Passive
sampling of very hydrophilic chemicals is challenging due
to the weak adsorption affinity to commonly used sorbent
phases. Here we present a technique for the passive time-integrative
sampling of highly water-soluble chemicals in wastewater influent,
using a new diffusion-based sampling device. The sampler is a sealed
chamber covered at one end by a porous polyethylene membrane, allowing
chemicals to diffuse through the water-filled pores into the receiving
phase of water. When submerged, the concentration gradient drives
diffusion into the sampler, increasing the concentration of analytes
in the receiving phase over time. To calibrate and test sampler performance,
the sampler was deployed in wastewater influent for 31 d. The accumulation
of acesulfame, ethyl sulfate, methamphetamine, and benzoylecgonine
into the sampler was modeled using simultaneously collected 24 h composite
samples. The four chemicals are typically monitored in wastewater-based
surveillance programs and ranged in log K
ow from −2.49 (ethyl sulfate) to 2.22 (methamphetamine). In situ calibration showed linear increases in concentration
over the deployment period, and calculated sampling rates ranged from
2.2 mL d–1 (methamphetamine) to 4.0 mL d–1 (ethyl sulfate). This technique is useful for the time-integrative
sampling of a range of hydrophilic chemicals in wastewater and shows
potential for other aquatic matrices.
Passive
sampling approaches to monitor licit and illicit drugs
of concern in wastewater shows promise as a supplementary sampling
technique to grab sampling when conventional composite autosampling
may not be possible. Recent studies have assessed the applicability
of passive sampling at a single wastewater treatment plant (WWTP).
However, it remains unknown whether a single-site calibration can
be applied to other WWTPs. This study evaluated the in situ calibration
of microporous polyethylene tube passive samplers (MPTs) against simultaneously
collected composite samples for 22 different WWTPs. Samples were analyzed
for methylamphetamine, amphetamine, hydroxycotinine, cotinine, benzoylecgonine,
3,4-methylenedioxymethamphetamine, and noroxycodone. Estimated rates
of chemical uptake (sampling rates) were calculated using the mass
accumulated in the samplers, the concentration measured in composite
samples, and the duration of deployment. The estimated sampling rates
were consistent between WWTPs (>90% within a factor of two) and
ranged
from 5 mL day–1 (amphetamine) to 9 mL day–1 (noroxycodone). The samplers were effective at estimating analyte
concentrations, with 77% of results having a normalized difference
to 24 h composite samples of below 30%. Our study suggests that MPT
passive samplers provide a tool for the spatiotemporal monitoring
of drug use where automated integrative sampling techniques may not
be feasible.
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