• Luca Rota Written by Luca Rota, Product Manager | 20 December 2024

Determination of tyre wear particle (TWP) through microwave extraction of 6-PPDQ antioxidant


through microwave extraction of 6-PPDQ antioxidant

INTRODUCTION

Tyre wear particles (TWP) are one of the common types of microplastics found in the environment, potentially posing a significant risk to wildlife that ingest the particles. Recent studies have linked the presence of additives leaching from these microplastics to the deaths of fish species, as salmon and trout in the United States and Canada rivers. It should be noted that possible risks for human health are also under assessment. One of the additives recognized to be more accountable for the aforementioned toxicity is 6-PPDQ, the oxidized quinone form of 6-PPD [N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine].
6-PPD is widely used as an antiaging agent not only for tyres but in the rubber manufacturing sector globally, and its mechanism of action involves the migration to the object surface where it can scavenge ozone and oxygen, preserving the material from wearing.
The UK Centre for Ecology & Hydrology (UKCEH) project team recently published a comprehensive study on the field.
It was carried out on behalf of Department of environment, food and rural affair (DEFRA) with the aim to detect and quantify the occurrence of different type of microplastic in UK river and sediments, including the assessment of TWP though an indirect quantification of 6-PPD, which was chose a a molecular marker due to its particular chemical structure and persistency in the environment.
Microwave assisted extraction (MAE) proved to be a reliable and effective technique to obtain extraction of those types of additives from the treated sediments and soils. To perform MAE, the group of research used Milestone’s ETHOS X benchtop microwave extraction system with fastEX 24 eT rotor.

EXPERIMENTAL

INSTRUMENT
  • ETHOS X equipped with fastEX-24 eT extraction rotor
  • 100-mL disposable glass vials (PN GB00122)
  • Gas chromatograph with Mass Spectrometer detector (GC-MS)
  • Analytical balance
  • Vials for collection of extracts
  • Glass funnels for filtration
  • Glass fiber filters
STANDARD AND REAGENTS
For extraction Dichloromethane HPLC grade >99.9% (Rathburn chemical) and Sodium sulfate (Sigma Aldritch) were used. Each sample was spiked with labelled recovery standard (D10-Fluoranthene; Spex) For the GC-MS calibrarion curve a standard of 6-PPD (Sigma Aldrich) was employed.

SAMPLE INFORMATION
The sediments were collected in three replicates from two different sites along UK rivers. First site (urban) was on the Irk river in Greater Manchester while second (rural) was on Thames river in Wallingford, Oxfordshire.

ANALYTICAL PROCEDURE
Field samples were stored at -20°C in cleaned glass jars cautiously cleaned to avoid any contamination. Defrosted samples were mixed thoroughly using a metal spatula, to homogenize. 4 g of sample was decanted into a clean beaker, the weight was recorded accurately, and the samples were then dried with sodium sulphate. The sediments were then transferred into the glass vials of the fastEX-24 rotor. For the recovery essay all the sediments extracted were spiked with the recovery standard D10-Fluoranthene, an analogous compound to 6-PPD. 25 ml of mixture of DCM:Acetone 1:1 was added. The extraction procedure was carried out. After the extraction, samples were filtered on glass fiber filters and the vials were rinsed with additional solvent aliquots. Extracts and rinsates were collected and concentrated at low volumes (1.5 ml of solvents).

GC-MS QUANTIFICATION
Prior to GC analysis a step of cleaning through size exclusion chromatography was employed (Agilent HPLC 1200).
Injection was carried splitless mode in a GC 6890N Gas Chromatograph (Agilent, Santa Clara, CA, USA) equipped with HP5-MS column (30 m, 0.25 mm, 0.25 µm; Agilent J&W GC Columns). The injector was maintained at 250 °C. The injection quantity was 1.7 µL at a flow rate of 1.5 mL/min of He. The oven was held at 50 °C for 1.5 min, followed by a 30 °C/min increase to a final temperature of 260 °C, which was held for 10 minutes.
The detector was a 5975B Mass Spectrometer (Agilent, Santa Clara, CA, USA) working in SCAN/SIM mode. The range of SCAN was set at 50-800 m/z and SIM ions chosen were m/z 211, 212 and 268 (6-PPD fragments).
6PPD was quantified using a calibration curve of the 6PPD and the samples were recovery-corrected using the IS D10-Fluoranthene.

RESULTS AND DISCUSSION

Firstly, the recovery results obtained on the recovery standard D10-Fluoranthene in every sediment was excellent. The mean recovery was 95.8% (SD 10.73%, CoV 11.2%).
Results from extractions for the two types of sediment sample are shown in Figure 4. As expected in the rural site the concentration of 6-PPD detected was substantially lower than the one of the urban site. In the river Ink in the Greater Manchester area (urban site) the concentration of 6-PPD was detected as 12.0 ± 5.98 µg kg-1 while in the river Thames in Wallingford (rural site) the concentration detected was 1.02 ± 0.37 µg kg-1.
The outcome is in line with a recent study reported for sediment analyzed in China.

Figure 4 – Summary of 6PPD concentrations (µg kg-1 d.w.) detected at a Rural location in the River Thames at Wallingford, Oxfordshire (n=15) and on an urban location on the River Irk,Manchester IR4 (n=9)

Taking a worst-case scenario where 6-PPD does not degrade within sediments and that the concentration of 6-PPD in tyres is a uniform 2% (which is the maximum concentration in formulation), these concentrations would mean a final calculation of 51 and 599 µg kg-1 of TWP in the rural compared to the urban area sediments.

CONCLUSIONS

The synergy between the cleanliness provided using glass vials, which eliminate possible carryover and memory effect, robustness and inertness of the materials employed in the hardware construction and the contact-less temperature control in all positions ensure a perfect temperature uniformity and make fastEX24 eT a unique and innovative solution for the extraction of environmental pollutant analytes and additives from soils and sediments.
The quantity of sediment, due to the capacity of the glass vials, can be increased or decreased in the range from 3 to 30 g of sample, enabling the detection of analyte on the trace and ultratrace levels.
Furthermore, ETHOS X enables simultaneous solvent extraction of up to 24 samples (from weighing to filtration steps) in only 30 minutes. Indeed, this means that extraction throughput of over 200 samples in 8-hour workday.
The ETHOS X, with all its unique features, fully addresses the need of environmental laboratories which require a reliable equipment capable of exctraing a wide range of analytes, including the most particular ones like the 6-PPD, subject of this study.

ACKNOWLEDGEMENTS

1. K. Hiki and H. Yamamoto, Environmental Science & Technology Letters 2022 9 (12), 1050-1055

2. Measurement and Characterisation of Microplastics in English River Catchment Waters and Sediments, phase 3 https://randd.defra.gov.uk/ProjectDetails?ProjectId=20540

3. Zeng et al., Science & Technology 2023 57 (6), 2393-2403

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