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Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
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Appendix B

Mass Balance for the Newport Chemical Agent Disposal Facility (NECDF) Process

Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
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This page in the original is blank.
Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
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FIGURE B-1 Process flow diagram for the integrated NECDF process.

Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×

TABLE B-1 NECDF Inputs for Process Mass Balance (stream numbers correspond to streams identified in Figure B-1 )

 

Process Inputs

Description

Agent in Ton Containers

50% NaOH Solution

Oxidant to SCWO

Nitrogen to Neutralization Vessels

Process Air to TCC

Total Inputs

Stream Number

1

2

3

N/A

N/A

N/A

Total Flow (kg/1,000 kg agent)

1,000

1,195

3,500

7

5,667

11,369

Physical State

liquid

liquid

vapor

vapor

vapor

temperature (°F)

70

80

70

70

70

pressure (psig)

14.7

14.7

3,500

17.7

100

Vapor Components

oxygen (kg/1,000 kg agent)

3,500

1,190

4,690

nitrogen (kg/1,000 kg agent)

7

4,477

4,484

Liquid Components

VX (kg/1,000 kg agent)

957

957

agent impurities (kg/1,000 kg agent)

44

44

NaOH (kg/1,000 kg agent)

598

598

Water (kg/1,000 kg agent)

598

598

Solid Components

TC shells (no./1,000 kg agent)

1.5

1.5

TC valves (no./1,000 kg agent)

2.9

2.9

TC plugs (no./1,000 kg agent)

8.8

8.8

Source: Adapted from Stone and Webster, 1997b.

Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×

TABLE B-2 NECDF Outputs for Process Mass Balance (stream numbers correspond to streams identified in Figure B-1)

 

Process Outputs

Description

Ton Container Parts

TCC Air Dry Vent

Neutralization Reactors Vent

Hydrolysate Tanks Vent

SCWO Vapor Effluent

Salt Solids to Disposal

Discharge to STP

Total Outputs

Stream Number

4

N/A

5

6

7

8

9

Total Flow (kg/1,000 kg agent)

5,667

6

1

3,121

1,531

1,043

11,369

Physical State

solid

vapor

vapor

vapor

vapor

solid

liquid

temperature (°F)

46

40

80

95

100

pressure (psig)

18

21

15

15

15

Vapor Components

oxygen (kg/1,000 kg agent)

1,190

1,803

2,993

nitrogen (kg/1,000 kg agent)

4,477

6

0.3

4,483.3

VOCs (kg/1,000 kg agent)

0.4

1,165

1,165.4

carbon dioxide (kg/1,000 kg agent)

82

82

nitrous oxide (kg/1,000 kg agent)

0.1

0.1

inorganic impurities (kg/1,000 kg agent)

10

10

Solid/Liquid Components

Na2SO4 (kg/1,000 kg agent)

70

451

1,043

1,574

Na2HPO4 water (kg/1,000 kg agent)

530

530

TOC (kg/1,000 kg agent)

0.1

0.1

inorganic impurities (kg/1,000 kg agent)

10

10

TC shells (no./1,000 kg agent)

1.5

1.5

TC valves (no./1,000 kg agent)

2.9

2.9

TC plugs (no./1,000 kg agent)

8.8

8.8

Source: Adapted from Stone and Webster, 1997b.

Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×

TABLE B-3 Water Formation Resulting from the Neutralization of VX and Oxidation of the Hydrolysate during the NECDF Process

Water is formed in the neutralization supercritical water oxidation (SCWO), and pre-evaporation pH adjustment processes. The following illustrates this water formation by showing that elemental hydrogen enters the process in water and other compounds but exits the process mostly as water.

The elemental hydrogen inputs to process are for 1,000 kg of agents.

Stream

Constituents

Hydrogen Content

Agent

1,000 kg VX

98 kg

50% NaOH solution

598 kg NaOH

598 kg H2O

15 kg

67 kg

Total

2,195 kg

180 kg

Notes: For simplification, the agent is assumed to be pure VX, with a molecular weight of 267 and a molecular formula of C11H26O2NPS. The 50% NaOH solution flow shown here includes all caustic to the process, both for neutralization and for post-treatment.

The only product other than water that contains hydrogen is the phosphate salt in stream number 8, Figure B-1, salt solids to disposal, which contains

530 kg Na2HPO4/1,000 kg of agent = 4 kg H/1,000 kg of agent

The balance of hydrogen:

180 - 4 = 176 kg H/1,000 kg of agent

is reacted with oxygen present throughout the process to form water.

The resulting water is found in the following output streams (per 1,000 kg of agent).

Stream

Water Content

Hydrogen Content

SCWO vapor effluent

70 kg H2O

8 kg

Salt solids to disposal

461 kg H2O

51 kg

Discharge to STP

1,043 kg H2O

116 kg

Total

1,574 kg H2O

175 kg

The total amount of water formed in the process is water out minus water in.

1,574

- 598

976 kg H2O/1,000 kg of agent

   

Source: Stone and Webster, 1997b

Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×
Page 65
Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×
Page 66
Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×
Page 67
Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×
Page 68
Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×
Page 69
Suggested Citation:"Appendix B." National Research Council. 1998. Using Supercritical Water Oxidation to Treat Hydrolysate from VX Neutralization. Washington, DC: The National Academies Press. doi: 10.17226/6150.
×
Page 70
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The U.S. Army has asked the National Research Council (NRC) to evaluate whether supercritical water oxidation (SCWO) is an effective and appropriate means of eliminating hazardous or toxic organic constituents in VX hydrolysate for ultimate disposition. The NRC was not asked to conduct an in-depth analysis of the entire integrated VX bulk agent destruction and disposal process for the Newport Chemical Agent Disposal Facility. As the facility design is being finalized (March 1999-April 2000), the NRC will probably be asked to assess all aspects of the facility design, including monitoring, containment, process control, and redundancy, as well as the quantitative risk assessment (QRA). This report outlines the elements of the proposed neutralization/SCWO technology, evaluates the results of ongoing SCWO tests, and makes recommendations concerning aspects of the technology that require further development. The scope of this evaluation did not include evaluations of other potential technologies or management options for the treatment of VX hydrolysate.

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