 cm.The observed cracks were less than 1.0 cm, which confirms the absence of expansive clay, and agrees with plasticity results 4 .
Table 4 shows the results obtained by chemical analysis of the clays using X-ray fluorescence, which is expressed in terms of pure elements.The main constituent elements of the studied clays are iron (Fe), with percentages ranging from 39.78 to 45.44%, aluminium (Al), varying from 10.05 to 37.77% and silicon (Si), varying from 13.03 to 21.21%.These results confirm the possibility of these clays presenting some degree of pozzolanicity.Studies report that alumina and iron oxide are the predominant components of argillaceous materials, but the relative amounts of SiO 2 and Na 2 O (or NaOH) are also relevant 5 .In low levels, the clays contain barium (Ba), calcium (Ca), phosphorus (P), potassium (K), and titanium (Ti).In addition, the results showed traces of zinc (Zn), manganese (Mn), zirconium (Zr), copper (Cu), niobium (Nb), strontium (Sr), vanadium (V), yttrium (Y), and cerium (Ce).
When compared with other clays, YC has a high Si content, while RC has higher aluminium content, which is an indicative of the existence of a higher percentage of clay minerals.High Fe levels in clays are sufficient to ensure the reddish colour after burn off.The ratio of silica to alumina is an indicative parameter of the amount of present clay minerals.Thus, a lower silica/alumina quotient indicates a higher content of clay minerals present and greater plasticity.These results could justify the higher plasticity index of RC clay as well as the occurrence of a high iron content, which is responsible for the red colour before and after burn off.
The degree of crystallinity was qualitatively evaluated by X-ray diffraction.In Figure 2, the X-ray diffraction results of the clays are presented.In the sample diffractograms, the presence of several peaks of crystalline materials is observed, such as kaolinite, goethite, anatase, apatite, and gibbsite.These results are consistent with those reported in the application study of red mud residue from bauxite processing for use as raw material in clay-based products 6 .The spectra are consistent with the results presented in the X-ray Fluorescence Spectroscopy test that shows the prevalence of elements such as Al, Fe, Si, Ti, and P.
In the YC XRD data, we observe kaolinite, goethite, and apatite with sharp, intense reflections at angles of 12.26, 21.34, and 36.9 (2θ), respectively, and we observe distinct, medium-intensity reflections at 20.1 (2θ) for kaolinite and 30.26 (2θ) for apatite.The IC XRD data also features kaolinite, goethite, and anatase with sharp, high intensity reflections at angles of 12.34, 21.24, and 25.36 (2θ), respectively.Regarding the RC XRD data, gibbsite stands out with a sharp, high intensity peak at 18.27 (2θ).Other characteristics of kaolinite are observed with lower intensity at angles of 12.26, 20.25, and 24.78 (2θ), and we find a low intensity goethite reflection at 21.4 (2θ).
Table 5 shows the measured weight loss after the calcination process.In this process, 20-g samples were passed through a sieve with an opening of 0.075 mm (#200) in established temperature and time conditions.It is observed that RC showed the highest percentage of mass loss (14-15.3%),while YC lost around 6.6-7.3%, and IC showed the smallest loss of 2.45-3.15%.These values are directly correlated to loss values during burn off.The calcined samples were used to assess the level of pozzolanic activity through electrical conductivity in solution.The results of the measurements are presented in Table 4.By observing the difference in conductivity, most of the calcined clays have a high level of activity with calcium hydroxide solution, indicating that these clays can be considered to have a high pozzolanic activity index; however, IC.840 clays (60-120) are considered moderate.Figure 3 shows the results of the pozzolanic activity index test using the compressive strength of proof-bodies designed with the three calcined clays at temperatures of 680, 760, and 840 °C and without calcining (WC).In some moulded proof-bodies with the addition of calcined clay, the compressive strength within the physical requirements parameters established in NBR 12653 7 was equivalent to 75% of compressive strength (red line) attained by the reference mortar without the addition of calcined clay.Thus, these clays can be considered to be pozzolanic materials in accordance with the NBR 12653 7 standard.For glass powder usage in partial replacement of the fine aggregate in cement composites, the results show that the increase in the compressive strength is a characteristic of materials with a good pozzolanic index 8 .In particular, red clay calcined at 680 to 840 °C presented pozzolanic behaviour in the pozzolanic activity index test.Moreover, intermediate clay   calcined at 760 °C presented pozzolanic behaviour in the pozzolanic activity index test.

Conclusions
This paper shows that the residual clay from the phosphate mining process has chemical and physical characteristics similar to the characteristics of known pozzolans.Calcined residual clays presented as pozzolanic materials using the electrical conductivity method in a saturated solution of calcium hydroxide, and the calcination process increases the pozzolanic activity index of cement.According to the tests performed, yellow clay presented as a effective pozzolan.

Figure 2 .
Figure 2. The X-ray diffraction data for the three types of clay.

Sterile Clay Pozzolans from Phosphate Mining José Afonso de Matos Neto a , Domingos Sávio de Resende a , João Trajano da Silva Neto b , Antônio Maria Claret de Gouveia b , Maria Teresa Paulino de Aguilar c , Augusto Cesar da Silva Bezerra a *
. The binder used was Portland cement with class 32-MPa slag compound (CPII E 32).Portland cement was selected because its composition does not present pozzolanic additions

Table 1 .
Geographic location of samples.

Table 4 .
EDX analysis of the clay chemical composition.

Table 5 .
Mass loss and pozzolanic activity index.