Elsevier

Applied Clay Science

Volume 47, Issues 3–4, February 2010, Pages 263-270
Applied Clay Science

Effect of modified montmorillonite on biodegradable PHB nanocomposites

https://doi.org/10.1016/j.clay.2009.11.001Get rights and content

Abstract

Polymer nanocomposites, based on a bacterial biodegradable thermoplastic polyester, poly(hydroxybutyrate) (PHB), and two commercial montmorillonites (MT), Na-M (MT) and 30B-M (organically modified MT), were prepared by melt-mixing technique at 165 °C. Both clays minerals were characterized by morphology, crystallochemical parameters, and thermal stability. Lower specific surface area (determined by adsorption methods) values were found for 30B-M. The apparent particle size from light scattering measurements, scanning electron microscopy observations, and crystallite size (determined from XRD patterns) of 30B-M indicated a higher degree of particles exfoliation than of Na-M.

The nanocomposites PHBNa and PHB30B were characterized by differential scanning calorimetry (DSC), polarized optical microscopy (POM), X-ray diffraction (XRD), transmission electron microscopy (TEM), mechanical properties, and burning behaviour. Intercalation/exfoliation observed by TEM and XRD was more pronounced for PHB30B than PHBNa, indicating the better compatibility of 30B-M with the PHB matrix. An increase in crystallization temperature and a decrease in spherullites size were observed for PHB30B. The intercalation/exfoliation observed by TEM and structure XRD increased the moduli of the nanocomposites. The burning behaviour of PHB30B was influenced by the aggregation of the clay mineral particles.

Introduction

Montmorillonite, hectorite and saponite are the most commonly used clay minerals for the preparation of polymer nanocomposites. Numerous studies have shown that the incorporation of small quantities of these clay minerals (5–10% in mass), with a certain degree of exfoliated structure, have a great influence on the properties of the final material, such as mechanical strength, stiffness, thermal stability, conductivity, and gas barrier properties (Ray & Okamoto, 2003, Ray & Bousmina, 2005, Tjong, 2006, Ruiz-Hitzky & Van Meerbeek, 2006, Xiong et al., 2007). The nanocomposite structure depends on the clay mineral–polymer compatibility and on processing conditions (Zenggang et al., 2002, Fornes et al., 2003, Homminga et al., 2005, Avella et al., 2006, Cervantes-Uc et al., 2007, Hablot et al., 2008). Mainly, two different structures are achievable: nanocomposites with intercalated or exfoliated clay mineral particles (Ray & Bousmina, 2005, Lagaly et al., 2006). Both structures coexist in nanocomposites, and it is believed that the properties are related to the high aspect ratio of exfoliated structure (Alexandre and Dubois, 2000). The term intercalation (Dennis et al., 2001, Lagaly et al., 2006) describes the case where a small amount of polymer moves into the interlayer space of the clay mineral particles. Exfoliation or delamination occurs when polymer further separates the clay mineral layers, e.g. by 80–100 Å or more.

The use of conventional plastics in the last years has been broadened to new areas. Due to their very low degradation rates, plastics can cause environmental problems when they are disposed as solid waste. An alternative to reduce this problem is the substitution of conventional plastics by biodegradable ones. Polyhydroxybutyrate (PHB) is an example of a biodegradable polymer, obtained from a renewable resource, showing a biodegradation rate of about 3 months after soil burial (Correa et al., 2008). The main applications of PHB are in biomedical, agricultural, and packaging products (Scott, 2002), being the last industry one of the most interested in the use of PHB in form of nanocomposites.

The aim of this study is to characterize two commercial clays minerals (one of them being organically modified) used to prepare PHB nanocomposites.

Section snippets

Montmorillonite characterization

Na-montmorillonite was Cloisite® Na+, named Na-M, and organo-montmorillonite was Cloisite® 30B referred to as 30B-M, from Southern Clay Products. Both samples were used as received.

Fig. 1 shows the chemical structure of the quaternary ammonium ion in 30B-M, where T indicates tallow. The amount of the quaternary ammonium ion corresponded to CEC 0.90 mEq/g as indicated by the supplier.

Chemical analysis (ICP-AES) was performed with Na-M and 30B-M. To decompose the organic material in 30B-M, the

Clay minerals

Similar elemental contents were found in both samples (Table 1). The decrease of the Na2O and CaO of the heated 30B-M was indicative of the amount of quaternary ammonium ions bound. LOI was low due to the reduced amount of interlamellar water and the preceding calcination.

The structural formulae were determined following Siguin et al. (1994) from chemical composition (Table 1):Na-M (Si 3.97 Al 0.03) [Al 1.56 Fe 0.22 Mg 0.22] 0.25 M+calcined 30B-M (Si 3.97 Al 0.03) [Al 1.57 Fe 0.22 Mg 0.21] 0.24

Conclusions

The apparent particle diameters from light scattering measurements indicated aggregated particles of 30B-M. The montmorillonite particles acted as a nucleating agent in the PHB matrix. PHB30B TEM images showed better particle dispersion and intercalation than PHBNa, due to a compatibility between the organic modified montmorillonite and PHB which may be responsible for the higher Young modulus obtained. However, the exfoliation/intercalation ratio was not high enough to increase the tensile

Acknowledgements

The authors thank ANPCyT PICT 1360 and NOVELQ: Novel Processing Methods for the Production and Distribution of High-Quality and Safe Foods contract no: 015710- for financial support.

References (50)

  • H.R. Dennis et al.

    Effect of melt processing conditions on the extent of exfoliation in organoclay-based nanocomposites

    Polymer

    (2001)
  • T. Fornes et al.

    Polymer matrix degradation and color formation in melt processed nylon 6/clay nanocomposites

    Polymer

    (2003)
  • E. Hablot et al.

    Thermal and thermo-mechanical degradation of poly (3-hydroxybutyrate)-based multiphase systems

    Polym. Degrad. Stab.

    (2008)
  • H. He et al.

    Changes in the morphology of organoclays with HDTMA+ surfactant loading

    Appl. Clay Sci.

    (2006)
  • D. Homminga et al.

    Influence of shear flow on the preparation of polymer layered silicate nanocomposites

    Polymer

    (2005)
  • S.Y. Lee et al.

    Expansion characteristics of organoclay as a precursor to nanocomposites

    Colloids Surf., A Physicochem. Eng. Asp.

    (2002)
  • S. Lee et al.

    Microstructure, tensile properties, and biodegradability of aliphatic polyester/clay nanocomposites

    Polymer

    (2002)
  • B. Lepoittevin et al.

    Poly(ε-caprolactone)/clay nanocomposites prepared by melt intercalation: mechanical, thermal and rheological properties

    Polymer

    (2002)
  • B. Lombardi et al.

    Bentonite deposits of Northern Patagonia

    Appl. Clay Sci.

    (2003)
  • A. Magnoli et al.

    Structural characteristic of commercial bentonites used as detoxifier of broiler feed contamination with aflatoxin

    Appl. Clay Min.

    (2008)
  • N. Ogata et al.

    Structure and thermal/mechanical properties of poly(ethylene oxide)-clay mineral blends

    Polymer

    (1997)
  • L.M. Oliveira et al.

    Gamma irradiation effects on poly(hydroxybutyrate)

    Polym. Degrad. Stab.

    (2006)
  • S. Pavlidou et al.

    A review on polymer-layered silicate nanocomposites

    Prog. Polym. Sci.

    (2008)
  • S. Tjong

    Structural and mechanical properties of polymer nanocomposites

    Mater. Sci. Eng. Res.

    (2006)
  • A. Vazquez et al.

    Modification of montmorillonite with cationic surfactants. Thermal and chemical analysis including CEC determination

    Appl. Clay Sci.

    (2008)
  • Cited by (135)

    • Role of Green Polymers in Food Packaging

      2020, Encyclopedia of Renewable and Sustainable Materials: Volume 1-5
    View all citing articles on Scopus
    View full text