Difference between revisions of "Part:BBa K5166066"

 
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<h1>Biology</h1>
 
<h1>Biology</h1>
<p>UreA, UreB, and UreC are all derived from <i>S. pasteurii</i>, and their sequences can be found in the following parts: UreA:BBa_K5166015;UreB:BBa_K5166016;UreB:BBa_K5166017.Microorganisms that produce urease can utilize the enzymatic activity of urease to catalyze the decomposition of urea into ammonia and carbonate, causing metal ions to precipitate into stable carbonates, effectively immobilizing these metals[1].It has been reported that the high-urease-activity strain <i>S. pasteurii</i> can utilize this hydrolytic capability to bind heavy metal ions in water and generate carbonate precipitates to remove heavy metals [2]. Our project precisely leverages the same principle.</p><br>
+
<p>UreA, UreB, and UreC are all derived from <i>S. pasteurii</i>, and their sequences can be found in the following parts: UreA:BBa_K5166015;UreB:BBa_K5166016;UreC:BBa_K5166017.Microorganisms that produce urease can utilize the enzymatic activity of urease to catalyze the decomposition of urea into ammonia and carbonate, causing metal ions to precipitate into stable carbonates, effectively immobilizing these metals<sup>[1] </sup>.It has been reported that the high-urease-activity strain <i>S. pasteurii</i> can utilize this hydrolytic capability to bind heavy metal ions in water and generate carbonate precipitates to remove heavy metals <sup> [2]</sup>. Our project precisely leverages the same principle.</p><br>
  
 
<h1>Experiments</h1>
 
<h1>Experiments</h1>
 
<p><b>Stage 1</b>:<br>
 
<p><b>Stage 1</b>:<br>
Due to the excessive length of the highly efficient urease gene in S. pasteurii, we have divided it into two segments and cloned them onto corresponding plasmids separately. Specifically, UreA, UreB, and UreC are cloned onto the pET28a plasmid (with a T7 promoter), while UreE, UreF, UreG, and UreD are cloned onto the pET21b plasmid (with a proD promoter).(This page shows only the UreABC part)<br>
+
Due to the excessive length of the highly efficient urease gene in <i>S. pasteurii</i>, we have divided it into two segments and cloned them onto corresponding plasmids separately. Specifically, UreA, UreB, and UreC are cloned onto the pET28a plasmid (with a T7 promoter), while UreE, UreF, UreG, and UreD are cloned onto the pET21b plasmid (with a proD promoter).(This page shows only the UreABC part)<br>
  
 
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<b>Stage 2</b>:<br>
 
<b>Stage 2</b>:<br>
 
Based on the issues encountered during Stage 1 of urease expression, we plan to make the following improvements:<br>
 
Based on the issues encountered during Stage 1 of urease expression, we plan to make the following improvements:<br>
Change the promoter: Replace the proD promoter preceding UreE, UreF, UreG, and UreD with the strong T7 promoter to enhance the expression of downstream genes. Concurrently, we need to optimize the induction conditions, which primarily include the concentrations of IPTG and Ni2+, as well as the induction temperature and time, to improve the activity of expressed urease.
+
Change the promoter: Replace the proD promoter preceding UreE, UreF, UreG, and UreD with the strong T7 promoter to enhance the expression of downstream genes. Concurrently, we need to optimize the induction conditions, which primarily include the concentrations of IPTG and Ni<sup>2+</sup>, as well as the induction temperature and time, to improve the activity of expressed urease.
 
For detailed improvements regarding UreEFGD, please refer to Part:BBa K5166065<br>
 
For detailed improvements regarding UreEFGD, please refer to Part:BBa K5166065<br>
 
Similarly, this time we also examined the effect of urease expression through quantitative urease detection and SDS-PAGE analysis. The SDS-PAGE result is shown in Fig.3, while the principle and results of the quantitative urease detection are presented in Fig.4.The urease activity is 0.153U/g DCW(U:the amount of enzyme that catalyzes the formation of 1.0 µmole of ammonia per minute at pH 7.0.)<br>
 
Similarly, this time we also examined the effect of urease expression through quantitative urease detection and SDS-PAGE analysis. The SDS-PAGE result is shown in Fig.3, while the principle and results of the quantitative urease detection are presented in Fig.4.The urease activity is 0.153U/g DCW(U:the amount of enzyme that catalyzes the formation of 1.0 µmole of ammonia per minute at pH 7.0.)<br>
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<b>2.Atomic Force Microscopy (AFM) Observation</b><br>
 
<b>2.Atomic Force Microscopy (AFM) Observation</b><br>
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<p style="text-align: center;"><b>Fig. 6</b> Results of Biomineralization Observed by AFM. a) Dual-plasmid experimental group for Li;b) Dual-plasmid experimental group for Mn;c) Dual-plasmid experimental group for Ni;d) Dual-plasmid experimental group for Co;e) BL21 control group.</p>
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It can be observed that the bacteria in the control group are relatively dispersed, and the surrounding area appears flat. In contrast, the dual-plasmid experimental groups predominantly show aggregation of the bacteria, with noticeable elevation around them. AFM analysis confirms that a layer of material is indeed attached to the bacteria.<br>
 
It can be observed that the bacteria in the control group are relatively dispersed, and the surrounding area appears flat. In contrast, the dual-plasmid experimental groups predominantly show aggregation of the bacteria, with noticeable elevation around them. AFM analysis confirms that a layer of material is indeed attached to the bacteria.<br>
  
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<p style="text-align: center;"><b>Fig. 6</b> SEM Image of Ca<sup>2+</sup> Biomineralization Results.</p>
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<p style="text-align: center;"><b>Fig. 7</b> Electron Microscopy Images of Lithium, Manganese, Nickel, and Cobalt Carbonate Biomineralization(Note: The negative control uses wild-type BL21 bacteria co-cultured with metal ions without urease for biomineralization; the positive control involves the addition of urease to wild-type BL21 bacteria to simulate in vitro biomineralization; the experimental group uses BL21 bacteria expressing recombinant urease with dual plasmids for biomineralization.)a) Li negative control electron microscopy image;b) Mn negative control electron microscopy image;c) Ni negative control electron microscopy image;d) Co negative control electron microscopy image;e) Li experimental group electron microscopy image;f) Mn experimental group electron microscopy image;g) Ni experimental group electron microscopy image;h) Co experimental group electron microscopy image;i) Li positive control electron microscopy image;j) Mn positive control electron microscopy image;k) Ni positive control electron microscopy image;l) Co positive control electron microscopy image.</p>
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As shown in the figure above, the surfaces of the Li, Mn, Ni, and Co negative control bacteria are relatively smooth. The Li experimental group and positive control group exhibit swelling at one or both ends of the bacteria. In the Mn experimental group, the bacteria show swelling at one end, with a ring-like swelling in the middle and additional swelling at both ends; in contrast, the positive control also forms two hemispherical carbonate precipitates around the bacteria. The Ni experimental group presents a swollen appearance at one end and a swelling in the middle of the bacteria, similar to the positive control. The Co experimental group primarily displays a swollen appearance that resembles a club shape at one end and a swelling in the middle of the bacterial surface, while the positive control group shows no significant mineralization on the surface of the bacteria. Next, we will perform EDS analysis on the Mn, Ni, and Co groups to further validate the metal adsorption and mineralization capabilities of our recombinant urease-expressing <i>Escherichia coli.</i><br>
  
 
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<p style="text-align: center;"><b>Fig. 8</b> EDS analysis of Mn. a)Schematic diagram of Mn carbonate biomineralization;b)EDS layered images of Mn;c)EDS analysis of Mn negative control;d)EDS analysis of the Mn
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experimental group;e)EDS analysis of Mn positive control.</p>
 
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<p style="text-align: center;"><b>Fig. 9</b> EDS analysis of Ni. a)Schematic diagram of Ni carbonate biomineralization;b)EDS layered images of Ni;c)EDS analysis of Ni negative control;d)EDS analysis of the Ni experimental group;e)EDS analysis of Ni positive control.</p>
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<p style="text-align: center;"><b>Fig. 7</b> SEM images of Ca<sup>2+</sup> biomineralization results (Note: Negative control is biomineralization by co-incubation with metal ions using wild-type BL21 bacteria without urease double plasmid; Positive control is simulated in vitro biomineralization by adding urease in addition to wild-type BL21 bacteria; Experimental group is the biomineralization of BL21 bacteria with recombinantly expressed double plasmid containing urease in the present project) a) Electromicrograph of Ca negative control;b) Electromicrograph of Ca Electron micrograph of experimental group;c) Electron micrograph of Ca positive control
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<p style="text-align: center;"><b>Fig. 10</b> EDS analysis of Co. a)Schematic diagram of Co carbonate biomineralization b)EDS layered images of Co; c)EDS analysis of Co negative control;d)EDS analysis of the Co experimental group;e)EDS analysis of Co positive control.</p>
 
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The EDS results indicate that the elemental content analysis of Mn, Ni, and Co follows the trend: positive control > experimental group > negative control. This result is normal and relatively ideal, as the positive control group involved the direct addition of urease, allowing metal ions to interact with urease and decompose urea, generating carbonate ions that precipitate as carbonates. Consequently, the metal element content is highest in this group. The recombinant urease <i>Escherichia coli</i> adsorbs and mineralizes metal ions via its expressed urease. However, due to lower urease activity compared to that in the positive control group, the metal element content in the experimental group is slightly lower than in the positive control but significantly higher than in the negative control group. The negative control group, consisting of wild-type BL21 bacteria, does not express urease, rendering it incapable of biomineralization, resulting in the lowest metal element content.<br>
 +
In conjunction with the previously obtained SEM biomineralization images of Li, Mn, Ni, and Co, these findings effectively demonstrate that our recombinant urease-expressing <i>Escherichia coli</i> can successfully facilitate mineralization.<br>
  
As shown in the figure above, the surfaces of the Li, Mn, Ni, and Co negative control bacteria are relatively smooth. The Li experimental group and positive control group exhibit swelling at one or both ends of the bacteria. In the Mn experimental group, the bacteria show swelling at one end, with a ring-like swelling in the middle and additional swelling at both ends; in contrast, the positive control also forms two hemispherical carbonate precipitates around the bacteria. The Ni experimental group presents a swollen appearance at one end and a swelling in the middle of the bacteria, similar to the positive control. The Co experimental group primarily displays a swollen appearance that resembles a club shape at one end and a swelling in the middle of the bacterial surface, while the positive control group shows no significant mineralization on the surface of the bacteria. Next, we will perform EDS analysis on the Mn, Ni, and Co groups to further validate the metal adsorption and mineralization capabilities of our recombinant urease-expressing Escherichia coli.<br></p>
+
<h1>Conclusion</h1>
 +
<p>The results obtained from this study preliminarily demonstrate that the urease from <i>S. pasteurii</i> can be successfully expressed in <i>Escherichia coli</i> and can effectively facilitate mineralization. However, there remains considerable scope for improvement, particularly in enhancing urease activity and optimizing mineralization efficiency. Moving forward, our team will continue to refine the expression system and mineralization conditions, explore more efficient biomineralization methods, and strive to expand the application range of the resulting mineralization products, thereby contributing significantly to environmental protection and resource utilization.</p><br>
  
 
<h1>Reference</h1>
 
<h1>Reference</h1>
<p>[1]Fang L, Niu Q, Cheng L, et al. Ca-mediated alleviation of Cd2+ induced toxicity and improved Cd2+ biomineralization by Sporosarcina pasteurii[J]. Science of The Total Environment, 2021, 787: 147627.(https://www.sciencedirect.com/science/article/pii/S004896972102698X)<br>
+
<p>[1]Fang L, Niu Q, Cheng L, et al. Ca-mediated alleviation of Cd<sup>2+</sup> induced toxicity and improved Cd<sup>2+</sup> biomineralization by Sporosarcina pasteurii[J]. Science of The Total Environment, 2021, 787: 147627.(https://www.sciencedirect.com/science/article/pii/S004896972102698X)<br>
 
[2] Li M, Cheng X, Guo H. Heavy metal removal by biomineralization of urease producing bacteria isolated from soil[J]. International Biodeterioration & Biodegradation, 2013, 76: 81-85.(https://www.sciencedirect.com/science/article/pii/S0964830512001497)<br></p>
 
[2] Li M, Cheng X, Guo H. Heavy metal removal by biomineralization of urease producing bacteria isolated from soil[J]. International Biodeterioration & Biodegradation, 2013, 76: 81-85.(https://www.sciencedirect.com/science/article/pii/S0964830512001497)<br></p>
  

Latest revision as of 03:06, 2 October 2024

UreA-UreB-UreC

Usage

UreABC is the primary functional subunit of bacterial Urease protein,they combine to form a hetero-trimer, which binds together to create an active enzyme.When co-expressed with UreEFGD (the accessory subunit,BBa K5166065) from another part, it can produce bacterial Urease. In this project, we utilize E.coli to express this urease, enabling metal ions present in solution after sorting to precipitate in the form of carbonate, thus achieving the purpose of mineralization.


Biology

UreA, UreB, and UreC are all derived from S. pasteurii, and their sequences can be found in the following parts: UreA:BBa_K5166015;UreB:BBa_K5166016;UreC:BBa_K5166017.Microorganisms that produce urease can utilize the enzymatic activity of urease to catalyze the decomposition of urea into ammonia and carbonate, causing metal ions to precipitate into stable carbonates, effectively immobilizing these metals[1] .It has been reported that the high-urease-activity strain S. pasteurii can utilize this hydrolytic capability to bind heavy metal ions in water and generate carbonate precipitates to remove heavy metals [2]. Our project precisely leverages the same principle.


Experiments

Stage 1:
Due to the excessive length of the highly efficient urease gene in S. pasteurii, we have divided it into two segments and cloned them onto corresponding plasmids separately. Specifically, UreA, UreB, and UreC are cloned onto the pET28a plasmid (with a T7 promoter), while UreE, UreF, UreG, and UreD are cloned onto the pET21b plasmid (with a proD promoter).(This page shows only the UreABC part)


Fig. 1 UreA, UreB, and UreC cloned onto the pET28a plasmid (with a T7 promoter).


However, during the preparation of the urease activity detection medium and quantitative detection, the expression of urease was not apparent. Additionally, in subsequent SDS-PAGE analysis, the protein bands were also not distinct. Therefore, we further optimized our dual-plasmid system.


Fig. 2 SDS-PAGE result of stage 1.


Stage 2:
Based on the issues encountered during Stage 1 of urease expression, we plan to make the following improvements:
Change the promoter: Replace the proD promoter preceding UreE, UreF, UreG, and UreD with the strong T7 promoter to enhance the expression of downstream genes. Concurrently, we need to optimize the induction conditions, which primarily include the concentrations of IPTG and Ni2+, as well as the induction temperature and time, to improve the activity of expressed urease. For detailed improvements regarding UreEFGD, please refer to Part:BBa K5166065
Similarly, this time we also examined the effect of urease expression through quantitative urease detection and SDS-PAGE analysis. The SDS-PAGE result is shown in Fig.3, while the principle and results of the quantitative urease detection are presented in Fig.4.The urease activity is 0.153U/g DCW(U:the amount of enzyme that catalyzes the formation of 1.0 µmole of ammonia per minute at pH 7.0.)


Fig. 3 SDS-PAGE result of stage 2.




Fig. 4 The principle and results of the quantitative urease detection.


Through the above experimental investigations, we have improved the recombinant expression of urease, and measurements have confirmed that the recombinant urease is active.
Stage 3:Mineralization Validation Experiment
We conducted a series of validation experiments, and some of the more representative results are as follows:
1.Optical Microscope Observation
As can be seen from Fig.5, compared to the BL21(DE3) control group, the dual-plasmid experimental group with recombinant urease exhibits significant differences in the mineralization of four metal ions: Li, Mn, Co, and Ni, under optical microscopy. Specifically, the bacteria in the experimental group show noticeable agglomeration and clustering, and a layer of material is clearly attached around the bacteria.


Fig. 5 Optical Microscope Observation of Biomineralization Results.


2.Atomic Force Microscopy (AFM) Observation


Fig. 6 Results of Biomineralization Observed by AFM. a) Dual-plasmid experimental group for Li;b) Dual-plasmid experimental group for Mn;c) Dual-plasmid experimental group for Ni;d) Dual-plasmid experimental group for Co;e) BL21 control group.


It can be observed that the bacteria in the control group are relatively dispersed, and the surrounding area appears flat. In contrast, the dual-plasmid experimental groups predominantly show aggregation of the bacteria, with noticeable elevation around them. AFM analysis confirms that a layer of material is indeed attached to the bacteria.
3.SEM/EDS analysis
Note: Due to the limitations of scanning electron microscopy, elements with an atomic number below that of carbon cannot be analyzed using EDS; therefore, Li cannot be detected with EDS.




Fig. 7 Electron Microscopy Images of Lithium, Manganese, Nickel, and Cobalt Carbonate Biomineralization(Note: The negative control uses wild-type BL21 bacteria co-cultured with metal ions without urease for biomineralization; the positive control involves the addition of urease to wild-type BL21 bacteria to simulate in vitro biomineralization; the experimental group uses BL21 bacteria expressing recombinant urease with dual plasmids for biomineralization.)a) Li negative control electron microscopy image;b) Mn negative control electron microscopy image;c) Ni negative control electron microscopy image;d) Co negative control electron microscopy image;e) Li experimental group electron microscopy image;f) Mn experimental group electron microscopy image;g) Ni experimental group electron microscopy image;h) Co experimental group electron microscopy image;i) Li positive control electron microscopy image;j) Mn positive control electron microscopy image;k) Ni positive control electron microscopy image;l) Co positive control electron microscopy image.


As shown in the figure above, the surfaces of the Li, Mn, Ni, and Co negative control bacteria are relatively smooth. The Li experimental group and positive control group exhibit swelling at one or both ends of the bacteria. In the Mn experimental group, the bacteria show swelling at one end, with a ring-like swelling in the middle and additional swelling at both ends; in contrast, the positive control also forms two hemispherical carbonate precipitates around the bacteria. The Ni experimental group presents a swollen appearance at one end and a swelling in the middle of the bacteria, similar to the positive control. The Co experimental group primarily displays a swollen appearance that resembles a club shape at one end and a swelling in the middle of the bacterial surface, while the positive control group shows no significant mineralization on the surface of the bacteria. Next, we will perform EDS analysis on the Mn, Ni, and Co groups to further validate the metal adsorption and mineralization capabilities of our recombinant urease-expressing Escherichia coli.



Fig. 8 EDS analysis of Mn. a)Schematic diagram of Mn carbonate biomineralization;b)EDS layered images of Mn;c)EDS analysis of Mn negative control;d)EDS analysis of the Mn experimental group;e)EDS analysis of Mn positive control.




Fig. 9 EDS analysis of Ni. a)Schematic diagram of Ni carbonate biomineralization;b)EDS layered images of Ni;c)EDS analysis of Ni negative control;d)EDS analysis of the Ni experimental group;e)EDS analysis of Ni positive control.




Fig. 10 EDS analysis of Co. a)Schematic diagram of Co carbonate biomineralization b)EDS layered images of Co; c)EDS analysis of Co negative control;d)EDS analysis of the Co experimental group;e)EDS analysis of Co positive control.


The EDS results indicate that the elemental content analysis of Mn, Ni, and Co follows the trend: positive control > experimental group > negative control. This result is normal and relatively ideal, as the positive control group involved the direct addition of urease, allowing metal ions to interact with urease and decompose urea, generating carbonate ions that precipitate as carbonates. Consequently, the metal element content is highest in this group. The recombinant urease Escherichia coli adsorbs and mineralizes metal ions via its expressed urease. However, due to lower urease activity compared to that in the positive control group, the metal element content in the experimental group is slightly lower than in the positive control but significantly higher than in the negative control group. The negative control group, consisting of wild-type BL21 bacteria, does not express urease, rendering it incapable of biomineralization, resulting in the lowest metal element content.
In conjunction with the previously obtained SEM biomineralization images of Li, Mn, Ni, and Co, these findings effectively demonstrate that our recombinant urease-expressing Escherichia coli can successfully facilitate mineralization.

Conclusion

The results obtained from this study preliminarily demonstrate that the urease from S. pasteurii can be successfully expressed in Escherichia coli and can effectively facilitate mineralization. However, there remains considerable scope for improvement, particularly in enhancing urease activity and optimizing mineralization efficiency. Moving forward, our team will continue to refine the expression system and mineralization conditions, explore more efficient biomineralization methods, and strive to expand the application range of the resulting mineralization products, thereby contributing significantly to environmental protection and resource utilization.


Reference

[1]Fang L, Niu Q, Cheng L, et al. Ca-mediated alleviation of Cd2+ induced toxicity and improved Cd2+ biomineralization by Sporosarcina pasteurii[J]. Science of The Total Environment, 2021, 787: 147627.(https://www.sciencedirect.com/science/article/pii/S004896972102698X)
[2] Li M, Cheng X, Guo H. Heavy metal removal by biomineralization of urease producing bacteria isolated from soil[J]. International Biodeterioration & Biodegradation, 2013, 76: 81-85.(https://www.sciencedirect.com/science/article/pii/S0964830512001497)

Sequence and Features


Assembly Compatibility:
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    INCOMPATIBLE WITH RFC[10]
    Illegal XbaI site found at 47
  • 12
    INCOMPATIBLE WITH RFC[12]
    Illegal NheI site found at 129
  • 21
    COMPATIBLE WITH RFC[21]
  • 23
    INCOMPATIBLE WITH RFC[23]
    Illegal XbaI site found at 47
  • 25
    INCOMPATIBLE WITH RFC[25]
    Illegal XbaI site found at 47
    Illegal AgeI site found at 514
    Illegal AgeI site found at 1055
    Illegal AgeI site found at 2485
  • 1000
    COMPATIBLE WITH RFC[1000]