Difference between revisions of "Team:UC Davis/Safety"

 
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<a href="https://2015.igem.org/Team:UC_Davis/Project" style="text-decoration:none;color:#FFFFFF">PROJECT</a> </td>
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<a href="https://2015.igem.org/Team:UC_Davis/Attributions" style="text-decoration:none;color:#FFFFFF">TEAM </a> </td>
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<a href="https://2015.igem.org/Team:UC_Davis/Design" style="text-decoration:none;color:#FFFFFF">PROJECT</a> </td>
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<a href="https://2015.igem.org/Team:UC_Davis/Parts" style="text-decoration:none;color:#FFFFFF">ACHIEVEMENTS</a> </td>
  
 
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<a href="https://2015.igem.org/Team:UC_Davis/Attributions" style="text-decoration:none;color:#FFFFFF">THE TEAM</a> </td>
  
 
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<a href="https://2015.igem.org/Team:UC_Davis/Safety" style="text-decoration:none;color:#FFFFFF">SAFETY </a></td>
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<font size="5" face = "Avenir">Table of Contents:<br><br>
<a href="#firstblock"> 1. First section<br>
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<a href="#firstblock"> 1. Safety<br><br>
<a href="#secondblock"> 2. Second section<br>
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<a href="#secondblock"> 2. Protocols<br><br>
<a href="#thirdblock"> 3. Third section<br>
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<b>In the Laboratory</b><br>
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At the beginning of summer everyone on our team took the online UC Fundamentals of Laboratory Safety course. This course described correct use of personal protective equipment and engineering safety controls within the lab to reduce risks associated with each lab space. The course also covered methods involved in chemical safety including the identification of chemical hazards through the use of Material Safety and Data Sheets (MSDS) and pictograms as well as proper chemical storage and disposal. In addition to this general safety course, we were also trained on the laboratory specific hazards by the lab managers of the three spaces that we worked in. <br><br>
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Since our project involved use of some proteins found in known pathogens, we decided to synthesize the genes we were interested in through IDT to express in laboratory E. coli. These safety precautions ensured that we 1. did not culture pathogenic organisms in the laboratory and 2. the proteins we expressed were not toxic or pathogenic. To ensure that our engineered strains did not exit the lab, we killed all of our cultures with 10% (v/v) bleach before disposal. We also did not transport any engineered strains outside of the lab, reducing the risk of release. <br><br>
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Our project involved the use of an array of small molecules. To ensure safety, we followed recommendations in the MSDS for each of the chemicals that we used. When ordering our library of alternate FabI substrates, we made sure not to order chemicals that were acutely toxic. For the chemicals we tested, we followed the MSDS recommendations for proper use of personal protective equipment including, wearing eye protection, lab coats, and wearing rubbing gloves, and engineering controls such as a working in the fume hood to eliminate the risk of chemical exposure.<br><br>
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The inhibitor we are detecting, triclosan, is toxic, so we created a triclosan waste container to avoid dumping triclosan down the drain. The proper way to dispose of this container is to give it to <a href = "http://safetyservices.ucdavis.edu/quick-links/hazardous-waste-disposal-request">UC Davis’s Environmental Health and Safety Services </a>
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<strong>Sources:</strong><br>
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<b>In the Real World</b><br>
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The use of laboratory expressed enzymes in the environment is defined in <a href = "https://static.igem.org/mediawiki/2015/7/73/Coordinated-Framework-for-Regulation-of-Biotechnology.pdf">The Coordinated Framework for Regulation of Biotechnology </a>. Our device and its associated biosensor must be approved through this process before use in the real world. Additionally, for application in the real world setting, future screening of alternate substrates would require us to look for substrates that are non hazardous to use outside of the laboratory setting. The handling of known concentrations of triclosan must be handled with proper PPE outside of the lab. See above for triclosan disposal.
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1. We talked to researchers at the San Francisco Estuary Institute (SFEI), one of California’s premier aquatic and ecosystem science institutes.
 
  
From researchers at SFEI we learned that there is a need to better understand how chemicals get into our environment as well as their long-term effects (especially on aquatic organism health), but that this is difficult because chemicals are found in many sources and their effects can be insidious/slow acting.
 
  
Aquatic organisms are particularly at risk because they are constantly subjected to these toxic chemicals – making their exposure more chronic in nature.
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<b><u>Preparation of DNA for Cloning</u></b><br>
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Originally, our cloning method was to be Gibson assembly. We ordered our 8 genes with 5’ and 3’ gibson overhangs from IDT. Once received, we rehydrated the genes:
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<br><br>
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1. Centrifuge for 3-5 seconds at >3000 x g to pellet at the bottom<br>
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2. Add 20 uL TE buffer or Milli-Q water for a final concentration of 10ng/uL<br>
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3. Briefly vortex and centrifuge<br>
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4. Store at -20 degrees for up to 24 months with TE buffer or 1 month with dH2O<br>
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<br>
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We made four 50 mL and four 2 mL overnight cultures of DH10B containing pET29b+ vector for insertion with kanamycin resistance selection. The grown 50 mL cultures were then transferred to 50 mL falcon tubes and spun down to pellet at 4000 x g for 10 minutes. We then followed the protocol included in the Invitrogen MaxiPrep kit used. The results gave an average of 1.93 ng/uL, which is below the threshold for accurate concentration measurement for the Biotek Epoch spectrophotometer with the Take3 Microvolume plate. This also showed that the results yielded next to no DNA for the MaxiPrep and decided to go forth with a MiniPrep on the four 2 mL cultures using the Invitrogen MiniPrep protocol provided with the kit. The results yielded an average of 90 ng/uL which is above the 60-80 ng/uL concentration needed for the restriction digestion. <br><br>
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To manage the risk of triclosan, SFEI is pursuing source control measures.
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San Francisco Estuary Institutes researchers collect data to assess and improve the health of the waters, wetlands, wildlife, and landscapes of the San Francisco Bay and the California Delta.
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In 2011, SFEI named triclosan a contaminant of emerging concern and identified the following key information gaps [1]:
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- the contributions of storm water runoff and municipal waste water as pathways of triclosan to surface waters
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- the potential chronic effects on algae and microbes due to long term exposure to concentrations of triclosan and other antimicrobials that are typically found in aquatic organisms
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- the occurrence of degradation and transformation products
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- the identity, extent of use, and potential environmental health impacts of chemicals used as replacements for triclosan
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In particular, researchers expressed concern over how most of the toxicity threshold data currently available are from acute effect studies, which are not indicative of the potential effects due to long-term, chronic exposure to concentrations that are typically found in aquatic environments.
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While environmental levels may seem low, in chronic toxicity studies, effects on the endocrine system in amphibians and the structure and function of algal communities have been observed at concentrations occurring in the environment (Veldhoen et al. 2006; Wilson et al. 2003). More research needs to be done to study the chronic effects.
 
  
Additional concerns include the potential for indirect effects on algal and aquatic plant grazers due to the toxicity of triclosan to algae and the combined effects of persistent antimicrobial compounds, such as triclosan and triclocarban, on microbial communities.
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<b><u>Double digestion:</u></b>
--
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<br><br>
Because triclosan is commonly found in consumer products, ECWG’s approach to managing triclosan’s risks is, “encouraging less consumer usage of triclosan-containing antimicrobial hand soaps and other consumer products.”[3]
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<span class="read-more-target">
  
[1] http://www.sfei.org/sites/default/files/general_content/Triclosan_profile_0.pdf
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We used the NEB double digest finder to select which buffer and protocol to use for our reaction. Since we used NdeI and EcoRI as our restriction sites, the highest activity without having star activity was NEBuffer 3.1 with 100% activity in NdeI and 50% activity in EcoRI. 50 uL double digest reactions were made of the miniprep, containing 1 uL of each restriction enzyme, 5 uL of the 10x 3.1 NEBuffer, and the remaining 43 uL of our miniprepped plasmid and allowed to incubate at 37 degrees for one hour.
[2] http://www.sfei.org/projects/contaminants-emerging-concern-strategy
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[3]http://www.sfei.org/sites/default/files/biblio_files/RMP2011_TriclosanFactsheet_Final4web.pdf
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1. We met with Arlene Blum, director of Green Science Policy Institute, who works to inform companies on the appropriate use of toxic chemicals.
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Blum provided two key pieces of information:
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• the need to regulate chemicals as classes
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• and the influential role industry can play with their purchasing power
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- CLICK FOR MORE INFO -
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<p class="read-more-wrap">
  
Blum highlighted the incongruity in evaluating chemical toxicity/risks on an individual basis when chemicals interact with other chemicals – oftentimes synergistically – in the environment. To that end, Green Science Policy Institute categorizes and evaluates chemicals in 6 main classes: highly fluorinated chemicals, flame retardants, bisphenols & phthalates, organic solvents, metals, and antimicrobials.
 
  
To expound further on the utility of a ‘class’ approach, Blum explained how when chemicals are removed from use, manufacturers look for a replacement; but because these chemicals need to serve similar functions, they often have similar structures, and thus similar consequences. What results is a cycle whereby one toxic chemical is replaced by another toxic chemical.
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<b><u>Gel separation and purification:</u></b>
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<br><br>
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<span class="read-more-target">
  
Blum aims to stop this cycle and reduce the overall use of toxic chemicals in consumer products by targeting the elimination of these classes of chemicals where there use has no proven benefit.  
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Each 50 uL sample received 10 uL of NEB 6x loading dye and was run on a 1% agarose gel alongside uncut plasmid and O’Generuler 1kb Plus (Thermofisher). The gel was analysed on a [name of gel machine] and the lines of linear plasmid were cut out and placed in premeasured 2 mL eppendorf micro centrifuge tubes and weighed again. Gel purification was completed with the QIAprep Gel Extraction Kit, following the protocol provided with the kit. The average concentration of the DNA from the gel purification was about 14 ng/uL, much less than wanted for the next step.
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Blum affirmed that policy change through government is often slow and mentioned that a quicker, more effective, way to bring about change is if key players in industry take action. By electing to phase a chemical out of their products, industry can have an enormous influence on the types and amount of chemicals that are released into our environment.
 
  
At Green Policy Institute, Blum works to inform manufacturers, retailers and consumers about where these classes of chemicals can be found, how they can be avoided, and what alternatives might be available.
 
  
This approach has proven effective: Green Science Policy Institute provided much of the data that was instrumental in persuading furniture manufacturers to reduce their use of flame-retardants and in persuading policy makers to revise state furniture flammability standards. source
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<div>
  
3. We talked to Bruce Hammock, a National Academy Member for his work in environmental toxicology. Has authored # of papers on triclosan, and is largely responsible for raising awareness about triclosan/putting triclosan on the map.
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Hammock talked about how there are appropriate and inappropriate uses for chemicals, and that for even triclosan, a chemical that he has authored # papers on,
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<p class="read-more-wrap">
Even Hammock, who has authored ___ papers on the ___ of triclosan, mentioned that triclosan is not all bad.
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urged for the more prudent usage of chemicals – stating that the context of application is really important in determining when a chemicals use is appropriate. To illustrate this, Hammock talked about how triclosan actually plays a very useful role in surgical scrubs by removing the last 1% of bugs that soap won’t remove but that this extra bit of killing power is not needed in everyday use.
 
  
4. We talked to Jonathan Eisen, ____ who studies microbial communities.
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<b><u>Gibson assembly:</u></b>
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<br><br>
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<span class="read-more-target">
  
Doesn’t like how triclosan is embedded in building products
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5 uL gibson reaction were performed with 2.5 uL of gibson master mix and with rest having equimolar amounts of linear vector and gene. The reactions were placed in a 50 degree dry bath and left to react for 1 hour.
Questions if triclosans use in commercial products is justified.
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We don't know enough about harmful effects but are putting them in anyways.  
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Wrong approach. Instead, should justify a chemicals use before putting it into products.
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Summary:
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<div>
From talking to experts, we concluded that its hard to track and monitor the spread of chemicals because chemicals are found in a range of products and make their way into the environment through a variety of routes.
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In the environment, chemicals interact with one another – oftentimes synergistically. Aquatic organisms are particularly at risk because of their chronic exposure to toxic chemicals.
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To more effectively manage risks experts are pursuing the following measures:
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- regulating chemicals by class instead of on an individual basis
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- source control at the consumer and industry level
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And have expressed the need for:
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- raising awareness around appropriate use
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- and justifying the use of these chemicals in products
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<b><u>Transformation:</u></b>
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The 5 uL of DNA from the Gibson reactions were then loaded onto Millipore (type VSWP) drop dialysis film with 0.025 μm on ~40 uL of ultra-pure Milli-Q water for desalting over the course of one hour. 2 uL of dialyzed DNA along with 30 uL of electrocompetent BLR cells were transferred to Bio Rad 0.1 cm gap Gene Pulser cuvettes for electroporation and kept chilled. Electroporation was conducted with a Bio-Rad MicroPulser Electroporator set to pulse on the bacteria setting. After electroporation, the cells were immediately transferred to 200 L of TB and placed in a 37° incubator to recover for an hour. The cells were then added to LB agar plates with kanamycin and spread with ~10 sterile glass beads per plate. The beads were then dumped into 70% ethanol and the plates were allowed to dry in the incubator at 37 degrees for 30 minutes with the lid side up. The plates were then flipped lid side down and incubated at 37 degrees overnight.
  
  
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<b><u>CPEC reaction:</u></b>
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1. Each reaction contained:<br>
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  0.5 uL of Phusion High-Fidelity DNA Polymerase (Thermofisher) - added last<br>
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10 uL of 5x Phusion reaction buffer<br>
 +
2.5 uL of forward oligo<br>
 +
  2.5 uL of reverse oligo<br>
 +
1 uL of 10 uM dNTPs<br>
 +
1 ng of template DNA<br>
 +
2. Thermocycler settings:<br>
 +
- 30 seconds at 98 degrees - 1 cycle<br>
 +
- 10 seconds at 98 degrees     \<br>
 +
- 30 seconds at 55 degrees       # of cylces should exceed # of assembly pieces<br>
 +
- 15 seconds per kb at 72 degrees/<br>
 +
- 10 minutes at 72 degrees - 1 cycle<br>
 +
The PCR products of both the insert and the linearized plasmid were then combined in equimolar amounts and a CPEC was done on the combination. <br>
  
Testing testing testing
 
  
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<b><u>Transformation:</u></b>
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5 uL of each of the CPEC reactions were then loaded onto Millipore (type VSWP) drop dialysis film with 0.025 μm on ~40 uL of ultra-pure Milli-Q water for desalting over the course of one hour. 2 uL of dialyzed DNA along with 30 uL of electrocompetent DH10B cells for half and BLR cells for the other half were transferred to Bio Rad 0.1 cm gap Gene Pulser cuvettes for electroporation and kept chilled. Electroporation was conducted with a Bio-Rad MicroPulser Electroporator set to pulse on the bacteria setting. After electroporation, the cells were immediately transferred to 200 L of TB and placed in a 37° incubator to recover for an hour. The cells were then added to LB agar plates with kanamycin and spread with ~10 sterile glass beads per plate. The beads were then dumped into 70% ethanol and the plates were allowed to dry in the incubator at 37 degrees for 30 minutes with the lid side up. The plates were then flipped lid side down and incubated at 37 degrees overnight.
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<b><u>Checking for colonies and sequencing:</u></b>
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The resulting plates yielded very few colonies (1-3) for the BLR strains that did have colonies and the DH10B strains with too many to count. A colony from each plate was selected and grown overnight in 2 mL culture tubes with kanamycin. The cultures were then miniprepped with the QIAprep Spin Miniprep Kit and sent to Eurofins for sequencing. The colonies from the BLR strains showed recircularized plasmid while the DH10B strains showed proper gene insertion.
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Testing testing testing
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<b><u>Transformation for Expression:</u></b>
 +
<br><br>
 +
<span class="read-more-target">
  
<p>
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The leftover miniprepped plasmid that was sent for sequencing and confirmed to contain the genes of choice were then loaded onto Millipore (type VSWP) drop dialysis film with 0.025 μm on ~40 uL of ultra-pure Milli-Q water for desalting over the course of one hour. 2 uL of dialyzed DNA along with 30 uL of electrocompetent BLR cells were transferred to Bio Rad 0.1 cm gap Gene Pulser cuvettes for electroporation and kept chilled. Electroporation was conducted with a Bio-Rad MicroPulser Electroporator set to pulse on the bacteria setting. After electroporation, the cells were immediately transferred to 200 L of TB and placed in a 37° incubator to recover for an hour. The cells were then added to LB agar plates with kanamycin and spread with ~10 sterile glass beads per plate. The beads were then dumped into 70% ethanol and the plates were allowed to dry in the incubator at 37 degrees for 30 minutes with the lid side up. The plates were then flipped lid side down and incubated at 37 degrees overnight.
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<b><u>Checking for colonies and glycerol stock for culture growth:</u></b>
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<br><br>
 +
<span class="read-more-target">
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Colonies were seen on all of the plates and contained too many to count. Using a pipet tip, one colony from each of the plates were selected and mixed into 2 mL of TB with kanamycin for overnight growth. The cells, after ~16 hours had 2 mL of 50% glycerol stock solution added to achieve 4 mL total and were aliquoted out into 1.5 mL eppendorf microfuge tubes containing 1 mL of 25% glycerol cultures. These glycerol stock cells were kept in a -80 degree freezer until needed for expression growth cultures.
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<b><u>Cell growth for expression:</u></b>
 +
<br><br>
 +
<span class="read-more-target">
 +
 
 +
Using 50 mL falcon tubes, 25 mL of TB containing kanamycin were poured into each tube. Using the glycerol stock cells on ice, a pipet tip was used to obtain a fleck of frozen cultures and carefully mixed for each of the designated tubes. The cultures were shaken for ~24 hours at 300 rpm in 37 degrees.
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<b><u>Expression and Protein Purification:</u></b>
 +
<br><br>
 +
<span class="read-more-target">
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 +
Autoinduction media for n + 1 samples<br>
 +
25 mL * (n + 1) samples<br>
 +
 
 +
1000x Trace metals mix<br>
 +
1000x Kanamycin<br>
 +
1000x MgSO4<br>
 +
50x 50:52<br>
 +
20x NPS<br>
 +
TB to reach final volume<br><br>
 +
 
 +
 
 +
To express protein:<br><br>
 +
 
 +
A colony was grown overnight in 25 mL TB containing kanamycin in 50 mL falcon tubes at 37C at 300 rpm. The resulting cell cultures were then spun down in a centrifuge at 4700 rpm for 10 min, supernatant was removed, and the pellets were resuspended in 25 mL autoinduction media. These cultures were then allowed to express for 24-36 hours at 18 degrees at 300 rpm. Cells were spun down and supernatant was removed. Cells were stored in -20 until the protein was needed. Protein was always purified the same day they were assayed to assure quality.
 +
 
 +
 
 +
Protein Purification: <br><br>
 +
 
 +
-Dispense 500 uL aliquots of lysis solution to 2 mL microcentrifuge tubes<br>
 +
- Resuspend cells in 500 uL wash buffer and vortex<br>
 +
- Transfer 1 mL resuspension to tubes with lysis solution<br>
 +
- Seal put on rocker for 20 minutes<br>
 +
- Spin in micro centrifuge at 14,700 rpm for 20 minutes<br>
 +
- While spinning, prepare micro columns in rack over waste collector<br>
 +
- Add 100 uL Co2+ or Ni2+ to each column<br>
 +
- Add 1 column volume (1 mL) wash buffer <br>
 +
- Once 20 minute spin is complete, load clarified supernatant to column<br>
 +
- Wash 6 times with 500 uL wash buffer<br>
 +
- Transfer columns to fresh 2 mL microcentrifuge tubes<br>
 +
- Elute with 100 uL elution buffer, wait 2-3 min<br>
 +
- Transfer columns to fresh 2 mL microcentrifuge tubes<br>
 +
- Elute with 100 uL elution buffer, wait 2-3 min<br>
 +
- Transfer columns to fresh 2 mL microcentrifuge tubes<br>
 +
- Elute with 100 uL elution buffer, wait 2-3 min<br>
 +
- Briefly spin so all protein elutes in final fraction<br>
 +
- Check concentration of each elution from A280<br>
 +
- Check purity from SDS-PAGE gel<br>
 +
<br>
 +
For SDS-PAGE gel:<br>
 +
4x denaturing buffer: Add 100 uL beta-mercapto ethanol to 900 uL Laemmli sample bufer in fume hood. <br>
 +
<br>
 +
Mix 12 uL of protein with 4 uL denaturing buffer in PCR tubes and heat in thermocycler at 100C for 10 min. Load 12 uL of denatured protein onto gels. Run at 200 V for 20 min. <br>
 +
<br>
 +
<b><u>Enzyme activity assay with natural substrate analog crotonyl CoA</b></u><br>
 +
<br>
 +
in 96 well plate:<br>
 +
<br>
 +
Each well had 50 uL enzyme<br>
 +
25 uL 100 uM NADH (final concentration)<br>
 +
25 uL 100 uM crotonyl CoA (final concentration)<br>
 +
<br>
 +
Negative control:<br>
 +
25 uL 100 uM NADH (final concentration)<br>
 +
25 uL 100 uM crotonyl CoA (final concentration)<br>
 +
50 uL protein buffer<br>
 +
<br>
 +
Reactions were measured spectrophotometrically in either a Biotek plate reader or manually in cuvettes in the Io Rodeo colorimeter by measuring the decrease in NADH at 340 and/or 365 nm. Reading were taken every minute over an hour. <br>
 +
<br>
 +
To find the minimum amount of enzyme needed to still see enzyme activity, each enzyme was diluted 10 fold up to a million fold in PCR tubes. Assay was run same as just described.<br>
 +
<br>
 +
Enzyme activity assay with alternative substrates: <br>
 +
<br>
 +
5 mM substrates used on max concentration of enzyme that elutes <br>
 +
500 uM NADH<br>
 +
<br>
 +
<br>
 +
<b><u>To measure enzyme inhibition by triclosan</b></u><br>
 +
<br>
 +
Assayed contained 10 uM, 50 nM, and 1 nM triclosan with ~2 nM Enzyme diluted approximately 10,000x. 100 uM NADH, 100 uM Crotonyl CoA<br>
 +
<br>
 +
NADH oxidation was measured spectrophotometrically at either 340 nm or 365 nm every minute over the course of an hour<br>
 +
<br>
 +
Measurements were made in the IORodeo spectrophotometer using the IORodeo provided GUI "colorimeter-4". 700µL of reaction were loaded into a UV-clear cuvette and measured manually at 365 nm every 20 mins.
 +
 
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<b><u>Buffers:</u></b>
 +
<br><br>
 +
<span class="read-more-target">
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 +
Lysis Solution:<br>
 +
<br>
 +
250 uL Bugbuster * (n+1) samples <br>
 +
350 uL wash buffer *(n+1) samples<br>
 +
1 mg dry lysis mix * (n+1) samples<br>
 +
 
 +
PBS: 10x (pH 7.4)(1L)<br>
 +
-80g Nacl<br>
 +
-2.0g KCl<br>
 +
-14.4g Na2HPO4<br>
 +
-2.4g KH2PO4<br>
 +
*adjust pH to 7.4<br>
 +
<br>
 +
Wash Buffer: (1x PBS, pH 7.4, 10mM Imidazole)(2L)<br>
 +
-200mL 10x PBS<br>
 +
-20mL Imidazole<br>
 +
-Milli-Q water up to 2L<br>
 +
*adjust pH if necessary<br>
 +
<br>
 +
Elution Buffer: (pH 7.5)(1L)<br>
 +
-11.9g HEPES<br>
 +
-8.7g NaCl<br>
 +
-7.31g EDTA<br>
 +
-Milli-Q water up to 1L<br>
 +
*adjust pH to 7.50<br>
 +
<br>
 +
Wash Buffer (1X PBS, pH 7.4, 10mM Imidazole) (2L)<br>
 +
200mL 10X PBS<br>
 +
20mL 1M imidazole<br>
 +
*bring up to 2L with ddH20 and adjust pH if necessary<br>
 +
<br>
 +
Elution Buffer (1X PBS, pH 7.4, 200mM Imidazole) (1L)<br>
 +
100mL 10X PBS<br>
 +
200mL 1M imidazole<br>
 +
*bring up to 1L with ddH20 and adjust pH if necessary <br>
 +
<br>
 +
20X NPS – 1L<br>
 +
Water 900mL<br>
 +
(NH4)2SO4 66g<br>
 +
KH2PO4 (monobasic) 136g<br>
 +
Na2HPO4 142g<br>
 +
<br>
 +
1000x Trace Metals Mix - 100ml <br>
 +
Compound Amount<br>
 +
Water 36ml<br>
 +
0.1M FeCl3-6H2O 50ml<br>
 +
1M CaCl2 2ml<br>
 +
1M MnCl2-4H2O 1ml<br>
 +
1M ZnSO4-7H2O 1ml<br>
 +
0.2M CoCl2-6H2O 1ml<br>
 +
0.1M CuCl2-H2O 2ml<br>
 +
0.2M NiCl2-6H2O 1ml<br>
 +
0.1M Na2MoO4-2H2O 2ml<br>
 +
0.1M Na2SeO3-5H20 2ml<br>
 +
0.1M H3BO3 2ml<br>
 +
*SLOWLY ADD SOLIDS WHILE STIRRING, After dissolved sterile filter!<br>
 +
<br>
 +
1M MgSO4 - 300ml <br>
 +
Compound Amount<br>
 +
water 300ml<br>
 +
MgSO4 74g <br>
 +
After dissolved, sterile filter <br>
 +
<br>
 +
50x 5052 - 1L <br>
 +
5052 = 0.5% glycerol, 0.05% glucose, 0.2% alpha-lactose <br>
 +
Compound Amount<br>
 +
water 730ml<br>
 +
Glycerol 250g<br>
 +
Glucose 25g<br>
 +
a- lactose (D+) 100g <br>
 +
Can speed up dissolving by heating in the microwave… don’t get too hot or boil… <br>
 +
Sterile Filter <br>
 +
Store in refrigerator.<br>
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Latest revision as of 05:04, 21 December 2015



In the Laboratory
At the beginning of summer everyone on our team took the online UC Fundamentals of Laboratory Safety course. This course described correct use of personal protective equipment and engineering safety controls within the lab to reduce risks associated with each lab space. The course also covered methods involved in chemical safety including the identification of chemical hazards through the use of Material Safety and Data Sheets (MSDS) and pictograms as well as proper chemical storage and disposal. In addition to this general safety course, we were also trained on the laboratory specific hazards by the lab managers of the three spaces that we worked in.

Since our project involved use of some proteins found in known pathogens, we decided to synthesize the genes we were interested in through IDT to express in laboratory E. coli. These safety precautions ensured that we 1. did not culture pathogenic organisms in the laboratory and 2. the proteins we expressed were not toxic or pathogenic. To ensure that our engineered strains did not exit the lab, we killed all of our cultures with 10% (v/v) bleach before disposal. We also did not transport any engineered strains outside of the lab, reducing the risk of release.

Our project involved the use of an array of small molecules. To ensure safety, we followed recommendations in the MSDS for each of the chemicals that we used. When ordering our library of alternate FabI substrates, we made sure not to order chemicals that were acutely toxic. For the chemicals we tested, we followed the MSDS recommendations for proper use of personal protective equipment including, wearing eye protection, lab coats, and wearing rubbing gloves, and engineering controls such as a working in the fume hood to eliminate the risk of chemical exposure.

The inhibitor we are detecting, triclosan, is toxic, so we created a triclosan waste container to avoid dumping triclosan down the drain. The proper way to dispose of this container is to give it to UC Davis’s Environmental Health and Safety Services

In the Real World
The use of laboratory expressed enzymes in the environment is defined in The Coordinated Framework for Regulation of Biotechnology . Our device and its associated biosensor must be approved through this process before use in the real world. Additionally, for application in the real world setting, future screening of alternate substrates would require us to look for substrates that are non hazardous to use outside of the laboratory setting. The handling of known concentrations of triclosan must be handled with proper PPE outside of the lab. See above for triclosan disposal.

        ↥


Preparation of DNA for Cloning
Originally, our cloning method was to be Gibson assembly. We ordered our 8 genes with 5’ and 3’ gibson overhangs from IDT. Once received, we rehydrated the genes:

1. Centrifuge for 3-5 seconds at >3000 x g to pellet at the bottom
2. Add 20 uL TE buffer or Milli-Q water for a final concentration of 10ng/uL
3. Briefly vortex and centrifuge
4. Store at -20 degrees for up to 24 months with TE buffer or 1 month with dH2O

We made four 50 mL and four 2 mL overnight cultures of DH10B containing pET29b+ vector for insertion with kanamycin resistance selection. The grown 50 mL cultures were then transferred to 50 mL falcon tubes and spun down to pellet at 4000 x g for 10 minutes. We then followed the protocol included in the Invitrogen MaxiPrep kit used. The results gave an average of 1.93 ng/uL, which is below the threshold for accurate concentration measurement for the Biotek Epoch spectrophotometer with the Take3 Microvolume plate. This also showed that the results yielded next to no DNA for the MaxiPrep and decided to go forth with a MiniPrep on the four 2 mL cultures using the Invitrogen MiniPrep protocol provided with the kit. The results yielded an average of 90 ng/uL which is above the 60-80 ng/uL concentration needed for the restriction digestion.

Double digestion:

We used the NEB double digest finder to select which buffer and protocol to use for our reaction. Since we used NdeI and EcoRI as our restriction sites, the highest activity without having star activity was NEBuffer 3.1 with 100% activity in NdeI and 50% activity in EcoRI. 50 uL double digest reactions were made of the miniprep, containing 1 uL of each restriction enzyme, 5 uL of the 10x 3.1 NEBuffer, and the remaining 43 uL of our miniprepped plasmid and allowed to incubate at 37 degrees for one hour.

Gel separation and purification:

Each 50 uL sample received 10 uL of NEB 6x loading dye and was run on a 1% agarose gel alongside uncut plasmid and O’Generuler 1kb Plus (Thermofisher). The gel was analysed on a [name of gel machine] and the lines of linear plasmid were cut out and placed in premeasured 2 mL eppendorf micro centrifuge tubes and weighed again. Gel purification was completed with the QIAprep Gel Extraction Kit, following the protocol provided with the kit. The average concentration of the DNA from the gel purification was about 14 ng/uL, much less than wanted for the next step.

Gibson assembly:

5 uL gibson reaction were performed with 2.5 uL of gibson master mix and with rest having equimolar amounts of linear vector and gene. The reactions were placed in a 50 degree dry bath and left to react for 1 hour.

Transformation:

The 5 uL of DNA from the Gibson reactions were then loaded onto Millipore (type VSWP) drop dialysis film with 0.025 μm on ~40 uL of ultra-pure Milli-Q water for desalting over the course of one hour. 2 uL of dialyzed DNA along with 30 uL of electrocompetent BLR cells were transferred to Bio Rad 0.1 cm gap Gene Pulser cuvettes for electroporation and kept chilled. Electroporation was conducted with a Bio-Rad MicroPulser Electroporator set to pulse on the bacteria setting. After electroporation, the cells were immediately transferred to 200 L of TB and placed in a 37° incubator to recover for an hour. The cells were then added to LB agar plates with kanamycin and spread with ~10 sterile glass beads per plate. The beads were then dumped into 70% ethanol and the plates were allowed to dry in the incubator at 37 degrees for 30 minutes with the lid side up. The plates were then flipped lid side down and incubated at 37 degrees overnight.

CPEC reaction:

1. Each reaction contained:
0.5 uL of Phusion High-Fidelity DNA Polymerase (Thermofisher) - added last
10 uL of 5x Phusion reaction buffer
2.5 uL of forward oligo
2.5 uL of reverse oligo
1 uL of 10 uM dNTPs
1 ng of template DNA
2. Thermocycler settings:
- 30 seconds at 98 degrees - 1 cycle
- 10 seconds at 98 degrees \
- 30 seconds at 55 degrees # of cylces should exceed # of assembly pieces
- 15 seconds per kb at 72 degrees/
- 10 minutes at 72 degrees - 1 cycle
The PCR products of both the insert and the linearized plasmid were then combined in equimolar amounts and a CPEC was done on the combination.

Transformation:

5 uL of each of the CPEC reactions were then loaded onto Millipore (type VSWP) drop dialysis film with 0.025 μm on ~40 uL of ultra-pure Milli-Q water for desalting over the course of one hour. 2 uL of dialyzed DNA along with 30 uL of electrocompetent DH10B cells for half and BLR cells for the other half were transferred to Bio Rad 0.1 cm gap Gene Pulser cuvettes for electroporation and kept chilled. Electroporation was conducted with a Bio-Rad MicroPulser Electroporator set to pulse on the bacteria setting. After electroporation, the cells were immediately transferred to 200 L of TB and placed in a 37° incubator to recover for an hour. The cells were then added to LB agar plates with kanamycin and spread with ~10 sterile glass beads per plate. The beads were then dumped into 70% ethanol and the plates were allowed to dry in the incubator at 37 degrees for 30 minutes with the lid side up. The plates were then flipped lid side down and incubated at 37 degrees overnight.

Checking for colonies and sequencing:

The resulting plates yielded very few colonies (1-3) for the BLR strains that did have colonies and the DH10B strains with too many to count. A colony from each plate was selected and grown overnight in 2 mL culture tubes with kanamycin. The cultures were then miniprepped with the QIAprep Spin Miniprep Kit and sent to Eurofins for sequencing. The colonies from the BLR strains showed recircularized plasmid while the DH10B strains showed proper gene insertion.

Transformation for Expression:

The leftover miniprepped plasmid that was sent for sequencing and confirmed to contain the genes of choice were then loaded onto Millipore (type VSWP) drop dialysis film with 0.025 μm on ~40 uL of ultra-pure Milli-Q water for desalting over the course of one hour. 2 uL of dialyzed DNA along with 30 uL of electrocompetent BLR cells were transferred to Bio Rad 0.1 cm gap Gene Pulser cuvettes for electroporation and kept chilled. Electroporation was conducted with a Bio-Rad MicroPulser Electroporator set to pulse on the bacteria setting. After electroporation, the cells were immediately transferred to 200 L of TB and placed in a 37° incubator to recover for an hour. The cells were then added to LB agar plates with kanamycin and spread with ~10 sterile glass beads per plate. The beads were then dumped into 70% ethanol and the plates were allowed to dry in the incubator at 37 degrees for 30 minutes with the lid side up. The plates were then flipped lid side down and incubated at 37 degrees overnight.

Checking for colonies and glycerol stock for culture growth:

Colonies were seen on all of the plates and contained too many to count. Using a pipet tip, one colony from each of the plates were selected and mixed into 2 mL of TB with kanamycin for overnight growth. The cells, after ~16 hours had 2 mL of 50% glycerol stock solution added to achieve 4 mL total and were aliquoted out into 1.5 mL eppendorf microfuge tubes containing 1 mL of 25% glycerol cultures. These glycerol stock cells were kept in a -80 degree freezer until needed for expression growth cultures.

Cell growth for expression:

Using 50 mL falcon tubes, 25 mL of TB containing kanamycin were poured into each tube. Using the glycerol stock cells on ice, a pipet tip was used to obtain a fleck of frozen cultures and carefully mixed for each of the designated tubes. The cultures were shaken for ~24 hours at 300 rpm in 37 degrees.

Expression and Protein Purification:

Autoinduction media for n + 1 samples
25 mL * (n + 1) samples
1000x Trace metals mix
1000x Kanamycin
1000x MgSO4
50x 50:52
20x NPS
TB to reach final volume

To express protein:

A colony was grown overnight in 25 mL TB containing kanamycin in 50 mL falcon tubes at 37C at 300 rpm. The resulting cell cultures were then spun down in a centrifuge at 4700 rpm for 10 min, supernatant was removed, and the pellets were resuspended in 25 mL autoinduction media. These cultures were then allowed to express for 24-36 hours at 18 degrees at 300 rpm. Cells were spun down and supernatant was removed. Cells were stored in -20 until the protein was needed. Protein was always purified the same day they were assayed to assure quality. Protein Purification:

-Dispense 500 uL aliquots of lysis solution to 2 mL microcentrifuge tubes
- Resuspend cells in 500 uL wash buffer and vortex
- Transfer 1 mL resuspension to tubes with lysis solution
- Seal put on rocker for 20 minutes
- Spin in micro centrifuge at 14,700 rpm for 20 minutes
- While spinning, prepare micro columns in rack over waste collector
- Add 100 uL Co2+ or Ni2+ to each column
- Add 1 column volume (1 mL) wash buffer
- Once 20 minute spin is complete, load clarified supernatant to column
- Wash 6 times with 500 uL wash buffer
- Transfer columns to fresh 2 mL microcentrifuge tubes
- Elute with 100 uL elution buffer, wait 2-3 min
- Transfer columns to fresh 2 mL microcentrifuge tubes
- Elute with 100 uL elution buffer, wait 2-3 min
- Transfer columns to fresh 2 mL microcentrifuge tubes
- Elute with 100 uL elution buffer, wait 2-3 min
- Briefly spin so all protein elutes in final fraction
- Check concentration of each elution from A280
- Check purity from SDS-PAGE gel

For SDS-PAGE gel:
4x denaturing buffer: Add 100 uL beta-mercapto ethanol to 900 uL Laemmli sample bufer in fume hood.

Mix 12 uL of protein with 4 uL denaturing buffer in PCR tubes and heat in thermocycler at 100C for 10 min. Load 12 uL of denatured protein onto gels. Run at 200 V for 20 min.

Enzyme activity assay with natural substrate analog crotonyl CoA

in 96 well plate:

Each well had 50 uL enzyme
25 uL 100 uM NADH (final concentration)
25 uL 100 uM crotonyl CoA (final concentration)

Negative control:
25 uL 100 uM NADH (final concentration)
25 uL 100 uM crotonyl CoA (final concentration)
50 uL protein buffer

Reactions were measured spectrophotometrically in either a Biotek plate reader or manually in cuvettes in the Io Rodeo colorimeter by measuring the decrease in NADH at 340 and/or 365 nm. Reading were taken every minute over an hour.

To find the minimum amount of enzyme needed to still see enzyme activity, each enzyme was diluted 10 fold up to a million fold in PCR tubes. Assay was run same as just described.

Enzyme activity assay with alternative substrates:

5 mM substrates used on max concentration of enzyme that elutes
500 uM NADH


To measure enzyme inhibition by triclosan

Assayed contained 10 uM, 50 nM, and 1 nM triclosan with ~2 nM Enzyme diluted approximately 10,000x. 100 uM NADH, 100 uM Crotonyl CoA

NADH oxidation was measured spectrophotometrically at either 340 nm or 365 nm every minute over the course of an hour

Measurements were made in the IORodeo spectrophotometer using the IORodeo provided GUI "colorimeter-4". 700µL of reaction were loaded into a UV-clear cuvette and measured manually at 365 nm every 20 mins.

Buffers:

Lysis Solution:

250 uL Bugbuster * (n+1) samples
350 uL wash buffer *(n+1) samples
1 mg dry lysis mix * (n+1) samples
PBS: 10x (pH 7.4)(1L)
-80g Nacl
-2.0g KCl
-14.4g Na2HPO4
-2.4g KH2PO4
*adjust pH to 7.4

Wash Buffer: (1x PBS, pH 7.4, 10mM Imidazole)(2L)
-200mL 10x PBS
-20mL Imidazole
-Milli-Q water up to 2L
*adjust pH if necessary

Elution Buffer: (pH 7.5)(1L)
-11.9g HEPES
-8.7g NaCl
-7.31g EDTA
-Milli-Q water up to 1L
*adjust pH to 7.50

Wash Buffer (1X PBS, pH 7.4, 10mM Imidazole) (2L)
200mL 10X PBS
20mL 1M imidazole
*bring up to 2L with ddH20 and adjust pH if necessary

Elution Buffer (1X PBS, pH 7.4, 200mM Imidazole) (1L)
100mL 10X PBS
200mL 1M imidazole
*bring up to 1L with ddH20 and adjust pH if necessary

20X NPS – 1L
Water 900mL
(NH4)2SO4 66g
KH2PO4 (monobasic) 136g
Na2HPO4 142g

1000x Trace Metals Mix - 100ml
Compound Amount
Water 36ml
0.1M FeCl3-6H2O 50ml
1M CaCl2 2ml
1M MnCl2-4H2O 1ml
1M ZnSO4-7H2O 1ml
0.2M CoCl2-6H2O 1ml
0.1M CuCl2-H2O 2ml
0.2M NiCl2-6H2O 1ml
0.1M Na2MoO4-2H2O 2ml
0.1M Na2SeO3-5H20 2ml
0.1M H3BO3 2ml
*SLOWLY ADD SOLIDS WHILE STIRRING, After dissolved sterile filter!

1M MgSO4 - 300ml
Compound Amount
water 300ml
MgSO4 74g
After dissolved, sterile filter

50x 5052 - 1L
5052 = 0.5% glycerol, 0.05% glucose, 0.2% alpha-lactose
Compound Amount
water 730ml
Glycerol 250g
Glucose 25g
a- lactose (D+) 100g
Can speed up dissolving by heating in the microwave… don’t get too hot or boil…
Sterile Filter
Store in refrigerator.


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