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MEMBRANE TRANSFER TECHNOLOGY

Charles L. Kimbell
President
Keco R & D, Incorporated
Route 3, Box 141
Navasota, TX  77868
Bill Barnes
Sales Coordinator
Keco R & D, Incorporated
Route 3, Box 141
Navasota, TX  77868

KEYWORDS

Membrane Transfer, Sample Permeation, Permeation Transfer, Volatile Organic Carbon (VOC), Analyzer, VOC Remediation, Emissions Reporting, Calibration

ABSTRACT

The use of a permeable membrane to monitor volatile hydrocarbons including chlorinated hydrocarbons, alcohol and other chemicals from low PPB to percent in a liquid or gas phase is practical. This alternative to the sparger or purge and trap methods reduces maintenance for GC's or other analyzers.

INTRODUCTION

Permeation has been around for many years however, with the in depth research and development of the transfer unit, Figure 1, there are many ways to use the unit that have not been recognized in the past.

The main instrumentation use of the transfer unit is to allow a hydrocarbon tainted liquid or gas to pass on one side of a membrane and the hydrocarbon will permeate through the membrane where a clean flowing gas will evaporate the hydrocarbons from the membrane surface resulting in a clean dry sample suitable for an analyzer. Detectability is 1 PPB range to percent (1).

This eliminates use of heated injection valves to vaporize a sample and also eliminate need for heat traced lines. The clean, dry carrier gas prevents condensation in the flow lines.

Transfer units can operate for long periods of time with a minimum of maintenance, as shown by results in petrochemical plant testing.

Membrane tests are listed below, Table I. Various GC analyzers were employed and flowrates were not adjusted for optimum results. Detection limit was determined by multiplying the PPM weight by the average noise divided by response at that PPM.


TABLE I - RESPONSE USING MEMBRANE
TRANSFER SAMPLE INTO VARIOUS GC'S

TRACE HYDRO-
CARBON
CONCEN-
TRATION
RES-
PONSE
NOISE DETECT-
ABLE PPB
Benzene in Water 10 PPM 672.0 0.3 4.4 PPB
Benzene in Water 5 PPM 229.0 0.5 10.9 PPB
Benzene in Water 1 PPM 170.0 5.0 29.4 PPB
Benzene in Water 0.008 PPM 600.0 100.0 13.3 PPB
Benzene Quinch Water 5 PPM 623.0 1.0 8.0 PPB
Trichloro Ethylene in Water 1 PPM 598.0 3.0 5.0 PPB
Tertiary Butyl Alcohol 5 PPM 265.0 0.5 9.4 PPB

 

Two techniques for dynamic calibration were developed, one using the permeation tube and the other is the micro injection system. The injector mechanically injects minute quantities of a pure substance directly into flowing lines. This allows wide rangeability at PPM or PPB levels. Flow rates ranging from 0.000020 ml/min to 0.003 ml/min were obtained using an injection rate control.


TABLE II - COMPARISON TEST
SPARGER VS TRANSFER UNIT

HYDRO-
CARBON

SPARGER
RESPONSE

TRANSFER UNIT
RESPONSE
Ethylene-Ambient 9.4 PPB 6.3 PPB
Ethylene @ 55ºC 12.2 PPB 10.6 PPB
Propane-Ambient 13.6 PPB 15.7 PPB
Propane @ 55ºC 11.25 PPB 11.5 PPB
Methyl Chloride-Ambient 23.1 PPB 20.6 PPB
Methyl Chloride @ 55ºC 26.0 PPB 19.5 PPB

 

This set of data, Table II, was obtained in an operating plant on actual cooling tower water lines using the same GC readouts. Various types of membranes can be used. They can be used in water streams to monitor for hydrocarbons; as an alternative to the sparger or the purge and trap system. There is little maintenance to the transfer system which is an essential component of the equipment making the method superior to the older methods.

Monitoring quinch ponds, cooling tower water and head space in manholes or off plant water is all possible. The transfer unit can also be used in liquid or head space above the liquid. Good results have been obtained when analyzing for hydrocarbons being removed from plastic pellets by steam or nitrogen.

Figure 2, is a chart recording showing calibration of a Keco R & D, Inc., Model 204, benzene in cooling tower water analyzer. The actual cooling tower water was scrubbed with a charcoal filter which provided a zero benzene reading. A permeation tube designed to give 20 PPB by weight, read as 19.5 PPBw was used. A second calibrator mechanically injects benzene into clean water to the analyzer to provide 10 PPBw as shown on the right. The 7.7 PPBw reading correlates very well to the permeation tube calibration. This data was obtained after shipping and installation, additional adjustments after the original factory calibration were unnecessary.

The micro injection method of calibration is a new development which allows over 100 to 1 ranging for linearity checking and requires only a contact closure for automatic calibration. The sample is prepared at the time of use eliminating degradation with time as can result from bacterial action or absorption.

Figure 3, is a recording of cooling tower water with the ethylene plant in normal operation. Both recordings show the GC reading of benzene every four minutes shown as points on the long term graphs. Slight fluctuations of benzene levels of 2.25 PPBw and 1.1 PPBw are shown over a 3 day run. These fluctuations were caused by heat exchanger leaks. Disconnecting the leaking heat exchanger corrected the problem as shown by the recording.

REFERENCES

1. Kimbell, Charles, Barclay, Limuel, US Patent No. 5,448,922, Gas permeation system.
2. John P. Survis, Equivalency of Method Determination for Measurement of Volatile Organic Compounds (VOC) by Semipermeable Membrane Transfer, Texas Natural Resources Conservation Commission, letter May 10, 1996.

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