A Single-Method Approach for the Analysis of Volatile and Semivolatile Organic Compounds in Air Using Thermal Desoprtion Coupled with GC–MS

November 30, 2014
Adrian Boborodea, Andre Luciani
LCGC Europe

Volume 27, Issue 12

This study presents results of gel permeation chromatography (GPC) and analytical temperature rising elution fractionation (TREF) of polyethylene in butylal (dibutoxymethane, a halogen-free solvent).

This study presents results of gel permeation chromatography (GPC) and analytical temperature rising elution fractionation (TREF) of polyethylene in butylal (dibutoxymethane, a halogen-free solvent). A comparison is made with the results obtained using 1,2,4-trichlorobenzene showing that changing the solvent to butylal does not require any modification of the existing GPC instruments and has additional advantages such as lower toxicity, increased detector signal for polystyrene standards, and broadening domain of crystallization temperatures for TREF.

 

The molecular structure of polyethylene (PE) is usually analyzed by two techniques: Gel permeation chromatography (GPC) and temperature rising elution fractionation (TREF).

GPC separates the macromolecules according to their hydrodynamic volume and allows for a measurement of the molecular weight distribution (MWD). TREF separates semicrystalline polymers as a function of their melting temperature in solution and allows for the evaluation of short chain branching distribution (SCBD).

 

In both cases, the samples are analyzed in dilute solutions obtained in chlorinated solvents as dichlorobenzene or trichlorobenzene. Usually, the polymer is separated in fractions using a set of columns and the concentrations of the eluted fractions are measured with differential refractive index (dRI) detection. The resulting chromatograms are converted in MWD or SCBD by calibrating the method with standards.

The solvent 1,2,4-trichlorobenzene (TCB) is frequently used for these analyses, mainly because of the following properties:

  • Its boiling point is 214 °C, allowing the melting and dissolution of all types of polyethylenes.

  • The differential index of refraction (dn/dc) of polyethylene solutions is -0.1 mL/g, which gives good signals in dRI detection for injected concentrations as low as 1 mg/mL.

  • Polystyrene is soluble in TCB, which offers the possibility to use the polystyrene–divinylbenzene gel columns and calibrate the GPC systems with narrow standards.

However, TCB also has some disadvantages:

  • Its freezing point is 17 °C, close to room temperature, so precautions have to be taken to avoid TCB crystallization, which can damage the GPC column gel and GPC detectors.

  • Polystyrene solutions have a dn/dc of 0.05 mL/g, which renders the GPC calibration difficult, especially for low molecular weights of standards obtained by butyl lithium induced anionic polymerization, in which the residual butyl part of initiator with a high negative dn/dc further diminishes the peak intensity.

  • It has a relatively high toxicity, causes skin irritation, and is labelled as very toxic to aquatic life with long-lasting effects.

Because of environmental concerns there is a continuous trend towards the replacement of chlorinated solvents with solvents that have a lower toxicity, mostly in the cleaning industry (1). In a recent application patent (2), acetals were described as a valuable replacement for perchlorethylene or trichloroethylene for dry cleaning of textile, leather, or fur goods. In addition to dissolving a large spectrum of compounds, acetals produced by reactions between alcohols and aldehydes can be prepared from renewable or potentially renewable alcohols. With regard to their toxicity, only a few studies are available, but acetals are expected to show very good health and environment profiles and are also biodegradable.

In this study, we show the potential of using butylal in GPC and TREF analyses of polyethylenes. We chose this acetal because of its high boiling point (180 °C), low volatility, and ability to dissolve polystyrene. The evaluation was performed by comparing the results obtained with TCB and butylal on the same samples with the same GPC and analytical TREF systems and methods.

Experimental

Solvents: We used 1,2,4-trichlorobenzene (TCB, Spectropure dry, Biosolve Chimie) and dibutoxymethane (butylal, ultra-pure grade, Lambiotte & Cie, CAS 2568-90-3) for GPC and analytical TREF analyses.

Samples: Polyethylene standard (SRM 1475a, molecular weight [MW] = 52,000 g/mol, polydispersity = 2.9, National Institute of Standards and Technology [NIST]) and a narrow distribution polystyrene standard (MW = 135,000 g/mol, polydispersity = 1.1, Agilent Technologies) were analyzed by GPC. Four commercial metallocene polyethylenes with narrow short-chain branching distributions and the following densities were analyzed by analytical TREF: 0.923 g/cm3 , 0.934 g/cm3 , 0.947 g/cm3 , and 0.955 g/cm3 .

GPC Apparatus and Method: The GPC was performed on a GPC 2000 gel-permeation chromatograph (Waters Corporation). The samples were dissolved at 160 °C to obtain solutions with concentrations between 0.1 mg/mL and 1.0 mg/mL. A 300-µL volume of the hot solution was injected in a 300 mm × 7.5 mm PLgel 10 µm Mixed B column (Agilent Technologies). The flow rate was 1 mL/min, and the temperature of injector, column, and detector was 145 °C. The chromatograms were recorded using the built-in differential refractive index detector. For the analysis of polyethylene in TCB, because of its negative dn/dc, an inversed polarity of detector was selected.

Analytical TREF Apparatus and Method: The analytical TREF was performed using a GPC 2000 gel-permeation chromatograph (Waters), connected with a GC 6890N oven (Agilent Technologies). The samples were dissolved at 160 °C to obtain solutions with concentrations of 0.5 mg/mL and 1.0 mg/mL. A volume of 300 µL of the hot solution was injected at 150 °C in a 30 mm × 4.6 mm stainless steel column packed with metallic wires as described in our patent (3). The column filled with solution was fast cooled (1 °C/min) to 100 °C, and then was further cooled to 30 °C with a cooling rate of 0.1 °C/min. After the cooling step, the polymer was eluted from the column using a flow rate of 0.2 mL/min. Before starting the heating from 30 °C to 150 °C with a heating rate of 1 °C/min, the column was maintained at 30 °C for 30 min. The concentrations of the eluted fractions were measured using the built-in differential refractive index detector of the GPC system. A temperature shift of 3.2 °C because of the time delay between the oven and detector was measured for both solvents using the method described in a previous paper (4) by eluting the polyethylene with a density of 0.947 g/cm3 at different heating rates.

From a practical point of view, replacing the solvent with butylal in the high-temperature GPC and analytical TREF systems running on TCB is extremely easy. Actually, no temperature modification is required, the butylal is simply pumping at 1 mL/min to replace the TCB from the column and tubing. After replacing TCB, the dRI detector has to be purged for about 30 min. After purging the detector, the system has to be equilibrated at 1 mL/min as usual, by recirculating butylal for a few hours, before starting the analyses. Because we wanted to provide clear information on the expected results with butylal, apart from using a different offset in Figures 2 and 3 for the curves in butylal, all chromatograms are presented as obtained, without smoothing or drift corrections.