Literature DB >> 35572800

Data on occurrence of perfluoroalkyl substances in influents and effluents collected from different wastewater treatment plants in Latvia.

Dzintars Zacs1, Elina Pasecnaja1,2, Vadims Bartkevics1,2.   

Abstract

The data set provided in this paper contains occurrence data of 17 perfluoroalkyl substances (PFAS) (including 10 perfluorinated carboxylic acids and 7 perfluorinated sulfonic acids) in influent and effluent samples collected from 43 wastewater treatment plants (WWTPs) located in different cities in Latvia. Samples were collected in the period June-July 2021. In each WWTP one influent and one effluent sample were collected on the same day. Extraction and clean-up of the samples were performed using solid phase extraction (SPE) on a weak-anion SPE phase. Observed extracts were analysed using high performance liquid chromatography coupled with Orbitrap high resolution mass spectrometry (HPLC-Orbitrap-MS) on the content of selected PFAS representatives. The collected data are with fundamental scientific value and can be applied for local data analysis. The data set is useful for the estimation of overall background levels of PFAS and evaluation of local city WWTPs wastewater remediation efficiency towards the removal of PFAS contamination.
© 2022 The Author(s). Published by Elsevier Inc.

Entities:  

Keywords:  Occurrence; Perfluorocarboxylic acid; Perfluorosulfonic acid; Wastewater

Year:  2022        PMID: 35572800      PMCID: PMC9092855          DOI: 10.1016/j.dib.2022.108228

Source DB:  PubMed          Journal:  Data Brief        ISSN: 2352-3409


Specifications Table

Value of the Data

Perfluorinated substances transport and spread in the environment through WWTPs are of increasing concern, with a lack of data available in Latvia. These data offer a comprehensive overview of the occurrence of 17 perfluorinated carboxylic and sulfonic acids in influents and effluents collected from different WWTPs in Latvia. The data can be valuable for researchers studying contaminant transfer into the environment through the WWTPs. These data may be used by local authorities, policy makers and researchers to improve the environmental quality standards. These data may be valuable in the optimisation of WWTP operation conditions. These data may contribute to the existing worldwide need of monitoring data for PFAS to support future prioritisation of relevant compounds and the development of guidelines by national and international authorities.

Data Description

The presented data were obtained during a comprehensive monitoring study on the occurrence of 17 PFAS in influent and effluent samples collected from 43 WWTPs located in different regions of Latvia. Results are expressed as nanogram per liter concentrations (ng L−1). Data presented include (1) mapping of sampling locations in different regions of Latvia (Fig. 1); (2) datasets with concentrations of selected PFAS in influent wastewater collected before any treatment and concentrations in effluent wastewater collected immediately before the discharge from WWTP (Table 1); (3) constructed boxplots for datasets (Fig. 2).
Fig. 1

The distribution of sampling locations throughout Latvia.

Table 1

Dataset with concentrations of selected PFAS in influent wastewater collected before any treatment and concentrations in effluent wastewater collected immediately before the discharge from WWTP.

Sampling locationCoordinatesPFPeAPFHxAPFHpAPFOAPFNAPFDAPFUdAPFDoAPFTrDAPFTeDAPFBSPFPeSPFHxSPFHpSPFOSPFNSPFDS
WWTP "Piebalgas", Vecumnieki district, influent56.60057, 24.494471.142.691.193.061.210.790.15<LOQ<LOQ<LOQ0.570.140.250.050.22<LOQ<LOQ
WWTP "Piebalgas", Vecumnieki district, effluent0.992.861.114.700.840.450.01<LOQ<LOQ<LOQ0.33<LOQ0.100.050.46<LOQ0.82
WWTP "Uzvara", Bauska district, influent56.31715, 24.195180.300.140.082.040.110.01<LOQ<LOQ<LOQ<LOQ0.22<LOQ<LOQ<LOQ0.110.030.11
WWTP "Uzvara", Bauska district, effluent0.450.290.120.750.110.03<LOQ<LOQ<LOQ<LOQ0.29<LOQ<LOQ<LOQ0.35<LOQ<LOQ
WWTP "Nākotne", Jelgava region influent56.61932, 23.443941.012.402.741.920.810.03<LOQ<LOQ<LOQ<LOQ0.31<LOQ<LOQ<LOQ0.46<LOQ<LOQ
WWTP "Nākotne Jelgava region effluent1.201.102.090.820.760.080.01<LOQ<LOQ<LOQ0.48<LOQ<LOQ0.020.40<LOQ<LOQ
Vilce village WWTP, Jelgava region, influent56.37061, 23.525691.094.060.575.020.290.10<LOQ<LOQ<LOQ<LOQ0.53<LOQ0.040.200.29<LOQ0.68
Vilce village WWTP, Jelgava region, effluent0.902.160.431.620.240.14<LOQ<LOQ<LOQ<LOQ0.53<LOQ<LOQ0.020.34<LOQ0.07
Kalnciems village WWTP, Kalnciems, influent56.80218, 23.605590.792.628.501.320.540.190.02<LOQ<LOQ<LOQ1.02<LOQ0.05<LOQ0.40<LOQ0.36
Kalnciems village WWTP, Kalnciems, effluent1.601.292.5464.1<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ0.69<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ
Ezernieki WWTP, Ezernieki, influent56.81207, 26.565850.011.200.150.890.240.12<LOQ0.04<LOQ<LOQ0.220.530.21<LOQ0.430.45<LOQ
Ezernieki WWTP, Ezernieki, effluent0.030.830.193.710.200.05<LOQ<LOQ<LOQ<LOQ0.510.01<LOQ0.021.290.02<LOQ
Naujene WWTP, Naujene parish, influent55.94411, 26.75450.072.771.392.190.520.12<LOQ<LOQ<LOQ<LOQ1.040.40<LOQ<LOQ1.970.180.10
Naujenes WWTP, Naujenes parish, effluent0.122.190.872.680.690.17<LOQ<LOQ<LOQ<LOQ0.940.080.03<LOQ1.430.150.03
Rudzāti WWTP, Rudzāti, influent56.45533, 26.471090.010.820.221.500.190.09<LOQ<LOQ<LOQ<LOQ0.390.010.06<LOQ0.72<LOQ<LOQ
Rudzāti WWTP, Rudzāti, effluent0.020.500.292.050.07<LOQ<LOQ<LOQ<LOQ<LOQ0.550.000.15<LOQ0.470.02<LOQ
Viesīte WWTP, Viesīte, influent56.34486, 25.560320.063.710.261.690.460.10<LOQ<LOQ<LOQ<LOQ0.600.080.58<LOQ1.69<LOQ<LOQ
Viesīte WWTP, Viesīte, effluent0.011.720.196.480.660.18<LOQ<LOQ<LOQ<LOQ1.090.050.02<LOQ1.150.02<LOQ
Aknīste WWTP, Aknīste, influent56.15973, 25.744280.134.410.443.082.020.11<LOQ<LOQ<LOQ<LOQ0.470.070.15<LOQ0.770.150.12
Aknīste WWTP, Aknīste, discharge0.122.310.097.432.730.24<LOQ0.09<LOQ<LOQ0.730.340.41<LOQ1.480.130.07
Straupe PKS, "Pienotava", Straupe parish, influent57.34699, 24.94770.032.420.081.780.090.03<LOQ0.02<LOQ<LOQ0.190.07<LOQ<LOQ0.270.090.12
Straupe PKS, "Pienotava", Straupe parish, effluent0.010.360.051.17<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ0.25<LOQ<LOQ<LOQ0.12<LOQ<LOQ
SIA "Rūjienas siltums", Rūjiena, influent57.89389, 25.339330.011.561.122.490.710.17<LOQ0.020.01<LOQ0.820.26<LOQ0.052.21<LOQ<LOQ
SIA "Rūjienas siltums", Rūjiena, effluent4.246.783.583.271.030.12<LOQ<LOQ<LOQ<LOQ12.50.190.190.054.51<LOQ<LOQ
SIA "Salagrīvas ūdens" WWTP, Salacgrīva, influent57.75813, 24.354340.031.622.363.322.520.25<LOQ0.07<LOQ<LOQ0.590.562.251.4741.781.88<LOQ
SIA "Salagrīvas ūdens" WWTP, Salacgrīva, effluent0.591.850.946.232.270.19<LOQ<LOQ<LOQ<LOQ0.980.081.110.368.40<LOQ<LOQ
Turaida village WWTP, influent57.18226, 24.850280.422.030.411.370.350.31<LOQ0.100.01<LOQ0.610.150.06<LOQ0.74<LOQ<LOQ
Turaida village WWTP, effluent0.101.280.132.240.130.09<LOQ<LOQ<LOQ<LOQ0.490.010.020.030.350.01<LOQ
Līgatne biological WWTP, influent57.23633, 25.038070.011.170.372.780.470.090.050.18<LOQ<LOQ0.500.02<LOQ0.000.46<LOQ<LOQ
Līgatne biological WWTP, effluent0.031.710.440.990.240.02<LOQ<LOQ<LOQ<LOQ0.550.060.020.050.45<LOQ<LOQ
Sēlija WWTP, Sēlpils parish, influent56.52801, 25.613120.021.460.240.910.170.050.020.04<LOQ<LOQ0.260.010.41<LOQ0.610.00<LOQ
Sēlija WWTP, Sēlpils parish, effluent0.021.720.791.200.180.030.020.03<LOQ<LOQ0.300.010.43<LOQ0.75<LOQ<LOQ
Ozolmuiža village, WWTP BIO II 300, Ozolmuiža parish, influent56.49696, 27.27792<LOQ1.080.070.620.080.040.020.01<LOQ<LOQ0.130.000.380.000.760.01<LOQ
Ozolmuiža village, WWTP BIO II 300, Ozolmuiža parish, effluent0.011.760.130.320.090.020.020.02<LOQ<LOQ0.13<LOQ0.40<LOQ0.51<LOQ<LOQ
SIA "Gulbenes nami", Pilskalna village WWTP, Gulbene district, influent57.28817, 26.787240.011.380.380.650.110.04<LOQ0.04<LOQ<LOQ0.220.020.430.010.77<LOQ0.01
SIA "Gulbenes nami", Pilskalna village WWTP, Gulbene district, effluent0.011.700.411.020.050.040.010.04<LOQ<LOQ0.470.030.430.010.84<LOQ<LOQ
Skriveri SAC "Ziedugravas" WWTP ASD BX −100, Skriveri district, influent56.63707, 25.114340.010.890.110.560.170.150.000.02<LOQ<LOQ0.150.010.43<LOQ1.39<LOQ0.02
Skriveri SAC "Ziedugravas" WWTP ASD BX −100, Skriveri district, effluent<LOQ1.090.130.390.190.090.010.04<LOQ<LOQ0.340.010.43<LOQ1.04<LOQ<LOQ
Žīguri village, WWTP BIO KRB 60, Žīguru parish, influent57.29366, 27.672041.112.131.862.671.070.15<LOQ<LOQ<LOQ<LOQ1.68<LOQ0.02<LOQ2.09<LOQ<LOQ
Žīguri village, WWTP BIO KRB 60, Žīguru parish, effluent0.681.001.522.110.940.11<LOQ<LOQ<LOQ<LOQ1.770.060.11<LOQ1.35<LOQ<LOQ
Vilaka WWTP BIO - 240, Vilaka, influent57.18795, 27.68250.030.674.041.329.280.070.020.070.190.130.620.08<LOQ<LOQ0.89<LOQ0.16
Vilaka WWTP BIO - 240, Vilaka, effluent0.270.863.251.9810.20.04<LOQ<LOQ<LOQ<LOQ0.750.11<LOQ<LOQ0.970.080.02
Ludza, WWTP BIO-2800, Isnaudas parish, influent56.48444, 27.835916.347.455.8910.14.010.60<LOQ<LOQ0.030.181.75<LOQ0.11<LOQ2.29<LOQ<LOQ
Ludza, WWTP BIO-2800, Isnaudas parish, effluent4.355.571.534.181.570.19<LOQ<LOQ<LOQ<LOQ1.70<LOQ0.07<LOQ1.78<LOQ<LOQ
Nirzas village, WWTP BIO M 27,5 × 2, Nirzas parish, influent56.39374, 27.90853<LOQ0.840.310.981.080.08<LOQ<LOQ<LOQ<LOQ0.11<LOQ<LOQ<LOQ0.18<LOQ<LOQ
Nirzas village, WWTP BIO M 27,5 × 2, Nirzas parish, effluent0.340.940.592.231.240.25<LOQ<LOQ<LOQ<LOQ0.33<LOQ<LOQ0.020.65<LOQ<LOQ
Raipole village WWTP BIO 50 (Mechanical), "Lupinas", Kusneri, Nirzas parish, influent56.37307, 27.895860.010.050.251.280.160.200.03<LOQ<LOQ<LOQ0.06<LOQ<LOQ<LOQ0.34<LOQ2.17
Raipole village WWTP BIO 50 (Mechanical), "Lupinas", Kusneri, Nirzas parish, effluent0.01<LOQ0.100.070.04<LOQ<LOQ<LOQ<LOQ<LOQ0.07<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ
SIA "Madonas ūdens", Liezēres WWTP BIO-DRY-S-45, Liezēre, Madona district, influent57.03367, 26.052360.080.200.180.410.08<LOQ<LOQ<LOQ<LOQ<LOQ0.08<LOQ0.07<LOQ0.80<LOQ0.12
SIA "Madonas ūdens", LiezēresWWTP BIO-DRY-S-45, Liezēre, Madona district, effluent0.521.310.791.420.330.11<LOQ<LOQ<LOQ<LOQ0.510.07<LOQ<LOQ1.56<LOQ<LOQ
SIA "Mālpils piensaimnieks" WWTP, Mālpils region, influent57.00842, 24.95752<LOQ<LOQ0.120.230.020.01<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ0.25<LOQ0.03
SIA "Mālpils piensaimnieks" WWTP, Mālpils, Mālpils region, effluent<LOQ<LOQ0.180.950.060.03<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ0.02
SIA "Saltavots" WWTP, "Jaunlorupes", Sigulda region, influent57.14387, 24.934760.192.390.682.110.210.15<LOQ<LOQ<LOQ<LOQ2.170.08<LOQ<LOQ0.85<LOQ<LOQ
SIA "Saltavots" WWTP, "Jaunlorupes", Sigulda region, effluent<LOQ<LOQ0.453.920.140.03<LOQ<LOQ<LOQ<LOQ0.420.00<LOQ<LOQ0.210.01<LOQ
SIA "Ādažu ūdens" "Centre treatment plant", Ādažu district, influent57.06847, 24.33940.083.221.366.450.360.28<LOQ<LOQ<LOQ<LOQ0.300.01<LOQ<LOQ<LOQ<LOQ0.03
SIA "Ādažu ūdens" "Centre treatment plant", Ādažu district, effluent2.615.331.306.830.290.10<LOQ<LOQ<LOQ<LOQ4.23<LOQ<LOQ<LOQ0.26<LOQ<LOQ
JSC "Olainfarm", production WWTP, Olaine region, influent56.7892, 23.95962<LOQ<LOQ2.481.640.460.04<LOQ<LOQ<LOQ<LOQ0.49<LOQ<LOQ<LOQ<LOQ<LOQ<LOQ
JSC "Olainfarm", production WWTP, Olaine region, effluent1.001.768.412.070.940.05<LOQ<LOQ<LOQ<LOQ0.76<LOQ<LOQ<LOQ0.18<LOQ0.03
PSIA "Vangažu avots" WWTP "Kārļzemnieki", Inčukalns district, influent57.09544, 24.650320.010.660.686.360.380.360.010.02<LOQ0.000.40<LOQ<LOQ<LOQ0.29<LOQ0.02
PSIA "Vangažu avots" WWTP "Kārļzemnieki", Inčukalns district, effluent0.000.520.431.900.200.200.01<LOQ<LOQ<LOQ0.180.00<LOQ<LOQ0.49<LOQ<LOQ
JSC "Jaunpils pienotava" WWTP, influent56.72998, 23.016580.300.980.041.050.150.02<LOQ0.11<LOQ<LOQ0.400.080.04<LOQ1.080.150.48
JSC "Jaunpils pienotava" WWTP, effluent0.410.97<LOQ0.370.060.01<LOQ0.02<LOQ<LOQ0.130.09<LOQ0.021.230.090.08
Valdeku village WWTP influent56.99956, 22.772590.240.650.170.950.290.400.751.401.791.060.420.180.17<LOQ1.840.58<LOQ
Valdeku village WWTP effluent1.232.520.792.490.390.24<LOQ<LOQ<LOQ<LOQ0.910.050.790.083.03<LOQ<LOQ
Kazdanga WWTP "Avenes", Aizpute region, influent56.73262, 21.73280.050.560.054.070.280.06<LOQ0.03<LOQ<LOQ0.280.570.05<LOQ2.460.44<LOQ
Kazdanga WWTP "Avenes", Aizpute region, effluent0.140.620.131.350.270.02<LOQ0.01<LOQ<LOQ0.530.780.130.491.96<LOQ<LOQ
SIA "Durbes KS" WWTP Raibenieki, Durbe district, influent56.62798, 21.491620.120.52<LOQ1.060.290.09<LOQ0.01<LOQ<LOQ0.391.38<LOQ<LOQ6.210.33<LOQ
SIA "Durbes KS" WWTP Raibenieki, Durbe district, effluent0.261.210.357.570.190.08<LOQ0.02<LOQ<LOQ0.430.040.350.061.43<LOQ<LOQ
WWTP "Cīruļi", Valdgale parish, influent57.35444, 22.375650.452.130.292.510.66<LOQ<LOQ0.04<LOQ<LOQ0.981.990.290.234.300.25<LOQ
WWTP "Cīruļi", Valdgale parish, influent0.392.680.067.070.67<LOQ0.010.010.040.020.722.690.06<LOQ5.46<LOQ<LOQ
WWTP, Viduskurzeme AAO, Brocēnu region, influent56.73475, 22.635731169152840680159.432.81.881.190.990.745325.334065.02201<LOQ<LOQ
WWTP, Viduskurzeme AAO, Brocēnu region, effluent1115157424023719.64.010.210.20<LOQ<LOQ3464.142400.0064.80.000.00
SIA "Madonas ūdens", Laudona WWTP BI0-KRD-17, Madona District, influent56.70736, 26.193540.013.120.831.590.280.10<LOQ0.01<LOQ0.000.470.010.440.011.110.090.09
SIA "Madonas ūdens", Laudona WWTP BI0-KRD-17, Madona District, effluent1.183.681.827.540.710.380.01<LOQ<LOQ<LOQ0.26<LOQ<LOQ<LOQ1.57<LOQ0.03
SIA "Olaines ūdens un siltums", municipal WWTP, Olaine district, influent56.78967, 23.929570.762.782.463.950.750.240.10<LOQ<LOQ<LOQ8.480.060.06<LOQ0.95<LOQ0.02
SIA "Olaines ūdens un siltums", municipal WWTP, Olaine district, effluent0.582.492.533.550.440.05<LOQ<LOQ<LOQ<LOQ13.30.030.02<LOQ0.18<LOQ<LOQ
SIA "Gulbenes nami", Lizuma village WWTP, Gulbene district, influent57.21902, 26.36204<LOQ0.870.160.480.10<LOQ0.010.05<LOQ<LOQ0.430.080.50<LOQ0.64<LOQ<LOQ
SIA "Gulbenes nami", Lizuma village WWTP, Gulbene district, effluent1.071.850.370.560.120.080.01<LOQ<LOQ<LOQ0.43<LOQ<LOQ0.040.38<LOQ<LOQ
JSC "Rankas piens", Ranka WWTP, Gulbene district, influent57.17309, 26.761970.310.590.301.060.050.02<LOQ<LOQ<LOQ<LOQ0.36<LOQ<LOQ0.090.12<LOQ0.07
JSC "Rankas piens", Ranka WWTP, Gulbene district, effluent0.021.380.240.640.040.03<LOQ0.04<LOQ<LOQ0.320.020.430.000.71<LOQ<LOQ
Abavnieki village WWTP influent56.97438, 22.931970.330.630.081.590.38<LOQ0.010.040.02<LOQ1.221.760.080.7020.5<LOQ<LOQ
Abavnieki village WWTP effluent0.661.270.381.040.100.04<LOQ<LOQ<LOQ<LOQ0.920.04<LOQ<LOQ0.95<LOQ<LOQ
Popes WWTP "Pope", Popes Parish, influent57.44606, 21.879235.708.420.2510.41.911.370.210.070.490.552.950.170.250.207.34<LOQ<LOQ
Popes WWTP "Pope", Popes Parish, effluent0.491.370.440.790.200.110.07<LOQ<LOQ<LOQ0.440.030.030.080.470.030.27
SIA "L LIKO FARM", Strazdi, Saldus district, influent56.59974, 22.412080.01<LOQ1.032.030.210.080.02<LOQ<LOQ<LOQ0.380.04<LOQ<LOQ0.60<LOQ<LOQ
SIA "L LIKO FARM", Strazdi, Saldus district, effluent0.561.400.944.860.280.070.010.03<LOQ<LOQ0.790.130.94<LOQ1.85<LOQ<LOQ
Fig. 2

Boxplots of the concentrations of selected PFAS in analysed influents and effluents.

The distribution of sampling locations throughout Latvia. Dataset with concentrations of selected PFAS in influent wastewater collected before any treatment and concentrations in effluent wastewater collected immediately before the discharge from WWTP. Boxplots of the concentrations of selected PFAS in analysed influents and effluents.

Experimental Design, Materials and Methods

Wastewater aliquots were collected into 1 L brown coloured glass bottles and transferred to the laboratory at + 4 °C. Samples were stored at +4 °C and treated within seven days of receipt. Selected PFAS were analysed according to the previously published method with minor modifications in order to extend the scope of the target analytes [1]. 250 mL sample aliquots were spiked with 13C-isotopically labeled PFAS surrogates (5 ng of each component) served as internal standards and then 100 µL of formic acid was added to each sample. Samples were loaded at a flow rate of ∼ 5 mL min−1 on the weak anion-exchange SPE columns (Strata-X-AW 200 mg/3 mL (Phenomenex, Torrance, CA, USA)), which were previously pre-washed with 3 mL of 1% NH4OH in MTBE/MeOH (90:10, v/v), 3 mL of MeOH, and 3 mL of ultra-pure water. After the sample loading, the SPE cartridges were washed with 1 mL of 2% formic acid and 2 mL of MeOH, and after drying the cartridges for 30 min under vacuum, the analytes were eluted with 7 mL of 1% NH4OH in MTBE/MeOH (90/10, v/v) to a 10 mL glass vial. Eluted extracts were evaporated to dryness under a gentle stream of nitrogen at 30 °C, reconstituted with MeOH (100 µL) and subjected to the HPLC-Orbitrap-MS analysis. Prepared extracts were analysed within three days of sample preparation. Instrumental analysis was performed using HPLC-Orbitrap-MS operated in parallel reaction monitoring (PRM) mode, with detection of negative ions. Quantitation was carried out using isotope dilution and internal standardisation method with selected 13C-labeled surrogates. The results from real samples were corrected by subtracting the PFAS concentrtions of the procedural blanks (see Supporting Information) analysed in each sample sequence. Method accuracy was controlled by the analysis of certified reference material (CRM) Standard Reference Material 2781 Domestic Sludge (NIST, Gaithersburg, MD, USA), which was analysed in each sample run in the frame of the current study. Boxplots were constructed for datasets as follows: the horizontal line within the box represents the distribution median. The ends of the box represent the 25th and 75th percentiles, while the interquartile range (IQR) is the difference between the 25th and 75th percentiles. The lines that extend from each end are whiskers, from the ends of the box to the outermost data point that falls within the distances computed as follows: 1st quartile−1.5 × (IQR) 3rd quartile +1.5 × (IQR).

Ethics Statement

Not applicable.

CRediT authorship contribution statement

Dzintars Zacs: Methodology, Writing – original draft, Visualization. Elina Pasecnaja: Methodology, Software, Data curation. Vadims Bartkevics: Supervision, Writing – review & editing.

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
SubjectEnvironmental Science
Specific subject areaEmerging Contaminants in the environment
Type of dataTablesFigure
How the data were acquiredHigh performance liquid chromatography coupled with Orbitrap high resolution mass spectrometry (Thermo Scientific UltiMate 3000 HPLC coupled with Thermo Scientific Orbitrap Q-Exactive mass spectrometer). Xcalibur™ Software.
Data formatRaw;Analysed
Description of data collectionWastewater samples were collected into 1 L brown coloured glass bottles and transferred to the laboratory at + 4 °C. Samples were stored at +4 °C and extracted within seven days of receipt. Samples were extracted by weak-anion exchange solid phase extraction and subjected to HPLC-Orbitrap-MS analysis.
Data source locationInstitution: Institute of Food Safety, Animal Health and Environment “BIOR”• City: Riga• Country: Latvia• Latitude and longitude for monitoring points are presented in Table 1
Data accessibilityThe data are available within this article

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