Migration of mineral oil from party plates of recycled paperboard into foods: 1. Is recycled paperboard fit for the purpose? 2. Adequate testing procedure

Party plates made of recycled paperboard with a polyolefin film on the food contact surface (more often polypropylene than polyethylene) were tested for migration of mineral oil into various foods applying reasonable worst case conditions. The worst case was identified as a slice of fried meat placed onto the plate while hot and allowed to cool for 1?h. As it caused the acceptable daily intake (ADI) specified by the Joint FAO/WHO Expert Committee on Food Additives (JECFA) to be exceeded, it is concluded that recycled paperboard is generally acceptable for party plates only when separated from the food by a functional barrier. Migration data obtained with oil as simulant at 70°C was compared to the migration into foods. A contact time of 30?min was found to reasonably cover the worst case determined in food.     

Simulation of the migration of mineral oil from recycled paperboard into dry foods by Tenax®?

Conventional migration testing for long-term storage at ambient temperature with Tenax^® was applied to a recycled paperboard as well as to the same paperboard with a polyethylene or polypropylene film in between. Test conditions were from the European Union plastic Regulation 10/2011, that is, 10 days at 60°C, but previous standard conditions of 10 days at 40°C were also applied. The results were compared with the migration into real packs made of the same packaging material containing six test foods and stored over 9 months. For the direct contact, simulation at 60°C overestimated the maximum migration of the saturated hydrocarbons in the real packs by 73%. Simulation reflected hardly any effect by the plastic films and resulted in an overestimation of the maximum migration into the real packs by a factor of 5.1 and 27 for the polyethylene and the polypropylene film, respectively. Analogous simulation was performed with polenta (corn semolina) instead of Tenax^®. Three main causes for this deviation were identified: (i) at 60°C, migration reached beyond n-C₃₅, whereas it ends at about n-C₂₄ in reality. (ii) Tenax^® is a far stronger adsorbent than foods, resulting in almost complete extraction. (iii) The significant barrier effect of polypropylene films at ambient temperature is lost at increased temperature. The suitability of such simulation for the prediction of long-term migration is questioned.     

The analysis of saturated and aromatic mineral oil hydrocarbons in dry foods and from recycled paperboard packages by online HPLC–GC–FID

ABSTRACT

The purpose of this study was to determine the concentrations of mineral oil hydrocarbons in dry foodstuffs packed in recycled paperboard, which were imported from different foreign countries to Germany. After collection, mineral oil saturated hydrocarbons (MOSH) and mineral oil aromatic hydrocarbons (MOAH) in dry foodstuffs and recycled paperboard were analysed using online coupled high-performance liquid chromatography–gas chromatography–flame ionisation detection (online HPLC–GC–FID) far before the end of the shelf life of the samples. Our results showed that recycled paperboard has MOAH content higher than that of dry foodstuffs. The proportion of MOAH within total mineral oil hydrocarbons was determined to be 7–45% in dry foodstuffs and 4–48% in paperboard. In addition, 29% of the products were found to contain over 1.00 mg/kg MOAH, with a maximum of 2.72 mg/kg in oatmeal. White colour recycled paperboard contained lower amounts of MOSH and MOAH than that of brown and grey colour recycled paperboard. The MOSH concentration in dry foodstuffs ranged from 0.11 to 21.92 mg/kg (?C25 hydrocarbons), which may be an indication of rapid migration. The lowest determined MOSH concentrations (?C25 hydrocarbons) were found in sea salt and soda samples, even when their paperboard contained high mineral oil hydrocarbons. Our three samples in packages containing internal bags (for complete barriers) were found to have low mineral oil concentration due to reduced migration through plastic (acrylate-coated polypropylene). However, one sample, a ‘crispy’ product with an internal bag, contained the extreme amount of 21.92 mg/kg. Differences in contaminants observed in both dry foodstuffs and recycled paperboard may have been due to the different packaging and production techniques of the different countries. In addition, 8 of 24 dry foodstuff samples contained MOSH concentrations frequently exceeding the 2.0 mg/kg limit for MOSH C₂₀–C₃₅.     

The Method of Aschaffenburg and Drewry for the Crystallization of β-Lactoglobulin and α-Lactalbumin. 1. Electrophoresis of Fractions and the Calcium2+/Ethylenebis (Oxyethylenenitrilo) Tetraacetic Acid Shift of α-Lactalbumin

β-Lactoglobulin and α-Lactalbumin were isolated and crystallized by the classical method of Aschaffenburg and Drewry, and the purity of the crystals was assessed by native PAGE and SDS-PAGE. Although β-lactoglobulin was free of contaminants, α-lactalbumin was still contaminated after five recrystallization steps. Yields of crystals in this study were lower than reported by Aschaffenburg and Drewry. Further, it was observed that α-lactalbumin undergoes a Ca²⁺/Ca²⁺-free, dependent electrophoretic shift characteristic of many calcium-binding proteins.