Data for: Characterization of water-soluble synthetic polymeric substances in wastewater using LC-HRMS/MS

Synthetic water-soluble polymeric materials are widely employed in e.g. cleaning detergents, personal care products, paints or textiles. Accordingly, these compounds reach sewage treatment plants and may enter receiving waters and the aquatic environment. Characteristically, these molecules show a polydisperse molecular weight distribution, comprising multiple repeating units, i.e. a homologous series (HS). Their analysis in environmentally relevant samples has received some attention over the last two decades, however, the majority of previous studies focused on surfactants and a molecular weight range <1000 Da. To capture a wider range on the mass versus polarity plane and extend towards less polar contaminants, a workflow was established using three different ionization strategies, namely conventional electrospray ionization, atmospheric pressure photoionization and atmospheric pressure chemical ionization. The data evaluation consisted of suspect screening of ca. 1200 suspect entries and a non-target screening of HS with pre-defined accurate mass differences using ca. 400 molecular formulas of repeating units of HS as input and repeating retention time shifts as HS indicator.

To study the fate of these water-soluble polymeric substances in the wastewater treatment process, the different stages, i.e. after primary and secondary clarifier, and after ozonation followed by sand filtration, were sampled at a Swiss wastewater treatment plant. Remaining with two different ionization interfaces, ESI and APPI, in both polarities, a non-targeted screening approach led to a total number of 146 HS (each with a minimum number of 4 members), with a molecular mass of up to 1200 detected in the final effluent. Of the 146 HS, ca 15% could be associated with suspect hits and approximately 25% with transformation products of suspects. Tentative characterization or probable chemical structure could be assigned to almost half of the findings. In positive ionization mode various sugar derivatives with differing side chains, for negative mode structures with sulfonic acids, could be characterized. The number of detected HS decreased significantly over the three treatment stages. For HS detectable also in the biological and oxidative treatment stages, a change in HS distribution towards to lower mass range was often observed.

Dataset extent

Data and Resources


This Data Package

Mairinger, T., Loos, M., & Hollender, J. (2020). Data for: Characterization of water-soluble synthetic polymeric substances in wastewater using LC-HRMS/MS (Version 1.0) [Data set]. Eawag: Swiss Federal Institute of Aquatic Science and Technology.

The associated article

Mairinger, T., Loos, M., & Hollender, J. (2021). Characterization of water-soluble synthetic polymeric substances in wastewater using LC-HRMS/MS. Water Research, 190, 116745.


Open Data Open Data
  • Mairinger, Teresa
  • Loos, Martin
  • Hollender, Juliane
Keywords surfactants,polymeric substances,mass spectrometry,ionization sources,waste water treatment plant,non-targeted analysis,homologous series
Substances (scientific names)
  • /c21-1-3-23-5-7-25-9-11-27-13-15-29-17-19-31-20-18-30-16-14-28-12-10-26-8-6-24-4-2-22/h21-22H,1-20H2)
  • 3,6,9,12,15,18,21,24,27,30,33,36,39,42,45-Pentadecaoxaheptatetracontane-1,47-diol (InChI=1S/C32H66O17/c33-1-3-35-5-7-37-9-11-39-13-15-41-17-19-43-21-23-45-25-27-47-29-31-49-32-30-48-28-26-46-24-22-44-20-18-42-16-14-40-12-10-38-8-6-36-4-2-34/h33-34H,1-32H2)
  • 3,6,9,12,15,18,21,24,27,30,33,36,39-Tridecaoxahentetracontane-1,41-diol (InChI=1S/C28H58O15/c29-1-3-31-5-7-33-9-11-35-13-15-37-17-19-39-21-23-41-25-27-43-28-26-42-24-22-40-20-18-38-16-14-36-12-10-34-8-6-32-4-2-30/h29-30H,1-28H2)
  • 3,6,9,12,15,18,21,24,27,30-Decaoxadotriacontane-1,32-diol (InChI=1S/C22H46O12/c23-1-3-25-5-7-27-9-11-29-13-15-31-17-19-33-21-22-34-20-18-32-16-14-30-12-10-28-8-6-26-4-2-24/h23-24H,1-22H2)
  • 3,6,9,12,15,18,21,24,27,30-Decaoxatetratetracontan-1-ol (InChI=1S/C34H70O11/c1-2-3-4-5-6-7-8-9-10-11-12-13-15-36-17-19-38-21-23-40-25-27-42-29-31-44-33-34-45-32-30-43-28-26-41-24-22-39-20-18-37-16-14-35/h35H,2-34H2,1H3)
  • 3,6,9,12,15,18,21,24,27-Nonaoxanonacosane-1,29-diol (InChI=1S/C20H42O11
  • 3,6,9,12,15,18-Hexaoxaicosane-1,20-diol (InChI=1S/C14H30O8/c15-1-3-17-5-7-19-9-11-21-13-14-22-12-10-20-8-6-18-4-2-16/h15-16H,1-14H2)
  • Dodecaethylene glycol (InChI=1S/C24H50O13/c25-1-3-27-5-7-29-9-11-31-13-15-33-17-19-35-21-23-37-24-22-36-20-18-34-16-14-32-12-10-30-8-6-28-4-2-26/h25-26H,1-24H2)
  • Hexaethylene glycol (InChI=1S/C12H26O7/c13-1-3-15-5-7-17-9-11-19-12-10-18-8-6-16-4-2-14/h13-14H,1-12H2)
  • Nonaethylene glycol, (InChI=1S/C18H38O10/c19-1-3-21-5-7-23-9-11-25-13-15-27-17-18-28-16-14-26-12-10-24-8-6-22-4-2-20/h19-20H,1-18H2)
  • Octaethylene glycol (InChI=1S/C16H34O9/c17-1-3-19-5-7-21-9-11-23-13-15-25-16-14-24-12-10-22-8-6-20-4-2-18/h17-18H,1-16H2)
  • Pentaethylene glycol (InChI=1S/C10H22O6/c11-1-3-13-5-7-15-9-10-16-8-6-14-4-2-12/h11-12H,1-10H2)
Substances (generic terms)
  • Alcohol ethoxylates
  • Alky sulfates
  • Alkyethoxysulfates
  • Alkylether sulfates
  • Benzenesulfonic acids
  • Coconut diethanolamides
  • Dialkyl tetralinsulfonates
  • ethoxylated melamines
  • ethoxylated Tetramethylbutylphenols
  • glycolether sulfates
  • Linear alkylbenzene sulfonates
  • Linear alkylethoxylates
  • Nonylphenol carboxylates
  • Nonylphenol ethoxylate sulfates
  • Nonylphenol ethoxylates
  • Octylphenol carboxylates
  • Octylphenol ethoxylates
  • Polyethylene dimethyl ethers
  • Polyethylene glycols
  • Polymeric substances, surfactants :
  • Polypropylene glycols
  • Secondary alkane sulfonates
  • Sulfophenyl alkyl carboxylic acids
  • wastewater treatment (WWTP)
  • 2018-03 TO 2020-03
Geographic Name(s)
  • ARA Neugut, Dübendorf
Review Level none
Curator Mairinger, Teresa
DOI 10.25678/00049T