I. Overview
Using associated cell outside a microorganism and biopolymers galena selective separation of binary mixtures has been reported from galena and sphalerite or pyrite. In this study, Paenibacillus poly-myxa (B. polymyxa, abbreviated as P. polymyxa) is a Gram-positive bacterium, neutrophilic, surrounded by flagellated heterotrophic organisms, and survives in many deposits. In addition to the main biopolymers such as exopolysaccharides and proteins, the main products of P. polymyxa metabolism contain organic acids such as oxalic acid, formic acid and acetic acid.
In addition to induction of copper ore sorting yellow galena and microbial bio-sourced polymer study, the effects on the organisms themselves understand the sorting process is required. The affinity for bacterial effects and the adjustment of biopolymer's attachment behavior have been studied. However, there is still a need to understand the biopolymers present at the mineral and bacterial interfaces and their role in the attachment process. This article will determine the affinity of chalcopyrite and galena for extracellular biopolymers such as extracellular proteins (EBP) and extracellular polysaccharides (ECP). The relationship between the surface hydrophobicity associated with floatability and the adsorption of biopharmaceuticals was also investigated.
Second, raw materials and test methods
(a) minerals
Samples were collected from Almin-Rock, Indscer Fabriks, India, and hand-selected high purity chalcopyrite and galena samples. Chemical analysis, X-ray analysis, and mineralogical analysis are used to determine the purity of the sample. The purity of chalcopyrite and galena samples was 99.8% and 99.7%, respectively. The above samples were finely ground using a porcelain ball mill and sieved into -105 + 74 μm and -37 μm pellets. Further ball milling was carried out at -37 μm particle size, and a -5 μm particle size was obtained by sedimentation. The samples were subjected to particle size analysis using a Malvern Zetasizer particle size analyzer with an average particle size of 3 to 5 μm. This fraction is used for adsorption and flocculation tests. The specific surface area of ​​the sample was determined using a BET nitrogen adsorption method. The chalcopyrite obtained by the above method had a specific surface area of ​​1.93 m 2 /g. The galena is 1.939 m 3 /g. The -105+74 μm fraction was used for flotation studies.
(two) bacterial culture
The Institute was obtained from the National Industrial Microbial Specimen Laboratory in the National Chemical Laboratory of India using the P. polymyxa strain (numbered NCIM2639). The culture was carried out in the laboratory using Bromfield medium. Potassium nitrate was used to maintain ionic strength, and nitric acid and potassium hydroxide were used as pH adjusters. All reagents in the test were of analytical grade. Distillation deionized water with a specific conductivity <1.5 μS/m was used in the test. 10 mL of the pure strain was injected into Bromfield medium for culture. The culture was carried out in a Remi incubator at 30 ° C and a rotational speed of 340 r/min. The pH change was measured every 30 min using a Systronics digital pH meter.
(3) Preparation of cell-free metabolites
Bacteria (48 h) grown at 4 °C were centrifuged for 15 min in a Sorvall RC-5B centrifuge (10000 r/min). The supernatant was decanted and filtered through sterile Millipore (pore size o. 2 μm) to remove all insoluble materials while removing bacterial cells. The cell spheres were washed with a second distillation of deionized water and then centrifuged. The above procedure was repeated twice to obtain a pure cell sphere.
(4) Separating proteins from metabolites
After 48 h incubation, 1 LP. polymyxa broth was centrifuged. The supernatant was filtered through a Millipore (pore size 0.2 μm) filter paper. Under the constant shaking at 4 ° C, the analytically pure ultrafine granular sulfuric acid was slowly added at a concentration of 90% (600.16 g/L). The solution was cooled at 4 ° C for 12 h. The protein precipitate was dissolved in 1 mol/L of a solution of tris (hydroxymethyl) aminomethane hydrochloride buffer (pH 7). Dialysis was carried out at 4 ° C for 18 h. The precipitate produced during dialysis was removed by centrifugation. The supernatant was frozen, weighed and stored at 4 °C.
(5) Separation of extracellular polysaccharide (ECP) from metabolites
1 L was centrifuged to remove the cells for 48 h. The supernatant containing ECP was filtered through a sterile Millipore membrane. It was then lyophilized to 200 mL under vacuum at -80 °C using a Virtis Freezemobile 12EL freezer. The dehydrated solid matter was dissolved in 10 mL of distilled millipore high purity water at room temperature and cooled below 10 °C. 20 mL of secondary distilled ethanol was added to precipitate ECP and it was separated from other bacteria-containing supernatants. The above ethanol precipitation was repeated two to three times to further purify the polysaccharide. The polysaccharide solution was dialyzed against double distilled water. Prior to dialysis, the dialysis tubing was boiled in a water bath of 0.01 mol/L EDTA and 2% sodium bicarbonate solution for 10-15 min. After dialysis, the ECP was stored at low temperature (4 ° C). The purity of ECP is determined by the phenol-sulfuric acid method.
(6) Adsorption test
1 g of the mineral sample was added to a 100 mL 10 -3 mol/L KNO 3 solution of known pH and EBP concentration in a 250 mL Erlenmeyer flask. The Remi oscillator was used to shake for 15 min at 30 ° C and 250 r/min. After equilibration, the pH of the slurry was measured again. It was then centrifuged at 200 r/min for 5 min to remove the mineral particles to which EBP adhered. The supernatant containing EBP was further filtered with Whatman No. 42 filter paper, and the concentration of EBP remaining in the supernatant was measured. A similar method was used to study the adsorption behavior of bacterial cells and ECP on mineral particles.
(7) Flocculation research
In the flocculation study, 1 g of the mineral sample was dispersed in 100 mL of twice-distilled deionized water in a graduated cylinder of 100 mL volume. The amount of the stopper was turned upside down and inverted 10 times, and then allowed to stand for 2 minutes. Using a pipette, remove 90 ml of the supernatant and place it in a beaker. The supernatant was filtered, dried and weighed to obtain a mass fraction of solid particle dispersion. The test was carried out with pH and time as variables. A flocculation test was carried out in a graduated cylinder containing 1 g of 50 mL of slurry and 50 mL of protein supernatant or a known concentration of ECP plus a 100 mL stopper. The pH of the pulp and protein was adjusted to the same value before mixing. The selective flocculation test was carried out in a binary mixture of 1:1 by weight of galena and chalcopyrite. Containing 0.5 g of 50 ml, the added slurry is added to the graduated cylinder with 50 mL of the added bacterial supernatant. Prior to mixing, the slurry and cell supernatant were adjusted to the same pH. The cylinder with the stopper was inverted 10 times and allowed to stand for 2 minutes (de-slurry stage). The dispersed and settled products were analyzed by ICP spectroscopy to obtain the mass fraction of each mineral in both products.
(8) Microflotation test
At neutral pH, 1 g of mineral was mixed with 100 mL of secondary distilled deionized water containing known concentrations of EBP, ECP or bacterial cells in an Erlenmeyer flask. The flask was incubated for 30 min in a 250 r/min shaker. After the action, the supernatant is removed and the mineral particles are separated. The mineral particles sinking at the bottom were filtered through Whatman No. 42 filter paper and washed with a second distillation of deionized water to remove EBP, ECP or cells adhering to the mineral surface. Transfer the conditioned minerals to a modified Harrison flotation tube. Transfer 40 mL of /min nitrogen for 3 min. The settled and floated portions were separated and dried and weighed separately. Potassium isopropyl xanthate (PIPX) was used as a collector to study flotation behavior. At the same time, the effect of the order of addition of collectors and bacterial reagents on flotation was studied. 1 g of a mineral having a degree of -105 + 74 μm (1:1 weight ratio) was suspended in a 200 mL addition solution. Prior to flotation, the mineral mixture acts with different bacteria. The mineral mixed sample was mixed with a solution of known pH for 15-20 min with a magnetic stirrer. Then a flotation test was conducted. The floated minerals were measured by ICP and the recovery was calculated.
(9) SEM analysis
Bacterial cells were obtained after centrifugation at 10,000 r/min for 15 min. The cell spheres were resuspended in secondary distilled deionized water. Wash the mineral particles twice with water through nitrogen. 0.5 g of mineral was suspended in 50 mL of water (NW) containing nitrogen. The mineral particles obtained above are interacted with a known number of cells. It was applied in an Erlenmeyer flask and then transferred to an Eppendorf tube and centrifuged at 5000 r/min. Add 5% glutaraldehyde, just enough to immerse the mineral sample, stir at 100 r/min for 2 h, then stir with 0.5% glutaraldehyde for another 2 h. The mineral sample was then adjusted with 35% ethanol. Remove 0.5 mL of the extract with a micropipette, take a drop onto the covered slide, dry it in the dry machine for 15 min, then add a drop (50%) of ethanol. Dry for 15min. The above procedure was then repeated with 70% and 95% ethanol. After complete dry operation, the drying was carried out sequentially with acetone at a concentration of 35%, 50%, 70% and 95%. Store the coverslip in a desiccator until an SEM test (not to exceed 12 h).
Third, the results and discussion
(1) Adsorption research
Firstly, the relationship between the adsorption behavior of BBS and ECP on the surface of galena and chalcopyrite and the change of action time and pH was established. The results are shown in Figures 1 and 2. Figure 1 is a scanning electron micrograph of the adhesion of bacterial cells to chalcopyrite and galena. It can be seen from the figure that the affinity of bacterial cells for both minerals is relatively large. The adsorption kinetics curves of bacterial cells were obtained by measuring the change of adsorption density of different components on the mineral surface with time. The adsorption behavior was observed with time at 10 -3 mol/L KNO 3 and pH 6.5-7. The cell concentration was 4 x 109 cells/mL before adsorption. Figure 2, a shows that the adsorption density of bacterial cells on chalcopyrite is 1.5 x 109 cells/m 2 after 15 min of action, and 1 x 109 cells/m 2 on galena. This indicates that the adsorption of bacterial cells on minerals is not selective. The literature indicates that the cell wall contains polysaccharides and proteins. Therefore, the adsorption behavior of EBP was investigated at an initial EBP concentration of 4 mg/g mineral. Figure 2, a shows that the adsorption density of EBP on chalcopyrite is 3 mg/m 2 after 15 min, while galena is less than 1 mg/m 2 . The adsorption behavior of ECP was also studied at an initial concentration of EPC of 10 mg/g. Figure 2, a shows that after 15 min of action, more than 9 mg/m 2 ECP is adsorbed on chalcopyrite, while the adsorption on galena is less than 8 mg/m 2 . After 15 minutes of action with the two minerals, the ECP is saturated on the mineral surface. However, the amount of adsorption of EBP and ECP on chalcopyrite and galena is not as large as the adsorption of bacterial cells on the surface of these two minerals.
Desliming section number (3 minutes each) | Galena removal (cumulative) /% at different pH | |||
6.5~7 | 8.5~9 | |||
cell | EBP | cell | EBP | |
1 2 3 4 5 | 22.6 41.8 61.8 68.0 71.4 | 25.6 49.7 69.9 81.2 92.3 | 31.2 56.7 62.3 69.8 70.2 | 33.0 45.6 70.2 85.1 89.7 |
Desliming section number (2 min per segment) | Chalcopyrite removal rate at different pH (cumulative) /% | |
6.5~7 | 8~8.5 | |
1 2 3 4 5 | 40.1 62.3 71.9 82.3 87.2 | 35.0 59.7 68.7 79.6 81.0 |
Test conditions | Cell/biological Reagent concentration | PIPX concentration /mol·L -1 | Chalcopyrite Recovery rate/% | Galena Recovery rate/% |
First interact with cells and then treated with PIPX | 2 × 10 9 cells / mL | 1×10 -3 | 49.9 | 44 |
First with the fine package, then with PIPX | 5×10 -4 | 44.4 | 37.2 | |
First with PIPX, then cell treatment | 2 × 10 9 cells / mL | 1×10 -3 | 48 | 47.9 |
First with PIPX, then cell treatment | 5×10 -4 | 39.2 | 38.8 | |
First with EBP, then with PIPX | 50mg/g | 5×10 -4 | 29.1 | 81.4 |
First with EBP, then with PIPX | 100mg/g | 5×10 -4 | 49.6 | 14.1 |
The main conclusions can be obtained from the results of this test.
(a) Paenibacillus polymyxa cells can be strongly adsorbed on the surface of chalcopyrite and galena.
(b) However, bacterial extracellular products, such as biological proteins and exopolysaccharides, adsorb more on chalcopyrite than galena.
(3) The degree of flocculation of chalcopyrite and galena is enhanced after the action of bacteria. Promotes chalcopyrite flocculation after interaction with biological proteins, whereas exopolysaccharide enhances flocculation of galena.
(d) When the pH is higher than 6, the biological protein enhances the flotation of galena.
(v) At natural pH, galena and chalcopyrite can be effectively separated by biologically induced flocculation by controlling the regulation of biological proteins and exopolysaccharides. Similarly, first action with biological proteins enhances selective flotation of galena from chalcopyrite.
Ultrasonic Pest Repellent,Ultrasonic Animal Repeller,,Solar Animal Repeller,Environmentally Solar Pest Repeller
SHAOXING SUNSHINE ELECTRONIC CO.,LTD , https://www.ultralitelamp.com