Team:UAB-Barcelona/Project2

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== '''Nitrite, nitrate and phosphate''' ==
== '''Nitrite, nitrate and phosphate''' ==
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The main risk for nitrate is its ability to oxidizes to nitrite, which has the responsibility for the toxic effects (See “nitrites” below). Also, they contribute to increase the cultural eutrophication effect (see “phosphates” below).  The Environmental Protection Agency (EPA) has adopted the 10 mg/L standard as the maximum contaminant level (MCL) for nitrate-nitrogen
The main risk for nitrate is its ability to oxidizes to nitrite, which has the responsibility for the toxic effects (See “nitrites” below). Also, they contribute to increase the cultural eutrophication effect (see “phosphates” below).  The Environmental Protection Agency (EPA) has adopted the 10 mg/L standard as the maximum contaminant level (MCL) for nitrate-nitrogen
-
===Nitrite===
+
===Nitrites===
Nitrite ions have the same primary origin than nitrate ones, owing to the fact that the majority of nitrite ions are produced by the oxidation of nitrate-nitrogen.
Nitrite ions have the same primary origin than nitrate ones, owing to the fact that the majority of nitrite ions are produced by the oxidation of nitrate-nitrogen.
Line 44: Line 41:
To sum up, it is very important to regulate nitrite concentrations in drinking waters. EPA establish the maximum contaminant level (MCL) for nitrite-nitrogen in about 1 mg/L
To sum up, it is very important to regulate nitrite concentrations in drinking waters. EPA establish the maximum contaminant level (MCL) for nitrite-nitrogen in about 1 mg/L
-
===Phosphate===  
+
===Phosphates===  
Line 55: Line 52:
Therefore, it is very important to regulate and limit the phosphate concentration in water, even more if this water will end in a reservoir like a lake. EPA establishes the MCL for phosphate in no more than 0,1 mg/L for streams that do not empty into reservoirs, 0.05 mg/L for streams which empty into reservoirs, and 0,025 for reservoirs.
Therefore, it is very important to regulate and limit the phosphate concentration in water, even more if this water will end in a reservoir like a lake. EPA establishes the MCL for phosphate in no more than 0,1 mg/L for streams that do not empty into reservoirs, 0.05 mg/L for streams which empty into reservoirs, and 0,025 for reservoirs.
 +
= '''Project Details''' =
 +
{|class="wikitable" border="0" cellpadding="10" cellspacing="1" style="padding: 0; background-color:black;  border: 1px solid black; text-align:center; margin:5px -5px 5px -5px"
 +
!width="30%" align="left" valign="top" style="background:#ECC850; color:black"|
 +
=='''Theoretical basis of the detection of nitrite'''==
 +
We will take advance of the ''N. europaea'' nirK system. This system encodes a nitrite reductase that is synthethised in response to high levels of nitrite.
 +
The key sequences are:
 +
-the nsrR protein (nitrite sensitive transcriptional repressor), that is constitutive
-
= '''Project Details''' =
+
-the promoter ''Pnir'' (that is before the nitrite reductase)
-
{|class="wikitable" border="0" cellpadding="10" cellspacing="1" style="padding: 0; background-color:black;  border: 1px solid black; text-align:center; margin:5px -5px 5px -5px"
+
-
!width="30%" align="left" valign="top" style="background:#ECC850; color:black"|
+
-
=='''The beginning of the laboratory work'''==
+
-
|-
+
In the absence of nitrite, nsrR is recognising a sequence inside ''Pnir'' and is bound blocking the transcription. In the presence of nitrite, it is released and it allows the transcription and synthesis of the downstream protein.
-
|}
+
In ''E. coli'' it works properly too.
 +
 
 +
So if we couple a reporter protein to ''Pnir'' and we add nsrR with a constitutive promoter, we will be able to detect the presence of nitrite. The threshold is around 3 milimolar at pH 5.3
 +
 
 +
This is our construct:
 +
 
 +
[[Image:designnitrite.jpg]]
 +
 
 +
=='''Theoretical basis of the detection of phosphate'''==
 +
 
 +
''Escherichia coli'' has a system to produce alkaline phosphatase if there is phosphate starvation.
 +
 
 +
''E. coli'' detects the low concentration of external phosphate, and after a chain of interactions, PhoB binds to ''phoA'' promoter, giving the σ70 binding region the promoter lacks and enhances the transcription and consequently the synthesis of alkaline phosphatase.
 +
 
 +
Joining ''phoA'' to a inverter system (like lacI)and then to a reporter is a mean of detecting phosphate concentration is water
 +
 
 +
[[Image:designphosphate.jpg]]
 +
 
 +
=='''Practical work for the detection of nitrite'''==
 +
 
 +
 
 +
====Cloning ''Pnir'' and nsrR====
 +
 
 +
 
 +
 
 +
We cloned the promoter ''Pnir'' and the protein nsrR from ''N.europaea''
 +
 
 +
First of all, we grew ''Nitrosomonas europaea''. It was a hard work because it grows very slowly. We used the ATCC recommended medium and after a week we could  <html><a href="https://2009.igem.org/Team:UAB-Barcelona/ext">extract the genomic DNA</a></html>
 +
 
 +
While growing, we ordered the <html><a href="https://2009.igem.org/Team:UAB-Barcelona/Primersn">four primers</a></html>
 +
 
 +
We cloned <html><a href="https://2009.igem.org/Team:UAB-Barcelona/PCRN">both sequences</a></html>
 +
 
 +
A problem we found was the fact that nsrR sequence has a EcoRI target inside. So it wouldn't fulfill the requirements of the standards.As the target is in the very middle of the sequence, we could't introduce a silent mutation with the primers.
 +
 
 +
The solution would be synthesizing the nsrR sequence with a silent mutation, but we didn't have enough time to order and receive it.
 +
 
 +
====Making new biobricks====
 +
 
 +
Following this <html><a href="https://2009.igem.org/Team:UAB-Barcelona/CS1">cloning strategy</a></html> we aimed to design this biobricks:
 +
 
 +
'''''Detection of nitrite'''''
 +
 
 +
''Ptet''-RBS-nsr-RBS-GFP-T-T  -------linker--------''Pnir''-RBS-tetR-RBS-RFP-T-T  // '''Biobrick 17'''
 +
 
 +
or
 +
 
 +
''pLac''-RBS-nsr-RBS-GFP-T-T  -------linker--------''Pnir''-RBS-LacI-RBS-RFP-T-T  // '''Biobrick 18'''
-
= '''Results and discussion''' =
 
-
{|class="wikitable" border="0" cellpadding="10" cellspacing="1" style="padding: 0; background-color:black;  border: 1px solid black; text-align:center; margin:5px -5px 5px -5px"
 
-
!width="30%" align="left" valign="top" style="background:#ECC850; color:black"|
 
-
=='''MilliQ® or distilled water?'''==
 
-
Distilled water has a small amount of chloroform, and we thought it could be able to activate gfp expression.
 
-
We made parallel experiments with both milliQ® and distilled water in order to discover if that amount could affect our research. So we made mediums and PBS solutions with those kind of water.
 
-
Finally, results showed us that the difference in chloroform between the two types of water produced no observable variation in gfp expression
 
-
=='''PBS'''==
+
'''''Using Pnir/nsrR regulation system'''''
-
Previous studies proved that sample incubation in PBS solution may amplify the fluorescence signal when working with GFP protein.
+
Biobrick with ''Pnir''  // '''Biobrick 2'''
-
However, when we were making our fluorescence measurement, we noticed that it was lower in samples which were incubated less. Then, we decided to do a kinetic experiment about how PBS affected our samples.
+
Biobrick with ''nsrR''  // '''Biobrick 3'''
-
The results showed that there was a top fluorescence at 30 minutes, but after this maximum, fluorescence declined with time. Thus the optimum time for incubation were 30 minutes.
+
=='''Practical work for the detection of phosphate'''==
-
It is due to the small amount of GFP in our samples. If we had used GFP-full samples, the optimum time would be higher.
+
====Cloning ''phoA''====
-
=='''Volatilization'''==
+
We cloned the promoter ''phoA'' from ''Escherichia coli''
-
When we performed the assays, one of the problems we had to think about was related to chloroform volatility. It was reasonable to suppose that chloroform concentrations could be modified due to that factor. Consequently, we tried to avoid chloroform losses by completely filling up test tubes, but it was useless.
+
First of all we grew ''E. coli'' DH5-alpha, and then we <html><a href="https://2009.igem.org/Team:UAB-Barcelona/ext">extracted the genomic DNA</a></html>
-
After that, a gas chromatography was done to check that fact; nevertheless, there was no appreciable variation in chloroform levels with time.
 
-
This is a logic result because all chloroform concentrations we tested were under its maximun water solubility. All of these conclusions can be contrasted in the following graphic.
 
-
=='''Induction experiment'''==
+
We ordered the <html><a href="https://2009.igem.org/Team:UAB-Barcelona/Primersp">two primers</a></html> for ''phoA''
-
For the induction experiment we followed a series of steps:
+
After that, we <html><a href="https://2009.igem.org/Team:UAB-Barcelona/PCRP">cloned</a></html> ''phoA''
-
• The day before the tests we inoculated a LB medium with our bacteria.
+
====Making new biobricks====
-
• The day of the tests:
+
Following this <html><a href="https://2009.igem.org/Team:UAB-Barcelona/CS1">cloning strategy</a></html> we aimed to design this biobricks:
-
o We pelleted the culture and resuspended in new LB medium.
+
'''''Detection of phosphate'''''
-
o We added the chloroform in several concentrations, from 0 to 3000μL (0, 7, 33.5, 84, 100, 168, 300, 1000, 1500 and 3000 μL). The standard test used 0, 33.5, 84 and 100  μL.
+
''pLacI''-RBS-RFP-T-T  -------linker--------''Phoa''-RBS-LacI-RBS-GFP-T-T // '''Biobrick 13'''
-
o We incubated the aliquots in different times, from 30 minutes to 120 minutes. The standar test used 30 and 90 minutes.
+
or
-
o We pelleted again and resuspended in PBS.
+
''ptet''-RBS-RFP-T-T  -------linker--------''Phoa''-RBS-tetR-RBS-GFP-T-T // '''Biobrick 14'''
-
o We incubated 30 minutes in PBS.
+
='''Bibliography'''=
-
o We measured fluorescence.
+
''''References''''
-
The highest concentrations turned out toxic to our cultures. This is reasonable considering they were higher than those which there are in drinking water.
+
''Nitrite''
-
The tests were run with three strains, a DH5alpha ''E.coli'', a mbla promoter-mutant ''E.coli'' and a clpb promoter-mutant ''E.coli''. But results showed an increase in fluorescence with time in all the strains, thus there were no conclusive conclusions.
+
Beaumont, H.J.E., Lens, S.I., Reijnders, W.N.M., Westerhoff, H.V and van Spanning, R.J.M. Expression of nitrite reductase in Nitrosomonas europaea involves NsrR, a novel nitrite-sensitive transcription repressor. Molecular Microbiology (2004) 54: 148–158
-
=='''AMO'''==
 
-
Our project was based on the ability of gfp-recombinant ''Nitrosomonas europaea'' strain to detect and metabolize chloroform, and thus express GFP. It’s supposed that ''N.europaea'' is able to do that due to the presence AMO, which is believed to recognize unspecifically this pollutant and oxidizes it to phosgene. Then, gfp expression would be activated.
+
''Phosphate''
-
So that, primer sequences were dessigned in order to clone amo gene by PCR. Nevertheless, after performing the PCR, purification and electrophoresis, we could observe the absence of the expected DNA.
+
Guan, D., Wanner, B. and Inouye, H. Analysis of regulation of phoB expression using a phoB-cat
 +
fusion. Journal of bacteriology (Nov 1983) 710-717
-
It was obvious that something was wrong, and it was thought that it could be due to the small amount of “mould” DNA. Therefore a ''N.europaea'' strain was grown up, but it took us about two weeks. When whe had a suitable optical density, we proceed to repeat the PCR. Unfortunately, we reached the same results. This conducted us to conclude that there was a mistake designing primer sequences.
+
Van Dien, S.J. and Keasling, J.K.  Analysis of regulation of phoB expression using a phoB-cat fusion. J.theor.biol. (1998) 190, 37-49
-
So, we could not obtain an amo-recombinant ''E.coli'' strain, and thus we could not reach our goal.
+
Amemura,M., Makino, K., Shinagawa,M., Nakata,A. Cross talk to the phosphate regulon of Escherichia coli by PhoM protein: PhoM Is a histidine protein kinase and catalyzes phosphorylation of PhoB and PhoM-open reading frame 2. Journal of bacteriology, Nov. 1990, p. 6300-6307
-
=='''Inclusion bodies'''==
 
-
As it was mentioned above, we tried to add chloramphenicol in order to inhibit protein synthesis and avoid producing those inclusion bodies. However, we didn't obtain any evidence about this; even more, it seemed that chloramphenicol contributed to slightly decrease fluorescence signal.
+
''Nitrate''
-
After that, we could check, by carrying out confocal microscopy, that there is not any inclusion bodies production. Thus, this fact could not affect neither gfp concentrations nor signal strength in our assays.
+
Wang,H. , Tseng, C.P., and .Gunsalus, R.P. The napF and narG nitrate reductase operons in Escherichia
 +
coli are differentially expressed in response to submicromolar concentrations of nitrate but not nitrite. Journal of bacteriology (Sept. 1999,) p. 5303–5308

Latest revision as of 03:02, 22 October 2009

Encap raro.jpg Documento sin título


Contents

Overall project

Abstract

In this project our aim is to engineer a biosensor that will be able to detect simultaneously the presence of the nitrite, nitrate and ortophosphate ions in water.

One of the tools that our biosensor uses is de nirK/nsrR system from N.europaea. We can use it too as a new transcriptional regulation system, as a protein coding sequence joined to Pnir (nirK promoter) without the presence of nitrite won't be expressed due to the coupling of NsrR (nitrite sensitive repressor)to Pnir. If we add nitrite to the media, NsrR will be released and the transcription will begin.

For our sensitive bacteria, we will join Pnir to a reporter gene , so we will be able to detect when NO2- concentration reaches a threshold.

To detect the phosphate we will make use of the phoA promoter from E. coli. It's upregulated in the absence of phosphate, so it can be used to detect its presence in waters after coupling it with an inverting system like tetR and then adding a reporter gene.

The nitrate will be detected using narG promoter from E.coli. This promoter takes part in the nitrate reductase system and it has its expression enhanced with the presence of NO3-. We will be able to detect the presence of nitrate coupling the promoter with a reporter protein. We notice it when the concentration of nitrate reaches a threshold.

Nitrite, nitrate and phosphate

Nitrates

Nitrogen compounds occur naturally into the soil from decaying plants and animals. Main sources of nitrogen compounds include human sewage and livestock manure; inorganic sources examples are plant fertilizers such potassium nitrate and ammonium nitrate. Many nitrificant bacteria are able to convert the rest of nitrogen compounds to nitrate ions; nitrate is also the form absorbable by plants. However, nitrate is highly leachable so that it can reach and pollute water easily.

The main risk for nitrate is its ability to oxidizes to nitrite, which has the responsibility for the toxic effects (See “nitrites” below). Also, they contribute to increase the cultural eutrophication effect (see “phosphates” below). The Environmental Protection Agency (EPA) has adopted the 10 mg/L standard as the maximum contaminant level (MCL) for nitrate-nitrogen

Nitrites

Nitrite ions have the same primary origin than nitrate ones, owing to the fact that the majority of nitrite ions are produced by the oxidation of nitrate-nitrogen.

It's very important to measure these ions in drinking water, especially for infants, pregnant and nursing women, and elderly people. Nitrite is able to oxidize Fe2+ to Fe3+ and thus transform hemoglobin to methemoglobin. When reaching the first year of life, most people can revert this transformation easily, but there are some risk groups, including babies under 1 year, pregnant and nursing women and elderly people. It is possible for them to get their enzymatic systems saturated and cannot convert methemoglobin to oxyhemoglobin, acquiring methemoglobinemia. This is a pathology in which there isn't hemoglobin enough to satisfy the tissues demands, so that symptoms should be: difficulty to breath and blueness of skin, and in long term diuresis, increased starchy deposits and hemorrhaging of the spleen.

To sum up, it is very important to regulate nitrite concentrations in drinking waters. EPA establish the maximum contaminant level (MCL) for nitrite-nitrogen in about 1 mg/L

Phosphates

Phosphorus allows plants and animals to grow and function, as it is an essential macronutrient. Inside living being, phosphorus is found in its oxidized form, phosphate. It is part of lots and lots of biochemical molecules, such as DNA, proteins, ATP, phospholipids, etc. Thus, phosphates are found in every wastewater and sewage, which constitute the main source of these ions. Also, they can increase their concentration due to the presence of fertilizers and so other farming products which can increase water phosphate levels.

When drinking water with very high levels of phosphates, digestive problems could occur, but they don't have any important toxic effect. The main risk of getting a high concentration of phosphates is produced on the environment; they allow the phenomenon of eutrophication. It is a term for what happens when algae becomes unusually productive on water systems, and is due to the presence in water of a large amount of nutrients. Eutrophication consists of the formation of masses of algae's blooms which choke rivers and lakes.

The consequence of generating such those algae blooms is the massive consumption of resources as oxygen, as well as the cut of light supply. Eutrophicated areas are dead areas, where is impossible for life to develop. The equilibrium of ecosystems is, thus, deeply altered.

Therefore, it is very important to regulate and limit the phosphate concentration in water, even more if this water will end in a reservoir like a lake. EPA establishes the MCL for phosphate in no more than 0,1 mg/L for streams that do not empty into reservoirs, 0.05 mg/L for streams which empty into reservoirs, and 0,025 for reservoirs.

Project Details

Theoretical basis of the detection of nitrite

We will take advance of the N. europaea nirK system. This system encodes a nitrite reductase that is synthethised in response to high levels of nitrite. The key sequences are:

-the nsrR protein (nitrite sensitive transcriptional repressor), that is constitutive

-the promoter Pnir (that is before the nitrite reductase)

In the absence of nitrite, nsrR is recognising a sequence inside Pnir and is bound blocking the transcription. In the presence of nitrite, it is released and it allows the transcription and synthesis of the downstream protein. In E. coli it works properly too.

So if we couple a reporter protein to Pnir and we add nsrR with a constitutive promoter, we will be able to detect the presence of nitrite. The threshold is around 3 milimolar at pH 5.3

This is our construct:

Designnitrite.jpg

Theoretical basis of the detection of phosphate

Escherichia coli has a system to produce alkaline phosphatase if there is phosphate starvation.

E. coli detects the low concentration of external phosphate, and after a chain of interactions, PhoB binds to phoA promoter, giving the σ70 binding region the promoter lacks and enhances the transcription and consequently the synthesis of alkaline phosphatase.

Joining phoA to a inverter system (like lacI)and then to a reporter is a mean of detecting phosphate concentration is water

Designphosphate.jpg

Practical work for the detection of nitrite

Cloning Pnir and nsrR

We cloned the promoter Pnir and the protein nsrR from N.europaea

First of all, we grew Nitrosomonas europaea. It was a hard work because it grows very slowly. We used the ATCC recommended medium and after a week we could extract the genomic DNA

While growing, we ordered the four primers

We cloned both sequences

A problem we found was the fact that nsrR sequence has a EcoRI target inside. So it wouldn't fulfill the requirements of the standards.As the target is in the very middle of the sequence, we could't introduce a silent mutation with the primers.

The solution would be synthesizing the nsrR sequence with a silent mutation, but we didn't have enough time to order and receive it.

Making new biobricks

Following this cloning strategy we aimed to design this biobricks:

Detection of nitrite

Ptet-RBS-nsr-RBS-GFP-T-T -------linker--------Pnir-RBS-tetR-RBS-RFP-T-T // Biobrick 17

or

pLac-RBS-nsr-RBS-GFP-T-T -------linker--------Pnir-RBS-LacI-RBS-RFP-T-T // Biobrick 18



Using Pnir/nsrR regulation system

Biobrick with Pnir // Biobrick 2

Biobrick with nsrR // Biobrick 3

Practical work for the detection of phosphate

Cloning phoA

We cloned the promoter phoA from Escherichia coli

First of all we grew E. coli DH5-alpha, and then we extracted the genomic DNA


We ordered the two primers for phoA

After that, we cloned phoA

Making new biobricks

Following this cloning strategy we aimed to design this biobricks:

Detection of phosphate

pLacI-RBS-RFP-T-T -------linker--------Phoa-RBS-LacI-RBS-GFP-T-T // Biobrick 13

or

ptet-RBS-RFP-T-T -------linker--------Phoa-RBS-tetR-RBS-GFP-T-T // Biobrick 14

Bibliography

'References'

Nitrite

Beaumont, H.J.E., Lens, S.I., Reijnders, W.N.M., Westerhoff, H.V and van Spanning, R.J.M. Expression of nitrite reductase in Nitrosomonas europaea involves NsrR, a novel nitrite-sensitive transcription repressor. Molecular Microbiology (2004) 54: 148–158


Phosphate

Guan, D., Wanner, B. and Inouye, H. Analysis of regulation of phoB expression using a phoB-cat fusion. Journal of bacteriology (Nov 1983) 710-717

Van Dien, S.J. and Keasling, J.K. Analysis of regulation of phoB expression using a phoB-cat fusion. J.theor.biol. (1998) 190, 37-49

Amemura,M., Makino, K., Shinagawa,M., Nakata,A. Cross talk to the phosphate regulon of Escherichia coli by PhoM protein: PhoM Is a histidine protein kinase and catalyzes phosphorylation of PhoB and PhoM-open reading frame 2. Journal of bacteriology, Nov. 1990, p. 6300-6307


Nitrate

Wang,H. , Tseng, C.P., and .Gunsalus, R.P. The napF and narG nitrate reductase operons in Escherichia coli are differentially expressed in response to submicromolar concentrations of nitrate but not nitrite. Journal of bacteriology (Sept. 1999,) p. 5303–5308