Pseudomonas aeruginosa being tolerant to zinc ion toxicity and application thereof
A Pseudomonas aeruginosa, zinc ion technology, applied in bacteria, microorganism-based methods, biological water/sewage treatment, etc., can solve problems affecting the quality of effluent from urban sewage treatment systems, and achieve huge economic and environmental benefits. Efficient removal, cost savings in equipment and investment
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Embodiment 1
[0024] Example 1. Utilize scanning electron microscope to observe the apparent morphology of Pseudomonas aeruginosa in the presence of zinc ions
[0025] The high-efficiency aerobic denitrification strain used in this experiment is Pseudomonas aeruginosa, which was isolated from the leachate treatment system of the landfill site.
[0026] Inoculate Pseudomonas aeruginosa into 1L of LB medium (containing 5g of NaCl, 10g of tryptone, and 5g of yeast extract per liter) to prevent the invasion of miscellaneous bacteria and maintain the growth vigor of the bacteria for enrichment nourish. Centrifuge the cultured bacterial liquid, wash three times with 0.5% NaCl, and make the optical density OD 600 For 1-2 bacterial suspensions. Then inoculate the bacterial suspension in the LB medium containing 0, 10, 50, 100mg / L Zn(II) according to the inoculum amount of 10%, and take samples after 8h and centrifuge at 8000rpm and 4°C for 5min to remove the supernatant solution and washed twice...
Embodiment 2
[0028] Example 2. The aerobic denitrification characteristics of Pseudomonas aeruginosa in the presence of 10mg / L Zn(II)
[0029] The denitrification performance test medium (BM) formula is per liter of water: 8.45g CH 3 COONa, 0.63g NH 4 Cl, 0.61g NaNO 3 ,1.76g K 2 HPO 4 ·3H 2 O, 0.20g MgSO 4 ·7H 2 O, 0.02g CaCl 2 ,0.005g FeSO 4 ·7H 2 O, 0.1mL trace element solution. Adjust the pH value of the medium to 7.5, and sterilize at 121°C for 30min.
[0030] Pseudomonas aeruginosa (Pseudomonas aeruginosa) was inoculated in BM medium containing 10mg / L Zn(II), and cultured with shaking at 30°C and 150rpm, and 100μL headspace was extracted every 5h with a valve injection needle body for the determination of N 2 O, use a sterile syringe to draw 2mL of gas and inject it into a 2L pure helium bag for the determination of NO. At the same time, 2 mL of the bacterial suspension was extracted with a sterile syringe, and the bacterial liquid was centrifuged at 8000 rpm for 5 min at...
Embodiment 3
[0032] Example 3. The aerobic denitrification characteristics of Pseudomonas aeruginosa in the presence of 50mg / L Zn(II)
[0033] Pseudomonas aeruginosa was inoculated in BM medium containing 50mg / L Zn(II) to test its aerobic denitrification performance. The result is as image 3As shown, 100mg / L nitrate nitrogen was utilized by the strain immediately after inoculation, and was completely consumed within 15h, and the average removal rate of nitrate nitrogen was 6.67mg / L / h. With the reduction of nitrate nitrogen, nitrite nitrogen gradually accumulated and reached the highest value of 35.5mg / L at 10h, and then was reduced at 20h. N 2 O also accumulated gradually, reaching the highest value of 84.4mg / L at 20h, and then completely reduced at 45h. It must be pointed out that at this time, the highest NO accumulation in the intermediate product of the denitrification process is 3.2μg / L, accounting for only 0.0032% of the nitrate nitrogen removal. It can be seen that the strain s...
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