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X ray fluorescence

Manufactured by Bruker
Sourced in Switzerland

X-ray fluorescence (XRF) is an analytical technique that uses X-rays to determine the elemental composition of materials. It measures the fluorescent (or secondary) X-rays emitted from a sample when it is exposed to primary X-rays. The energies of the fluorescent X-rays are characteristic of the elements present in the sample, allowing for their identification and quantification.

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4 protocols using x ray fluorescence

1

Phosphogypsum Aggregate Cemented Backfill Formulation

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PG was collected from a backfill plant in Guizhou, China. Considering that the pH value of PG is in the range of 1–7, three batches of PG with pH values of 1.68, 4.15 and 6.75 (measured by mixing PG and deionized water in a 1:1 ratio) were collected in this study. PG was used as an aggregate for cemented backfill. A composite cementitious agent (CCA; prepared with phosphorous slag, fly ash cement clinker and slaked lime [36 ]), 32.5R composite Portland cement (CPC) and S95 ground granulated blast furnace slag (GGBFS) were used as binders in this study. Figure 2 and Table 1 show the particle size distribution and physical properties of the raw materials, respectively, and indicate that the three batches of PG were coarser than the binders. In particular, GGBFS had the finest particle size. Table 2 and Figure 3 show the main chemical components (measured using X-ray fluorescence; Bruker, Billerica, MA, USA) and crystal phases (measured using advance D8 X-ray automatic diffractometer; Bruker, Billerica, MA, USA) of the PG samples, respectively. The results indicated that the main component of PG was gypsum. In addition, it was observed that the PG sample with a low pH value contained more P2O5 and F.
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2

Characterization of Phosphogypsum and Composite Binder

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This study evaluated representative samples of PG and composite binder in Guizhou, China. The binder is composed of yellow phosphorous slag: fly ash: cement clinker in 4:1:1, and 16–20% lime of the yellow phosphorous slag mass ratio is added. The main chemical compositions (measured by X-ray fluorescence; Bruker, Switzerland) and physical properties (measured by a particle size analyzer; Malvern Instruments, UK)of PG with different pH values were investigated through the toxicity leaching test, as listed in Table 1.

Impurity concentrations and physical properties of PG and binder.

Impurity concentrationRaw PGBinder
PG-1PG-2PG-3PG-4PG-5
pH1.751.992.633.524.9913.16
PO43− (mg/L)484040001510252200.04
F (mg/L)1641110352150918216
SO42− (mg/L)10,88510,042441923131359487
TDS (ppt)7.893.552.791.630.734.91
Physical property
D10 (µm)13.5611.9411.9410.6115.616.02
D30 (µm)42.7929.1833.1536.1037.7613.73
D60 (µm)92.0555.2481.0267.0881.3130.18
Cu = D60/D106.794.636.794.045.215.01
Cc = D302/(D60*D10)1.471.291.141.171.121.04
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3

Phosphate Tailings as Sustainable Aggregate

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Phosphate tailings (PT) were gathered from a phosphate mine’s (Guiyang, China) tailings pond and utilized as an aggregate. The main phase compositions of PT are dolomite and quartz. Fly ash (FA, collected from a powerplant in Guiyang, China) and 42.5 ordinary Portland cement (OPC) were used as binder. Based on the Chinese standard GB/T 1596-2017, the strength activity index (A = (R/R0) × 100, where A is the strength activity index, R0 is the UCS of hardened type 42.5 ordinary Portland cement, and R is the UCS of the hardened mixture of fly ash and type 42.5 ordinary Portland cement in a 3:7 ratio) of fly ash was more than 70% after 28 days.The particle size distribution of PT (measured by a particle size analyzer, Malvern, UK) is shown in Figure 1, and the components of PT (measured by X-ray fluorescence, Bruker, Switzerland) are listed in Table 1.
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4

Characterization of Loess Plateau Soil for Geopolymer Applications

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In this work, the PS used was obtained from Loess Plateau in Erdos, Inner Mongolia, China. The features of PS area and PS are shown in Figure 10. The particle size distributions of PS shown in Figure 11 were determined by using laser diffraction (Mastersizer 2000, Malvern Instruments, International Joint Research Lab for Eco-building Materials and Engineering of Henan, Henan, China). After drying the wet samples at 105 °C for 24 h, refined PS was obtained by pulverization. The mineral and chemical compositions of PS were determined by X-ray diffraction (XRD) and X-ray fluorescence (XRF) techniques (Bruker, Guangzhou, China), respectively. The detailed chemical compositions are shown in Table 1. The modifier solutions were prepared by dissolving KCl, NaCl, NH4Cl, LiCl, MgCl2,CaCl2, CuCl2, BaCl2, AlCl3 and FeCl3 pellets (99% purity quotient, Tianjin Kemiou Chemical Reagent Co., Ltd., Tianjin, China) in distilled water to a certain concentration (Table 2).
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