Attachment F - MIL-PRF-87930C w-Amendment 1 H70.pdf

MIL-PRF-87930C

w/AMENDMENT 1 26 June 2021

SUPERSEDING

MIL-PRF-87930C

15 June 2018

PERFORMANCE SPECIFICATION

PROPELLANT, HYDRAZINE – WATER

(70 % HYDRAZINE – 30 % WATER)

This specification is approved for use by all Departments and Agencies of the Department of Defense.

AMSC N/A FSC 9135

DISTRIBUTION STATEMENT A. Approved for public release; distribution is unlimited.

METRIC

Comments, suggestions, or questions on this document should be addressed to AFPET/PTPS, 2430 C Street, Bldg. 70, Area B, Wright-Patterson AFB OH 45433-7631 or e-mailed to AFPET.PTPS@us.af.mil. Since contact information can change, you may want to verify the currency of this address information using the ASSIST Online database at https://assist.dla.mil.

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CONTENTS

PARAGRAPH PAGE

1 SCOPE

1.1 Scope

2 APPLICABLE DOCUMENTS

2.1 General

2.2 Government documents

2.2.1 Specifications, standards, and handbooks

2.3 Non-Government publications

2.4 Order of precedence

3 REQUIREMENTS

3.1 Chemical and physical properties

3.2 Limiting values

3.3 Filter

3.4 Qualitative

4 VERIFICATION

4.1 Classification of inspections

4.2 Conformance inspection

4.2.1 Individual tests

4.2.2 Sampling tests

4.2.2.1 Sampling plan

4.2.2.1.1 Sample

4.2.3 Rejection

4.3 Test methods

4.3.1 Examination of product

4.3.2 Hydrazine assay and water

4.3.3 Particulate

4.3.4 Chloride

4.3.5 Aniline

4.3.6 Iron

4.3.7 Non-volatile residue

4.3.8 Carbon dioxide

4.3.9 Carbonaceous material

5 PACKAGING

5.1 Packaging

6 NOTES

6.1 Intended use

6.2 Acquisition requirements

6.3 Safety data sheet (SDS)

6.4 Subject term (key word) listing

6.5 Amendment notations

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TABLE

I Chemical and physical properties A-1 GC parameters G-1 GC parameters

FIGURE

E-1 NVR apparatus F-1 CO2 apparatus

APPENDIX

A Hydrazine assay and water B Chloride C Aniline D Iron E Non-volatile residue F Carbon dioxide G Carbonaceous material

CONCLUDING MATERIAL

1. SCOPE

1.1 Scope. This specification covers the requirements for hydrazine - water propellant blend, 70 percent hydrazine and 30 percent water by weight (H-70).

2. APPLICABLE DOCUMENTS

2.1 General. The documents listed in this section are specified in sections 3 and 4 of this specification. This section does not include documents cited in other sections of this specification or recommended for additional information or as examples. While every effort has been made to ensure the completeness of this list, document users are cautioned that they must meet all specified requirements of documents cited in sections 3 and 4 of this specification, whether or not they are listed.

2.2 Government documents.

2.2.1 Specifications, standards, and handbooks. The following specifications, standards and handbooks form a part of this document to the extent specified herein. Unless otherwise specified, the issues of these documents are those cited in the solicitation or contract.

DEPARTMENT OF DEFENSE SPECIFICATIONS

MIL-PRF-25604 Propellant, uns-Dimethylhydrazine

MIL-PRF-26536 Propellant, Hydrazine

MIL-PRF-27401 Propellant Pressurizing Agent, Nitrogen

MIL-PRF-27404 Propellant, Monomethylhydrazine

MIL-PRF-27407 Propellant Pressurizing Agent, Helium

(Copies of these documents are available online at https://quicksearch.dla.mil.)

2.3 Non-Government publications. The following documents form a part of this document to the extent specified herein. Unless otherwise specified, the issues of these documents are those cited in the solicitation or contract.

ASTM INTERNATIONAL

ASTM D1068 Standard Test Methods for Iron in Water

ASTM D1976 Standard Test Method for Elements in Water by Inductively- Coupled Plasma Atomic Emission Spectroscopy

ASTM D2276 Standard Test Method for Particulate Contaminant in Aviation Fuel by Line Sampling

ASTM E29 Standard Practice for Using Significant Digits in Test Data to Determine Conformance with Specifications

ASTM E394 Standard Test Method for Iron in Trace Quantities Using the 1,10-Phenanthroline Method

(Copies of these documents are available online at https://www.astm.org.)

2.4 Order of precedence. Unless otherwise noted herein or in the contract, in the event of a conflict between the text of this document and the references cited herein, the text of this document takes precedence. Nothing in this document, however, supersedes applicable laws and regulations unless a specific exemption has been obtained.

3. REQUIREMENTS

3.1 Chemical and physical properties. The chemical and physical properties of the propellant mixture shall conform to those listed in Table I when tested in accordance with (IAW) the applicable test methods.

3.2 Limiting values. The following applies to all specified limits in this specification: For purposes of determining conformance with these requirements, an observed value or a calculated value shall be rounded off “to the nearest unit” in the last right-hand digit used in expressing the specification limit according to the Rounding Method of ASTM E29.

3.3 Filter. A filter with a rating of at least 2 micrometer (µm) nominal and 10 µm absolute rating shall be installed between the manufacturer’s plant system and the container to be filled for delivery.

3.4 Qualitative. The propellant shall be colorless, homogeneous liquid when examined visually by transmitted light.

4. VERIFICATION

4.1 Classification of inspections. The inspection requirements specified herein are classified as conformance inspections (4.2).

4.2 Conformance inspection. The conformance inspection shall consist of the following:

a. Individual tests (see 4.2.1)

b. Sampling tests (see 4.2.2)

4.2.1 Individual tests. The propellant shall be subjected to the following test as described under 4.3:

a. Examination of product (see 4.3.1)

4.2.2 Sampling tests. The propellant shall be selected according to 4.2.2.1 and subjected to the tests indicated in Table I as described under 4.3.

4.2.2.1 Sampling plan. Unless otherwise specified (6.2), each filled shipping container shall be considered a lot and shall be sampled.

TABLE I. Chemical and physical properties.

Properties Limits Test Paragraph

Hydrazine wt%. 69 - 70 4.3.2

Water wt% 30 - 31 4.3.2

Particulate mg/L, max. 1.0 4.3.3

Chloride mg/kg (ppmw), max. 5 4.3.4

Aniline wt%, max. 0.40 4.3.5

Iron mg/kg (ppmw), max. 20 4.3.6

Non-volatile residue mg/L, max. 40 4.3.7

Carbon dioxide(1) wt%, max. 0.003 4.3.8

Carbonaceous material (Total of OVCM(2) + OCM(3).), wt%, max.

0.02

4.3.9

NOTES:

(1) Determination of carbon dioxide (CO2) content must be performed before all other analyses to prevent further absorption of CO2.

(2) OVCM – Other volatile carbonaceous material as the total of unsymmetrical dimethylhydrazine (UDMH), isopropyl alcohol (IPA), and monomethylhydrazine (MMH).

(3) OCM – Other carbonaceous material consisting of any impurity providing a positive FID response ahead of and trailing the hydrazine peak excluding OVCM and aniline.

4.2.2.1.1 Sample. A sample consists of not less than 1500 mL of propellant. Unless otherwise specified, conformance tests shall be made on the sample of propellant taken directly from the shipping container. When required, the sample shall be forwarded to a laboratory designated by the procuring activity for subjection to the quality conformance tests specified herein. The clear glass narrow mouth bottle intended for sampling shall be specially cleaned and handled according to the procedure described in ASTM D2276 Section 10 (Preparation of Flushing Apparatus) with the exception listed in 4.3.3d. The bottle must be dried with filtered nitrogen (N2) after cleaning. The sampling of drums and other shipping containers shall be conducted in such a manner that neither the contents of the container nor the sample is exposed to the atmosphere. The use of a plastic bag purged with N2 to cover the container is mandatory.

4.2.3 Rejection. When any sample of the propellant tested IAW 4.3 fails to conform to the requirements specified herein, the entire lot represented by the sample shall be rejected.

4.3 Test methods.

4.3.1 Examination of product. The propellant shall be visually examined to ensure that the material conforms to 3.4. The examination shall be conducted after a representative aliquot of the sample has been transferred to a clear glass vessel and compared to the same type vessel containing the same volume of purified water.

4.3.2 Hydrazine assay and water. The hydrazine (N2H4) and water (H2O) content of the propellant shall be determined by the gas chromatographic (GC) method described in Appendix A.

4.3.3 Particulate. The propellant sample shall be tested gravimetrically for particulate contamination in accordance with ASTM D2276, with the following exceptions:

a. Mix the sample thoroughly without exposure to air. Immediately pour no less than 250 mL of the sample into a clean graduated cylinder.

b. Pass the sample aliquot through a Mitex disc polytetrafluoroethylene (PTFE) hydrophobic, 5 µm, 47 mm diameter, white filter or equivalent.

c. The oven temperature shall be set at 70 °C (158 °F).

d. Filtered American Chemical Society (ACS) reagent grade isopropyl alcohol shall be used for rinsing the sample bottle and filter holder instead of petroleum ether specified in ASTM D2276. Use a suitable solvent resistant filter disc with an absolute rating of at least 1.0 µm. Wet the filter with the filtered isopropyl alcohol prior to filtering the sample.

4.3.4 Chloride. The chloride (Cl-) content of the propellant shall be determined by one of the methods described in Appendix B. In case of a dispute, the specific ion electrode method (B.2.1) shall be the referee.

4.3.5 Aniline. The aniline (C6H5NH2) content of the propellant shall be determined by one of the methods found in Appendix C. In case of a dispute, the spectrophotometric method (C.2.1) shall be the referee.

4.3.6 Iron. The iron (Fe) content of the propellant shall be determined by one of the methods described in Appendix D. In case of a dispute, the inductively-coupled plasma method (D.2.1) shall be the referee.

4.3.7 Non-volatile residue. The non-volatile residue (NVR) of the propellant shall be determined in duplicate by one of the methods described in Appendix E. In case of a dispute, the hot plate method (E.2.1) shall be the referee.

4.3.8 Carbon dioxide. The carbon dioxide (CO2) content of the propellant shall be determined by the method described in Appendix F.

4.3.9 Carbonaceous material. Other volatile carbonaceous material (OVCM) + other carbonaceous material (OCM) shall be determined by the gas chromatographic method found in Appendix G.

5. PACKAGING

5.1 Packaging. For acquisition purposes, the packaging requirements shall be as specified in the contract or order (see 6.2). When packaging of materiel is to be performed by DoD or in-house contractor personnel, these personnel need to contact the responsible packaging activity to ascertain packaging requirements. Packaging requirements are maintained by the Inventory Control Point’s packaging activities within the Military Service or Defense Agency, or within the military service’s system commands. Packaging data retrieval is available from the managing Military Department’s or Defense Agency’s automated packaging files, CD-ROM products, or by contacting the responsible packaging activity.

6. NOTES

(This section contains information of a general or explanatory nature that may be helpful, but is not mandatory.)

6.1 Intended use. The propellant described by this specification is intended for use as fuel for gas generators.

6.2 Acquisition requirements. Acquisition documents must specify the following:

a. Title, number, and date of this specification.

b. Quantity by weight in pounds (avoirdupois).

c. When test methods are other than those specified (4.3).

d. When a different sampling plan is required (4.2.2.1).

e. Packaging requirements (5.1).

6.3 Safety Data Sheet. Contracting officers will identify those activities that require copies of completed Safety Data Sheet (SDS) prepared in accordance with the 29CFR1910.1200.

6.4 Subject term (key word) listing.

Fuel

Gas generator

6.5 Amendment notations. The margins of this specification are marked with vertical lines to indicate modifications generated by this amendment. This was done as a convenience only and the Government assumes no liability whatsoever for any inaccuracies in these notations. Bidders and contractors are cautioned to evaluate the requirements of this document based on the entire content irrespective of the marginal notations

APPENDIX A

HYDRAZINE ASSAY AND WATER

A.1 SCOPE

A.1.1 Scope. This Appendix describes a gas chromatographic (GC) method for the determination of hydrazine and water content in the sample. This Appendix is a mandatory part of the specification. The information contained herein is intended for compliance.

A.2 METHOD

A.2.1 Gas chromatographic method – capillary column.

A.2.1.1 Procedure. A 60 or 30 meters (m) x 0.53 millimeters (mm), 1.00 µm film thickness DB-Wax column, a thermal conductivity detector (TCD), with a split injector and an ultra-inert, deactivated, glass wool packed split liner shall be used. Table A-1 provides a summary of the critical operating parameters. These parameters may vary depending on GC system, detector brands, and column length and may be adjusted to optimize component resolution.

Allow the instrument to stabilize, condition the column by adding a couple of injections to the sample sequence. Perform check runs by processing three consecutive injections of 1 microliter (µL) of sample.

The checks must meet the quality control criteria in A.2.1.4.

TABLE A-1. GC parameters.

PARAMETER CONDITION

Injector Port Temp. 150 °C Injection Mode Split injection Sample Volume 1 µL Split Ratio 50:1 Carrier Gas He Control Flow 10 mL/min Control Mode Flow TCD Detector Temp. 210 °C Equilibration Time 2.00 min Initial Temp.(T0) 60 °C Initial Time (t0) 3.00 min Rate (1) 10 °C/min Final Temp. (Tf1) 100 °C Final Time (tf1) 0.00 min Rate (2) 20 °C/min Final Temp. (Tf2) 185 °C Final Time (tf2) 3.75 min

The elution order of possible sample components is as follows:

Air > ammonia > water > hydrazine > aniline

A.2.1.2 Standard preparation.

Determine the hydrazine and water content of a sample of high purity hydrazine (HPH) using procedures in the latest revision of MIL-PRF-26536. Use this analyzed hydrazine (N2H4) to prepare a mixture with purified water which is approximately (~) 70% hydrazine and 30% water by mass (~ 0.3 mL H2O for each 0.7 mL of N2H4).

1. Weigh an empty volatile organic analysis (VOA) vial with its septa cap (or equivalent) to the nearest 0.1 mg and record the weight.

2. Add 3 mL purified water to the vial, cap and weigh to the nearest 0.1 mg. Subtract the weight of the vial from the weight obtained to determine the weight of the purified water added.

3. Follow the same procedure as above with the addition of 7 mL of HPH to the vial, cap, and allow to cool prior to weighing to the nearest 0.1 mg.

4. Mix the solution thoroughly.

A.2.1.3 Calculations.

%𝑁𝑁2𝐻𝐻4 =

𝑊𝑊𝑊𝑊𝐻𝐻𝐻𝐻𝐻𝐻 × % 𝑁𝑁2𝐻𝐻4 (𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓 𝐴𝐴. 2.1.2)

𝑇𝑇𝑓𝑓𝑊𝑊𝑇𝑇𝑇𝑇 𝑊𝑊𝑊𝑊𝑊𝑊𝑊𝑊ℎ𝑊𝑊

% 𝐻𝐻2𝑂𝑂 =

𝑊𝑊𝑊𝑊𝐻𝐻2𝑂𝑂 + �𝑊𝑊𝑊𝑊𝐻𝐻𝐻𝐻𝐻𝐻 × % 𝐻𝐻2𝑂𝑂 (𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓 𝐴𝐴. 2.1.2)

100 �

𝑇𝑇𝑓𝑓𝑊𝑊𝑇𝑇𝑇𝑇 𝑊𝑊𝑊𝑊𝑊𝑊𝑊𝑊ℎ𝑊𝑊

× 100

A.2.1.4 Quality control. Verify the HPH analysis falls within 10% of historical values. Analyze the H-70 prepared standard with the samples to be tested. The following performance criteria must be met for fuel purity analysis, GC replicate analyses (3 consecutive) H₂O content RSDa ≤ 1 %

a. RSD = Standard Deviation * 100% / Mean

A.2.1.5 Equipment and reagents. The following equipment and reagents shall apply as test conditions of A.2.

A.2.1.5.1 Equipment:

(1) Gas chromatograph equipped with a TCD and a split injector.

(2) Agilent ChemStation or equivalent.

(3) A 60 or 30 m x 0.53 mm ID and 1.00 µm film thickness DB-wax capillary column (Agilent P/Ns 125-7062 or 125-7032 respectively) or equivalent.

(4) Ultra-inert deactivated liner, split, straight, glass wool.

(5) No bleed septa.

(6) Analytical balance calibrated to 0.0001 g.

A.2.1.5.2 Reagents:

(1) High purity hydrazine (HPH) conforming to MIL-PRF-26536.

(2) Helium conforming to MIL-PRF-27407.

APPENDIX B

CHLORIDE

B.1 SCOPE

B.1.1 Scope. This Appendix describes three methods for the determination of chloride content of the H-70. This Appendix is a mandatory part of the specification. The information contained herein is intended for compliance.

B.2 METHODS

B.2.1 Specific ion electrode method.

B.2.1.1 Procedure. Rinse the H-70 NVR in one vessel from 4.3.7 with a 5 mL aliquot of 1N sulfuric acid (H2SO4). Briefly stir and heat the liquid to boiling and cover with an inverted watch glass to prevent the condensate from escaping. Transfer the solution to a 25 mL volumetric flask. Rinse the vessel with a second 5 mL aliquot of acid followed by one 5 mL aliquot of purified water. Combine the aliquots in the 25 mL volumetric flask and add two to three drops of bromocresol green indicator.

Dropwise titrate the contents of the flask to a green endpoint with 1N sodium hydroxide (NaOH) and dilute to the mark with purified water. Mix the solution and transfer ~ 10 mL to a 25 mL beaker. Immerse the electrodes in the sample solution and record the millivolt (mV) reading. Compare the mV reading from the sample to a calibration curve prepared from chloride standards and record the concentration (ppmv) of the sample.

B.2.1.2 Calibration. Prepare an acid matrix blank and a minimum of four calibration standards to bracket the expected chloride (Cl-) concentration range in the samples by adding one drop of 0.1N H2SO4 to 50 mL of purified water in 100 mL volumetric flasks, and combining appropriate aliquots of a 1000 ppm Cl- standard. Add 2-3 drops of bromocresol green indicator to each of the five flasks and if necessary adjust with 0.1N H2SO4 or 0.1N NaOH to obtain a green endpoint. Dilute each to the mark with purified water and mix the solutions thoroughly. Pour enough of the standards into a small beaker to cover the electrode tips and record the resulting mV reading. Prepare a calibration curve of Cl- concentration to mV and use this to determine Cl- concentration in the sample.

B.2.1.3 Calculation. Calculate the chloride content of the H-70 using the following formula:

𝐶𝐶𝑇𝑇−𝑝𝑝𝑝𝑝𝑓𝑓𝑝𝑝 =

� 𝐶𝐶𝑇𝑇−𝑝𝑝𝑝𝑝𝑝𝑝𝑝𝑝�(𝑉𝑉𝑑𝑑)

�𝑉𝑉𝑝𝑝�(𝜌𝜌)

where, 𝐶𝐶𝑇𝑇−𝑝𝑝𝑝𝑝𝑝𝑝𝑝𝑝 = Chloride content of the sample solution from the calibration curve.

𝑉𝑉𝑑𝑑 = Final dilution volume taken from NVR in mL.

𝑉𝑉𝑝𝑝 = Volume of H-70 used in the NVR analysis in mL.

𝜌𝜌 = Density of H-70 (1.03 g/mL @ 20 C°).

B.2.1.4 Reagents and equipment. The following shall apply as test conditions of B.2.1:

B.2.1.4.1 Reagents.

a. Purified water free of interfering substances; the water is considered free of interfering substances if a 100 mL sample used to dissolve 0.1 g of silver nitrate shows no turbidity after standing in the dark for 24 hours. The purified water as described in this paragraph shall be used throughout the procedure.

b. Standard sodium chloride (NaCl) solution, 1 mL = 1.00 mg Cl- ; weigh 1.648 g of dry NaCl into a 1 liter (L) volumetric flask. Dilute to the mark with purified water. Transfer the thoroughly mixed solution to a clean polyethylene bottle for storage. A 1000 mg/L (ppmv) chloride standard may be commercially obtained; must be certified.

c. 1N H2SO4; prepare by pouring 29 mL of ACS reagent grade concentrated H2SO4 into 300 mL of purified water contained in a 1000 mL volumetric flask. Cool the solution to room temperature, dilute to the mark with the purified water, and mix thoroughly. Transfer the solution to a plastic bottle. A 1N H2SO4 solution may be commercially obtained.

d. 1N NaOH; prepare by dissolving 40 g of ACS reagent grade, low carbonate, NaOH in 300 mL of purified water contained in a 1000 mL volumetric flask. Cool the solution to room temperature, dilute to the mark with the purified water, and mix thoroughly. Transfer the solution to a plastic bottle and protect from prolonged exposure to the atmosphere. A 1N NaOH solution may be commercially obtained.

e. Bromocresol green indicator; 1% aqueous solution. Use purified water.

B.2.1.4.2 Equipment.

a. Chloride electrode – solid state Orion 9417BN, or equivalent.

b. Reference electrode – Orion 900200 Sure-Flow® double junction with 1M potassium nitrate (KNO3) outer compartment filling solution, or equivalent.

c. pH/millivolt meter, Orion 420A+ or equivalent.

B.2.2 Colorimetric method.

B.2.2.1 Procedure. Add to the H-70 NVR in one vessel from 4.3.7 five milliliters of ferric alum indicator and transfer to a 100 mL volumetric flask. Rinse the vessel with three 5 mL purified water aliquots and combine into the volumetric. Set samples aside.

Prepare a calibration blank and at a minimum two standards to bracket the expected Cl-concentration in the samples in 100 mL volumetric flasks, and add 5 mL of ferric alum indicator. Add

2.5 mL of mercuric thiocyanate solution to each volumetric flask, samples and standards, and dilute to the mark with purified water. Mix the solutions thoroughly and allow to stand in darkness for 15 – 30 min.

Analyze in a UV-Vis spectrophotometer at 460 nm, at the wavelength recommended by the instrument manufacturer, or at that which provides the highest sensitivity using 5 cm cells. Use the blank to set the instrument to zero absorbance and determine the absorbances of standards and samples. Prepare a calibration curve of absorbance vs. concentration and determine the Cl- concentration in the samples.

The calibration correlation coefficient shall be ≥ 0.999.

B.2.2.2 Calculation. Calculate the chloride content of the H-70 using the formula in B.2.1.3.

B.2.2.3 Reagents and equipment. The following shall apply as test conditions of B.2.2:

B.2.2.3.1 Reagents.

a. Purified water of 18 M-ohm or greater resistivity.

b. Ferric alum indicator, Volhard (oxidation reduction indicator) – Dissolve 10 g of ferric ammonium sulfate dodecahydrate (FeNH4(SO4)2•12H2O) ACS reagent grade in ~ 50 mL of purified water.

Add 10 mL of ACS reagent grade nitric acid (HNO3), and dilute to 100 mL with purified water. Ferric alum indicator solution may be commercially obtained.

c. Mercuric thiocyanate, 4.17 g/L in methanol for chloride determination (commercially available).

d. Chloride standard, 1000 mg/L (may be commercially obtained; must be certified).

B.2.2.3.2 Equipment. UV-Vis Spectrophotometer, double beam, equipped with 5 cm cells.

B.2.3 Ion chromatography (IC) method.

B.2.3.1 Procedure. To the H-70 NVR in one vessel from 4.3.7, add an appropriate amount of purified water (18 M-ohm or greater resistivity) such that the instrument reading is within the instrument calibration curve. Gently warm the mixture for 3 to 5 minutes (min) ensuring the water contacts the surface area of the vessel that the fuel mixture came in contact with. Allow the solution to cool. Transfer a representative aliquot into an appropriate labeled IC vial and analyze.

B.2.3.2 Calibration. Prepare a series of calibration standards in purified water to bracket the expected concentration range of the samples by combining appropriate aliquots of a certified Cl- or multi-element IC anion standard solution. Prepare and/or commercially obtain a mid-range check standard from a different stock standard source to verify the calibration (Initial Calibration Verification, ICV).

Prepare a calibration curve by plotting the instrument response (integrated peak area) vs. the Cl- standard concentration to determine the sample concentration. Alternatively, use the quantitation method recommended by the instrument manufacturer.

B.2.3.3 Quality control.

(1) The calibration correlation coefficient must be ≥ 0.995.

(2) Analyze the ICV every 10 samples to validate the instrument calibration. The ICV should fall within ± 10% of its concentration.

B.2.3.4 Calculation. Calculate the chloride content of the H-70 using the formula in B.2.1.3. If the dilution factor is accounted for by the instrument adjust the formula accordingly.

B.2.3.5 Reagents.

a. Purified water of 18 M-ohm or greater resistivity.

b. Eluent mix stock, approximately equivalent to 3.5 mM sodium carbonate/1.0 mM sodium bicarbonate – If the IC system is equipped with an automatic eluent generator, follow the owner’s manual instructions. Otherwise, combine an appropriate aliquot of a commercially available IC sodium carbonate/sodium bicarbonate concentrate in a volumetric flask containing purified water, fill to the mark, and mix thoroughly. If preparing the mix in-house, dissolve 370.9608 mg ACS reagent grade sodium carbonate and 84.007 mg sodium bicarbonate in a 1 L volumetric flask, and proceed as above.

Eluent generator systems may use alternate eluents as long as they are paired with a column that can effectively quantitate 1 ppmw Cl-.

c. Chloride or multi-element IC anion standard solution (must be certified).

B.2.3.6 Equipment. The ion chromatograph must have the following components:

(1) Eluant pump capable of delivering 1 - 5 mL/min of eluent at a nominal flow and pressure specified by the instrument manufacturer.

(2) Sample pump capable of filling a sample loop with no resistance.

(3) Sample loop capable of delivering 5 to 100 µl of sample to the analytical column.

(4) An ion exchange column suitable for resolving chloride.

(5) A suppressor device.

(6) Conductivity cell.

(7) Data acquisition device.

(8) Five decimal place analytical balance (required only if eluent mix is prepared in-house).

APPENDIX C

ANILINE

C.1 SCOPE

C.1.1 Scope. This Appendix describes two methods for the determination of aniline content of the H-70. This Appendix is a mandatory part of the specification. The information contained herein is intended for compliance.

C.2 METHODS

C.2.1 Spectrophotometric method.

C.2.1.1 Procedure. Pipet or syringe 0.25 mL (250 μL) of H-70 into a 25 mL volumetric flask containing ~ 15 mL of purified water, dilute to the mark with purified water, and mix the solution thoroughly. Fill two 1 cm pathlength silica spectrophotometer cells with purified water and place one in each position for sample and reference cells. Using the appropriate source and detector for the spectrophotometer set the absorbance to zero at 320 nm and scan the region between 320 and 240 nm.

If the baseline is relatively stable, the cells and purified water can be considered free from interfering substances. Exchange the water in the sample cell with the previously prepared sample, using several rinses with sample solution, and rescan the 320 to 240 nm region, first ensuring that the instrument is set to zero absorbance at 320 nm. Using a baseline under the aniline peak at 280 nm, measure, and record the net absorbance of the peak. Determine the aniline content of the sample by comparing the net absorbance obtained to a calibration curve of net absorbance vs. percent aniline.

C.2.1.2 Calibration. Pipet or syringe 0.500 mL (500 µL) of ACS reagent grade aniline into a 100 mL volumetric flask containing 50 mL of purified water. Shake the mixture to dissolve the aniline and dilute the solution to the mark with purified water. Mix the standard thoroughly. This standard is equivalent to 0.51 wt%. Prepare a series of calibration standards in the aniline range expected to find in the samples. Determine the net absorbance of standards versus purified water in the same manner as with the sample. Plot net absorbance vs. percent aniline and draw a curve through the points. A check standard shall be prepared fresh daily to check the calibration standards. If the check standard falls outside of ± 5% of the expected value, fresh calibration standards shall be prepared and the calibration check repeated until the required accuracy is demonstrated.

C.2.1.3 Equipment. Spectrophotometer, double beam, ultra violet, narrow band width, recording, equipped with 1 cm silica cells.

C.2.2 Gas chromatographic method – Stabilwax®-DB (carbonaceous material determination).

C.2.2.1 Procedure. Follow the procedure described in G.2.1.1.

C.2.2.2 Calibration. Follow the calibration procedure as described in G.2.1.2. Add ~ 2.0 mL ACS reagent grade aniline to the OVCM stock standard solution, and prepare the working standard as described in G.2.1.2.2.

C.2.2.3 Calculation. Calculate the aniline concentration (by weight) using the equations in G.2.1.3.

APPENDIX D

IRON

D.1 SCOPE

D.1.1 Scope. This Appendix describes three methods for the determination of iron content of the H-70. This Appendix is a mandatory part of the specification. The information contained herein is intended for compliance.

D.2 METHODS

D.2.1 Inductively-coupled argon plasma atomic emission spectrometry. For each instrument interference effects must be evaluated, corrected as applicable (ASTM D1976), and instrument performance validated. The argon gas supply must have a purity of 99.99% or better. Choose the iron wavelength recommended by the instrument manufacturer or that which provides the highest sensitivity (most commonly used is 259.940 nm).

D.2.1.1 Procedure. Rinse the H-70 NVR in one vessel from 4.3.7 as follows: Add 5 mL of 5N HNO3 to the vessel and place on a hot plate. Heat the mixture to near boiling, maneuver the beakers so the acid contacts the surface area of the glass that the fuel mixture came in contact with, and maintain at that temperature for three to five minutes. Allow the solution to cool and transfer to a 100 mL volumetric flask. Rinse the vessel at least three times with 5 mL aliquots of 0.1N HNO3 combining all of the rinses in the volumetric flask. Dilute to the mark with purified water and mix thoroughly.

NOTE: Sulfuric acid may be substituted for nitric acid (nitric acid preferred) in D.2.1.1 provided standards and samples are matrix matched (applies to all of D.2).

D.2.1.2 Calibration. Prepare an acid matrix blank and an Fe standard in a 0.1N HNO3 acidified purified water solution to bracket the expected concentration range of the samples by combining an appropriate aliquot of a certified Fe stock standard. Prepare a mid-range check standard, from a different stock standard source to verify the calibration. Determine the concentration from the calibration curve prepared from the Fe standard using the acid matrix blank as the zero point, and record the Fe concentration of the sample.

D.2.1.3 Quality control. The instrumental drift shall be checked using the acid matrix blank and standard at the beginning of each run, at least every ten readings during the run, and at the end of the run. The blank shall read ≤ the detection limit and the standard shall fall within ± 10% of the standard value. If the recovery of the analyte falls outside of the required control limits, the source of the problem must be identified and resolved before continuing with the analyses.

D.2.1.4 Calculation. Calculate the iron content of the H-70 using the following formula:

𝐹𝐹𝑊𝑊 𝑝𝑝𝑝𝑝𝑓𝑓𝑝𝑝 =

�𝐹𝐹𝑊𝑊 𝑝𝑝𝑝𝑝𝑝𝑝𝑝𝑝 �(𝑉𝑉𝑑𝑑)

�𝑉𝑉𝑝𝑝�(𝜌𝜌)

where:

𝐹𝐹𝑊𝑊𝑝𝑝𝑝𝑝𝑝𝑝𝑝𝑝 = The iron content of the sample solution from the calibration curve.

𝑉𝑉𝑑𝑑 = Final dilution volume taken from NVR in mL.

𝑉𝑉𝑝𝑝 = Volume of H-70 used in the NVR analysis in mL.

𝜌𝜌 = Density of H-70 (1.03 g/mL @ 20 °C).

D.2.1.5 Reagents and equipment. The following shall apply as test conditions of D.2.1.

D.2.1.5.1 Reagents.

a. Purified water of 18 M-ohm or greater resistivity.

b. Iron standards, certified, commercially obtained solutions.

c. Nitric or sulfuric acid, concentrated, suitable for trace metal analysis.

D.2.1.5.2 Equipment

a. Hot plate – controllable heat.

b. Inductively-coupled argon plasma atomic emission spectrometer (ICP-AES).

D.2.2 Atomic absorption.

D.2.2.1 Procedure. Prepare the sample solution in the same manner as described in D.2.1.1.

Determine the absorbance of the sample at an Fe wavelength closest to 2480 Å on a suitable atomic absorption spectrophotometer, after setting the instrument to zero absorbance, with 0.1N HNO3.

Compare the results to a calibration curve prepared from the Fe standards and record the Fe concentration of the sample.

D.2.2.2 Calibration. Prepare a minimum of three calibration standards to bracket the expected Fe concentration range of the samples and a mid-range check standard to verify the calibration in the same manner as described in D.2.1.2. After setting the instrument to zero absorbance with 0.1N HNO3, determine the absorbance of the calibration standards and check standard. Prepare a calibration curve of absorbance vs. Fe concentration.

D.2.2.3 Calculation. Calculate the iron content of the H-70 using the formula in D.2.1.4.

D.2.2.4 Quality control. Follow the guidelines described in ASTM D1068 Method A with the following exceptions:

a. The mid-range standard from D.2.1.2 shall be used as the laboratory control sample.

D.2.2.5 Reagents and equipment. The following equipment shall apply as test conditions of D.2.2.

D.2.2.5.1 Reagents. Same as in D.2.1.5.1.

D.2.2.5.2 Equipment. Atomic absorption spectrophotometer with an iron hollow cathode lamp.

D.2.3 Colorimetric method.

D.2.3.1 Procedure. ASTM E394 shall be followed with the following exceptions:

a. Add 5 mL of the ammonium acetate-acetic acid buffer solution to each empty 100 mL volumetric flasks (for standards and samples) and set aside.

b. Dissolve the residue of one vessel from 4.3.7 by adding 1 mL of concentrated acid (HNO3 or H2SO4 as applicable), and carefully adding 50 mL purified water. Mix thoroughly.

c. Add 1 mL of concentrated acid (HNO3 or H2SO4 as applicable), and 50 mL purified water to at least four empty 150 mL evaporating dishes for the standards.

NOTE: Make sure the solution is thoroughly mixed after each component addition.

d. Add the 2 mL of hydroxylamine hydrochloride and the 5 mL of 1,10-phenanthroline as described in the method.

e. Add enough sodium acetate solution to bring the pH of the mixture to between pH 3 and pH 4 while swirling (add ~ 20 mL initially and then continue adding drop wise until desired pH is reached).

f. Transfer the solutions to their respective 100 mL volumetric flask from step (a) above, dilute to the mark, and mix thoroughly. Allow the flasks to set at room temperature in the dark for a minimum of 15 min.

g. Determine the Fe concentrations from the calibration curve prepared from the Fe standards;

the correlation coefficient shall be ≥ 0.990.

D.2.3.2 Calculation. Calculate the iron content of the H-70 using the formula in D.2.1.4.

D.2.3.3 Reagents. The following reagents are in addition to those reagents listed in ASTM E394,

a. Sodium acetate solution. Dissolve 200 g CH3COONa•3H2O in a 1 L volumetric flask in 700 mL of purified water and dilute to the mark. An equivalent solution may be obtained commercially or prepared from anhydrous sodium acetate.

b. Nitric or sulfuric acid, concentrated, suitable for trace metal analysis.

APPENDIX E

NON-VOLATILE RESIDUE

E.1 SCOPE

E.1.1 Scope. This Appendix describes two methods for the determination of non-volatile residue of the H-70. This Appendix is a mandatory part of the specification. The information contained herein is intended for compliance.

E.2 METHOD

E.2.1. Hot plate. This method involves the gradual evaporation of an H-70 sample on an explosion proof hot plate in a fume hood. The difference in weight before and after evaporation is calculated as NVR.

E.2.1.1 Procedure. Place three clean borosilicate glass or platinum evaporating dishes (latter preferred) in an oven at 110 °C for 30 min. Label one as a blank and the others as samples A1 and A2.

Remove evaporating dishes from the oven, place in a desiccator to cool for 15 min, and then place next to a five place balance long enough to equilibrate (usually around 30 min). Weigh each clean, dry evaporating dish to the nearest 0.0001 g until the weight remains constant to ± 0.1 mg. Record the sample evaporating dish weight as A1, A2 and the blank evaporating dish weight as C. Add 30 mL of purified water to each one of the evaporating dishes. Transfer 50 mL of the H-70 sample into the evaporating dishes marked A1 and A2. Place the evaporating dishes on a hot plate which is set to a temperature of 150 – 200 °C. Evaporate to dryness, but do not bake. Remove the evaporating dishes from the explosion-proof hot plate and place them in an oven set at 110 °C for 30 min. Remove dishes from the oven and place in a desiccator for 15 min to cool; then place them next to a five place balance long enough to equilibrate. Weigh each evaporating dish as before to a constant weight. Record the sample evaporating dish weight as B1, B2 and the blank evaporating weight as D.

Save the propellant residue/H-70 NVR for chloride (4.3.4) and iron (4.3.6) determinations.

E.2.1.2 Calculations. Calculate the nonvolatile residue of the H-70 as follows:

𝑁𝑁𝑉𝑉𝑁𝑁 𝑓𝑓𝑊𝑊 𝐿𝐿⁄ = �

(𝑊𝑊𝑊𝑊𝐵𝐵 − 𝑊𝑊𝑊𝑊𝐴𝐴) − (𝑊𝑊𝑊𝑊𝐷𝐷 −𝑊𝑊𝑊𝑊𝐶𝐶)

𝑆𝑆𝑇𝑇𝑓𝑓𝑝𝑝𝑇𝑇𝑊𝑊 𝑣𝑣𝑓𝑓𝑇𝑇𝑣𝑣𝑓𝑓𝑊𝑊𝑝𝑝𝑚𝑚

� × 106 where, 𝐴𝐴 = Weight of the sample evaporating dish, g.

𝐵𝐵 = Weight of the sample evaporating dish and residue, g.

𝐶𝐶 = Weight of blank evaporating dish, g.

𝐷𝐷 = Weight of blank and water residue, g.

NOTE

E.2.1.3 Equipment.

a. Hot plate, explosion proof.

b. High efficiency fume hood.

c. Five decimal place analytical balance (semi-micro balance).

E.2.2 Dropwise method.

E.2.2.1 Procedure. Clean the unassembled apparatus with detergent and rinse thoroughly with purified water. Dry the parts in an oven at 110 °C. Assemble the apparatus as shown in Figure E-1. Fill the water bath with purified water and turn on the heater. Adjust the water level of the bath to approximately one-half inch below the lowest fitting and mark this level on the bath. When the bath temperature reaches boiling, adjust the N2 purge to ~ 2 L/min and turn on the aspirator. With the sample delivery valve closed, the pressure in the apparatus should be below 30 mmHg. Open the sample delivery valve slowly to adjust the apparatus pressure to ~ 60 mmHg. Allow the apparatus to purge for ~ 5 min to remove traces of water. Remove the water bath and dry the outside of the residue vessel with a clean lintless tissue. Disconnect the aspirator from the apparatus and remove the residue vessel using a tissue to hold the vessel. Wipe the outside of the vessel carefully and place it near the analytical balance. After at least 20 min, accurately weigh the residue vessel until the weight remains constant to ± 0.1 mg. Record the weight. Reassemble the apparatus and close the sample delivery valve. Replace the water bath, adjust the water level to the mark, and heat the water to boiling. Transfer 100 mL of H-70 to the apparatus. With the N2 purge in place, turn on the water aspirator and reduce the apparatus pressure to less than 30 mmHg. Slowly open the sample delivery valve to admit H-70 to the residue vessel and adjust the flow such that the apparatus pressure does not exceed 60 mmHg (~ 2 drops per second). The quantity of H-70 in the residue vessel should not exceed 2 – 4 mL at the equilibrium evaporation rate. Adjust the sample delivery valve to maintain the evaporation pressure at less than 60 mmHg. After 100 mL of H-70 have been evaporated (~ 30 min), allow the residue vessel to purge for an additional 5 min to insure complete evaporation of volatile material. Remove the water bath, disconnect the aspirator, wipe the outside of the residue vessel, and remove it from the apparatus. Allow the residue vessel to stand near the analytical balance for at least 20 min before weighing. Weigh the residue vessel as above, and record the weight. To clean the residue vessel reflux 5 mL of 5N ACS grade H2SO4 (or equivalent) in the vessel for several minutes followed by several rinses of purified water.

The vessel may be dried as described above or by gently heating the vessel with a burner while purging with dry N2. Regardless of the drying method used, allow at least 20 min for the vessel to equilibrate to ambient temperature and humidity before weighing.

Save the propellant residue/H-70 NVR for chloride (4.3.4) and iron (4.3.6) determinations.

NOTE

A - GN2 J - Connector (Swagelok SS-400-7-2 or equivalent)

B - Water aspirator (glass or polyethylene) K - Sample delivery valve (Swagelok SS-ORM2 or equivalent)

C - Connector (polyethylene, separable) L - Syringe (100 mL glass with an 8 – 12 in PTFE needle).

D - Gauge (stainless steel, absolute pressure, 0 – 760 mmHg range)

M - Rod (PTFE or polyethylene, 1 4⁄ inch OD & a 1 16⁄ OD x

0.025 in wall tube inserted}

E - Adapter (Swagelok SS-8-TA-7-4 or equivalent) N - Reducer (Swagelok SS-400-R-8 or equivalent)

F - Union Tee (Swagelok SS-810-3 or equivalent; 2 ea.) O - Beaker (glass, 1000 mL capacity}

G - Pipette (100 mL, volumetric, borosilicate glass) P - Flask (25 mL volumetric, borosilicate glass)

H - Joints (borosilicate glass, spherical, 12/5, ball, socket and clamp)

Q - Hotplate (adjustable heat range}

I - PTFE Ferrules (Swagelok T-814-1, T-813-1, T-404-1, T-403-1, or equivalent)

NOTE: All fittings, stainless steel, Swagelok or equivalent.

FIGURE E-1. NVR apparatus.

E.2.2.2 Calculation. Calculate the non-volatile residue of the H-70 as follows:

𝑁𝑁𝑉𝑉𝑁𝑁 𝑓𝑓𝑊𝑊 𝐿𝐿⁄ = �

𝑊𝑊2 − 𝑊𝑊1

𝑉𝑉

� × 106 where:

𝑊𝑊1= Weight of clean vessel, g.

𝑊𝑊2= Weight of vessel and residue, g.

𝑉𝑉= Volume of sample used, mL.

Report the averaged result of duplicate NVR determinations.

E.2.2.3 Equipment. The following equipment shall apply as test conditions of E.2.2.

a. Components described in Figure E-1.

b. Tubing – polyethylene, ½ inch OD, borosilicate glass, ½ inch OD.

c. Clamps – hose, to fit ½ inch OD tube.

d. Five decimal place analytical balance (semi-micro balance).

APPENDIX F

CARBON DIOXIDE

F.1 SCOPE

F.1.1 Scope. This Appendix describes a method for the determination of carbon dioxide (CO2) content of the H-70. This Appendix is a mandatory part of the specification. The information contained herein is intended for compliance. Determination of CO2 content in H-70 must be performed before all other analyses to prevent further CO2 absorption.

F.2 METHOD

F.2.1 Determination of carbon dioxide by non-dispersive IR analysis. This method is to be utilized to determine the CO2 concentration in H-70 within a 10 – 100 mg/kg (ppmw) range. The sample of H-70 is injected into a solution of 30% phosphoric acid, which absorbs the hydrazine and ammonia.

Carbon dioxide is liberated from the acidic solution, swept out of the solution by a stream of N2 gas through a silica gel drying tube to remove water vapor, and measured by an infrared technique.

F.2.1.1 Calibration procedure.

a. Assemble the apparatus as shown in Figure F-1.

b. Adjust the flow of N2 purge gas according to manufacturer’s recommendation by use of the control valve and flow meter.

c. Calibrate the instrument using N2 gas at a flow rate of ~ 200 mL/min to set the instrument to zero and follow with a certified gas standard of ~ 100 ppm CO2 in N2 (span gas).

NOTE: The flow rate may need adjustment to obtain reproducible results but must remain constant throughout the analysis.

c. Add an appropriate amount of 30% phosphoric acid containing several drops of bromocresol green or methyl red indicator to the CO2 reaction flask, turn on the N2 gas to give vigorous, constant mixing. Allow the instrument to stabilize and adjust the zero.

F.2.1.2 Standardization.

If using a direct instrument response comparison (flow technique),

a. Prepare a working 100 ng/µL (ppmv) CO2 carbonate or bicarbonate standard. Using a gas-tight syringe, inject via the septum on the phosphoric acid unit, an appropriate amount of the prepared standard to achieve a reading of 100 ppm (~ 200 µL). Repeat the injection to ensure reproducibility is within ± 10 ppm and record.

b. Once reproducibility is verified, inject appropriate volumes of the working standard to obtain 50 ppm and 25 ppm (~ 100 and 50 µL respectively) and check for linearity.

If using a data acquisition device,

a. Inject via the septum, appropriate volumes (five) of the 100 ppmv working standard to bracket the expected concentration range of the samples using a gas-tight syringe (10 µL is equivalent to 1000 ng) and determine the absorbance counts of the standards.

b. Prepare a 5-point calibration curve of the number of nanograms vs. absorbance counts to determine the nanograms of CO2 in the samples. The calibration correlation coefficient shall be ≥ 0.995.

F.2.1.3 Sample analysis. Inject an appropriate volume of H-70 sample into the phosphoric acid reaction flask to obtain a reproducible result within the standards range. Record the reading from the infrared analyzer scale or data acquisition device (from the zero point). Perform the sample analysis in triplicate (verifying reproducibility) and use the average to determine the CO2 concentration.

F.2.1.3.1 Calculation. Determine the carbon dioxide content of the H-70 as follows,

a. Flow technique, 𝐶𝐶𝑂𝑂2 𝑊𝑊𝑊𝑊% =

�𝑆𝑆𝑊𝑊𝑆𝑆 𝑐𝑐𝑓𝑓𝑐𝑐𝑐𝑐𝑝𝑝𝑝𝑝𝑝𝑝𝑝𝑝��𝑆𝑆𝑊𝑊𝑆𝑆 𝑣𝑣𝑓𝑓𝑇𝑇𝜇𝜇𝑚𝑚�(𝑆𝑆𝑇𝑇𝑓𝑓𝑝𝑝𝑇𝑇𝑊𝑊 𝑓𝑓𝑊𝑊𝑟𝑟𝑝𝑝𝑓𝑓𝑐𝑐𝑟𝑟𝑊𝑊)

(𝑆𝑆𝑇𝑇𝑓𝑓𝑝𝑝𝑇𝑇𝑊𝑊 𝑣𝑣𝑓𝑓𝑇𝑇𝜇𝜇𝑚𝑚)(𝑆𝑆𝑊𝑊𝑆𝑆 𝑓𝑓𝑊𝑊𝑟𝑟𝑝𝑝𝑓𝑓𝑐𝑐𝑟𝑟𝑊𝑊)(𝜌𝜌)(1 × 104)

where, 𝜌𝜌 = Density of H-70, 1.03 g/mL @ 20 °C.

b. Data acquisition device, 𝐶𝐶𝑂𝑂2 𝑊𝑊𝑊𝑊% =

𝑆𝑆𝑇𝑇𝑓𝑓𝑝𝑝𝑇𝑇𝑊𝑊 𝐶𝐶𝑂𝑂2 𝑛𝑛𝑛𝑛

�𝑆𝑆𝑇𝑇𝑓𝑓𝑝𝑝𝑇𝑇𝑊𝑊 𝑣𝑣𝑓𝑓𝑇𝑇𝜇𝜇𝑚𝑚� (𝜌𝜌)(1 × 104)

𝜌𝜌 = Density of H-70, 1.03 g/mL @ 20 °C.

F.2.1.4 Reagents.

a. Purified water, CO2 free - Prepare by boiling purified water vigorously for 15 min or by bubbling N2 gas through it for several hours.

b. Carbon Dioxide Stock Solution, 1000 ppm - Dissolve 2.4083 g ACS reagent grade sodium carbonate or 1.9088 g ACS reagent grade sodium bicarbonate, previously dried for one hour at 100 °C, and dissolve in CO2 free purified water in a 1 L volumetric flask; fill to the mark and mix thoroughly.

Transfer 1 mL of this solution to a 10 mL volumetric flask, fill to the mark with CO2 free purified water to prepare a 100 ppm standard. Prepare fresh daily.

c. Phosphoric Acid, 30% by volume - Dilute 355 mL of 85% H3PO4 to 1 L with purified water.

Add enough indicator to this solution to readily determine when the acid solution is depleted.

d. Dry N2 gas supply.

e. Silica gel desiccant.

F.2.1.5 Equipment.

a. Non-dispersive infrared analyzer, Rosemount Analytical Model XStream-X2GP or equivalent.

b. Glass reaction tube with replaceable septum.

c. PTFE tubing.

d. Glass drying tube (should not be larger in outer diameter than the PTFE tubing used to transport the sample to the detector).

e. Needle valve to control flow into reaction tube.

f. Fittings to achieve air-tight connections.

g. Operating fume hood.

h. Gas-tight syringe.

i. Suitable data acquisition device.

A - Sparge gas inlet E - Trap for removing H2O

B - Needle valve F - Infrared analyzer

C - Reactor and phosphoric acid solution G - Recorder

D - Septum inlet for H-70 -

FIGURE F-1. CO2 apparatus.

APPENDIX G

CARBONACEOUS MATERIAL

G.1 SCOPE

G.1.1 Scope. This Appendix describes a method for the determination of carbonaceous material (other volatile carbonaceous material (OVCM) + other carbonaceous material (OCM)) content of the H-70. This Appendix is a mandatory part of the specification. The information contained herein is intended for compliance.

G.2 METHOD

G.2.1 Gas chromatographic method.

G.2.1.1 Procedure. A 60 m x 0.53 mm x 1.00 µm film thickness Stabilwax®-DB column, a flame ionization detector (FID), equipped with a split injector. An ultra-inert, deactivated, glass wool packed split liner shall be used. GC parameters for initial setup are listed in Table G-1. These parameters may vary depending on GC system and detector brands, and may be adjusted to provide adequate component resolution. The analysis requires ~ 15 min for elution of all components.

TABLE G-1. GC parameters.

PARAMETER CONDITION

Injector Port Temp. 175°C Injection Mode Split injection Sample Volume. 1 µL Split Ratio 4:1 Carrier Gas He Column Flow 10 mL/min Control Mode Flow FID Detector Port Temp. 210 °C Equilibration Time 2.00 min Initial Temp (T0) 60°C Initial Time (t0) 3.00 min Rate (1) 10 °C/min Final Temp. (Tf1) 100 °C Final Time (tf1) 0.00 min Rate (2) 20 °C/min Final Temp. (Tf2) 185 °C Final Time (tf2) 3.75 min

The elution order is as follows:

UDMH < IPA < MMH < hydrazine < aniline

G.2.1.2 Calibration. Prepare a standard stock solution, and a working standard of UDMH, IPA, and MMH in high purity hydrazine (HPH) meeting the latest revision of MIL-PRF-26536 as described in

G.2.1.2.1 and G.2.1.2.2 (deviations are allowed as long as the working standard is conducive to the analysis). Run an HPH blank and subtract the areas of UDMH, IPA, MMH and aniline (if detected) from the areas of the standard. The signal to noise ratio shall be such that it allows for the effective quantitation of at least 5 ppmw MMH. If any of the contaminants are found in an H-70 sample, analyze the standard and sample(s) in triplicate; the RSD ≤ 10%.

G.2.1.2.1 Standard stock solution.

1. Weigh a 200 mL borosilicate glass bottle with a PTFE cap to the nearest 0.0001g and record the weight.

2. Add ~ 98 mL of HPH to the tared bottle; cap and weigh to the nearest 0.0001g. Subtract the weight of the container from the weight obtained to determine the weight of HPH added.

3. Follow same procedure as above with the additions of ~ 100 µL UDMH, IPA, MMH, and ~ 2 mL aniline if applicable.

4. Mix the solution thoroughly and store it tightly sealed.

G.2.1.2.2 Working standard.

1. Weigh a suitable borosilicate glass container with a PTFE cap to the nearest 0.0001g. Record the weight.

2. Add an appropriate amount of HPH following the same procedure as in G.2.1.2.1.

3. Add a volume of the stock standard equivalent to a 1:10 dilution, and determine the weight added as above. Mix the solution thoroughly.

G.2.1.3 Calculations.

a. Standard stock solution:

𝐴𝐴𝑐𝑐𝑇𝑇𝑇𝑇𝐴𝐴𝑊𝑊𝑊𝑊 𝑝𝑝𝑝𝑝𝑓𝑓𝑝𝑝𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆 𝑆𝑆𝑆𝑆𝑑𝑑 =

𝑊𝑊𝑊𝑊𝑎𝑎𝑛𝑛𝑎𝑎𝑎𝑎𝑎𝑎𝑆𝑆𝑎𝑎 × 106

𝑊𝑊𝑊𝑊𝑇𝑇𝑆𝑆𝑆𝑆𝑎𝑎𝑎𝑎

𝑊𝑊𝑊𝑊𝑇𝑇𝑆𝑆𝑆𝑆𝑎𝑎𝑎𝑎 = 𝑊𝑊𝑊𝑊𝐻𝐻𝐻𝐻𝐻𝐻 + 𝑊𝑊𝑊𝑊𝑈𝑈𝐷𝐷𝑈𝑈𝐻𝐻 + 𝑊𝑊𝑊𝑊𝐼𝐼𝐻𝐻𝐴𝐴 + 𝑊𝑊𝑊𝑊𝑈𝑈𝑈𝑈𝐻𝐻 + 𝑊𝑊𝑊𝑊𝑎𝑎𝑛𝑛𝑎𝑎𝑎𝑎𝑎𝑎𝑛𝑛𝑎𝑎

b. Working standard:

𝐴𝐴𝑐𝑐𝑇𝑇𝑇𝑇𝐴𝐴𝑊𝑊𝑊𝑊 𝑝𝑝𝑝𝑝𝑓𝑓𝑝𝑝𝑊𝑊𝑆𝑆 𝑆𝑆𝑆𝑆𝑑𝑑 =

𝐴𝐴𝑐𝑐𝑇𝑇𝑇𝑇𝐴𝐴𝑊𝑊𝑊𝑊 𝑝𝑝𝑝𝑝𝑓𝑓𝑝𝑝𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆 𝑆𝑆𝑆𝑆𝑑𝑑 × 𝑊𝑊𝑊𝑊𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆 𝑆𝑆𝑆𝑆𝑑𝑑 𝑎𝑎𝑑𝑑𝑑𝑑𝑎𝑎𝑑𝑑

𝑊𝑊𝑊𝑊𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆𝑆 𝑆𝑆𝑆𝑆𝑑𝑑 𝑎𝑎𝑑𝑑𝑑𝑑𝑎𝑎𝑑𝑑 + 𝑊𝑊𝑊𝑊𝐻𝐻𝐻𝐻𝐻𝐻

c.. Sample calculation:

𝐴𝐴𝑐𝑐𝑇𝑇𝑇𝑇𝐴𝐴𝑊𝑊𝑊𝑊 𝑝𝑝𝑝𝑝𝑓𝑓𝑝𝑝𝑆𝑆𝑎𝑎𝑝𝑝𝑝𝑝𝑎𝑎𝑎𝑎 =

𝐴𝐴𝑐𝑐𝑇𝑇𝑇𝑇𝐴𝐴𝑊𝑊𝑊𝑊 𝑝𝑝𝑝𝑝𝑓𝑓𝑝𝑝𝑊𝑊𝑆𝑆 𝑆𝑆𝑆𝑆𝑑𝑑 × 𝐴𝐴𝑠𝑠

𝐴𝐴𝑎𝑎𝑛𝑛𝑎𝑎𝑎𝑎𝑎𝑎𝑆𝑆𝑎𝑎

𝐴𝐴𝑎𝑎𝑛𝑛𝑎𝑎𝑎𝑎𝑎𝑎𝑆𝑆𝑎𝑎 = The area of the analyte peak times its signal attenuation factor.

𝐴𝐴𝑠𝑠 = The area of the respective analyte in the sample times its signal attenuation factor.

Calculate OVCM in weight percent using the following equation, 𝑂𝑂𝑉𝑉𝐶𝐶𝑂𝑂 𝑊𝑊𝑊𝑊% = 𝑈𝑈𝐷𝐷𝑂𝑂𝐻𝐻 𝑊𝑊𝑊𝑊% + 𝐼𝐼𝐼𝐼𝐴𝐴 𝑊𝑊𝑊𝑊% + 𝑂𝑂𝑂𝑂𝐻𝐻 𝑊𝑊𝑊𝑊%

Calculate OCM in weight percent by addition of any impurity providing a positive FID response ahead of and…