This protocol describes the process to extract and derivatize amino acids (AAs) from biologic material so that they are suitable for quantification by GC-FID and isotopic analysis by GC-C-irMS. The method is based on that used by Chikaraishi et al. (2007) and Rachel Jeffery’s at University of Liverpool, UK, and is a slight modification of that published in Metges et al. (1996) combined with elements from Popp et al. (2007). The method involves esterification by isopropanol and acetyl chloride followed by derivatization using toluene and pivaloyl chloride. This method is unsuitable for carbon isotopic analysis. Norleucine is added to each sample as an internal quantification and isotopic standard. This protocol is designed for a run of 9 samples over two days.
This method uses numerous chemicals that are considered hazardous for flammability and toxicity. Therefore, most of the work must be conducted in the fume hood. Toxic chemicals include toluene, isopropanol (a.k.a., IPA), methylene chloride (dichloromethane or DCM), acetyl chloride, and pivaloyl chloride. Toluene and IPA can affect the respiratory and central nervous systems with repeat and prolonged exposure. DCM is a suspected carcinogen. Acetyl chloride reacts violently with water and can burn exposed skin. All of the above chemicals are flammable. Concentrated hydrochloric acid (HCl) is used when preparing reagents. When working with all chemicals always wear a minimum of nitrile gloves and eye protection. Work in the fume hood when dealing with organic solvents and acids. Familiarize yourself with the MSDS for all chemicals prior to starting this protocol.
0.01 N HCl — Work in the fume hood when using concentrated HCl. Using 1000 $\mu$L pipetter add 830 $\mu$L 12 N HCl to a 1 L volumetric flask filled ~2/3 with Nanopure water. Fill to mark with Nanopure water using a squirt bottle. Mix and transfer to the designated 1 L glass bottle.
0.2 N HCl — Work in the fume hood when using concentrated HCl. Using a 10 mL glass pipette, add 4.2 mL 12 N HCl to a 250 mL volumetric flask filled ~2/3 with Nanopure water. Fill to mark with Nanopure water using a squirt bottle. Mix and transfer to the designated 500 mL glass bottle.
4:1 IPA:acetyl chloride — Working in the fume hood, measure 400 mL 2-propanol (IPA) using 500 mL graduated cylinder. Transfer to a clean 1 L beaker. Prepare a large ice bath. Add a total of 100 mL acetyl chloride to the IPA in ~5 mL increments. Be careful to bring acetyl chloride in contact with water; results in a highly exothermic reaction. Store in the designated 500 mL media bottle with white Teflon lined cap.
4:1 Toluene: pivaloyl chloride — Working in the fume hood, measure 400 mL toluene using a 500 mL graduated cylinder. Transfer to the designated 500 mL glass bottle using an ashed glass funnel. Slowly add the entire 100 mL bottle of pivaloyl chloride (a.k.a. trimethylacetyl chloride) using the glass funnel.
3:2 n-hexanes/DCM — Working in the fume hood, measure 300 mL n-hexanes using a 500 mL graduated cylinder. Transfer to the designated 500 mL glass bottle using an ashed glass funnel. Next measure and add 200 mL DCM (a.k.a. methylene chloride) using the same graduated cylinder and glass funnel.
Dried DCM — Working in the fume hood, decant 100 mL DCM (a.k.a. methylene chloride) from supplier bottle into designated bottle. Add ~50 g of room temperature 3A molecular sieve beads. DCM will be dry in 48 hours (plan ahead). Activating the molecular sieves: Pre-weigh the desired amount of beads into an ashed beaker. Bake at 350 $^\circ$C in the muffle furnace for 4 hours. Remove while hot (use tongs) and place in desiccator until the cool to room temperature.
*Potential stopping point: can be stored long-term (<12 months) in freezer after adding 200 $\mu$L 0.2 N HCl and flushing with N~2~ or Ar. *
Label an empty jug with a temporary hazardous waste label that reads “Halogenated Waste”. Equip with a plastic funnel and stopper. All halogen-containing chemical waste should go in this container. Halogen wastes include DCM, chloroform, and TFAA. Non-halogenated waste can go in a similarly labeled “Non-halogenated Waste” jug.
When the halogenated waste jug is 4/5 full, submit an Online Chemical Waste Collection request. Replace hazardous waste label with one that represent the approximate contents. For this protocol, an example would be:
Chemical | Composition ------------------------ | ------------- hexanes | ~25 % methylene chloride (DCM) | ~25 % hydrochloric acid | ~25 % water | ~25 %
The glass cuvettes and used Pasteur pipettes can be disposed of in an appropriately labeled “Lab Glass” box. See the section on Non-Hazardous Laboratory Glass and Plastic at the UW EH&S website here.
Reacti-Vials, septa and caps should be cleaned following the HEEL Glass- & Plastic-ware Cleaning protocol. The glass syringe(s) and their needle(s) should be cleaned by rinsing with 2 mL water, 2 mL methanol, and 2 mL water prior to being returned to the drawer. Used glass tubes and Pasteur pipettes should be left in beakers in the hood until solvents have been fully evaporated then disposed of in Lab Glass. Syringe filters go in the trash.
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Chikaraishi Y, Ogawa NO, Kashiyama Y, Takano Y, Suga H, Tomitani A, et al. Determination of aquatic food-web structure based on compound-specific nitrogen isotopic composition of amino acids. Limnol Oceanogr Methods. 2009;7: 740–750. doi: 10.4319/lom.2009.7.740.
Macko, S.A., M.E. Uhle, M.H. Engel, and V. Andrusevich. 1997. Stable nitrogen isotope analysis of amino acid enantiomers by gas chromatography combustion/isotope ratio mass spectrometry. Anal. Chem. 69: 926–929.
Metges CC, Petzke K, Hennig U. Gas chromatography/combustion/isotope ratio mass spectrometric comparison of N -acetyl- and N-pivaloyl amino acid esters to measure 15N isotopic abundances in physiological samples: a pilot study on amino acid synthesis in the upper gastro-intestinal tract of minipigs. J Mass Spectrom. 1996;31: 367–376. doi: 10.1002/(SICI)1096-9888(199604)31:4<367::AID-JMS310>3.0.CO;2-V. pmid:8799283
Popp, B. N., and 7 others. 2007. Insight into the trophic ecology of yellowfin tuna, Thunnus albacares, from compound-specific nitrogen isotope analysis of proteinaceous amino acids, p. 173–190. In T.D. Dawson and R.T.W. Siegwolf [eds.], Stable isotopes as Indicators of Ecological Change. Terrestrial Ecology Series.
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