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Determination of atrazine and propazine metabolites deemed endocrine disruptors in human seminal plasma by LC–ESI-MS/MS



The increasing prevalence of male infertility and the declining trend in sperm quality has been associated to compounds known as “endocrine-disruptors”. The proven endocrine-disrupting effects of atrazine and propazine herbicides led us to conduct long-term research based on highly accurate specific analytical methods with a view to confirming the suspected association. Among the proposed developments was a sensitive analytical method for the simultaneous determination of three metabolites of atrazine and propazine.


In this work, the method was for first time used for the chromatographic separation and determination of deethyl- and deisopropyl-atrazine (DEA and DIA, respectively) and propazine-2-hydroxy (PP-2OH) in human seminal plasma by LC–ESI-MS/MS using deuterated atrazine (d5-AT) as internal standard (IS). Chromatographic and mass spectrometric conditions such as the mobile phase composition and flow-rate, injected volume, dry gas source temperature and flow-rate, nebulizer pressure and capillary voltage were all carefully optimized. Analytes were identified and quantified by using the multiple reaction monitoring (MRM) mode as applied to positive ions ([M + H]+). Transitions at three different m/z values for each analyte were selected from precursor ions, and the 212.1 → [128]+, 188.1 → [146]+ and 174.1 → [68.1]+ transitions for PP-2OH, DEA and DIA, respectively, were found to be quantitative. The proposed method was validated in terms of precision (repeatability and reproducibility), linear range (10–240 ng mL–1), limit of detection (150–210 pg mL–1), and quantification (500–700 pg mL–1), recovery, accuracy and matrix effects on extracts from variably treated seminal plasma samples. The overall analytical method was successfully applied to human seminal plasma samples from volunteers. PP-2OH was found at concentrations from 1.10 to 11.3 ng mL–1 in four of the six samples, and so was DIA at 9.60 ng mL–1 in one.


These results are suggestive of bioaccumulation of the target analytes in humans. Untargeted analytes including suspected parent molecules (atrazine and propazine) and other ions [viz., deethyldeisopropyl-atrazine (DD) and diamino-s-chlorotriazine (DACT)] were also detected under the working conditions used. These results may open up new prospects for as yet very incipient research into the bioaccumulation of endocrine disruptors in seminal plasma.

Graphical Abstract


Defective sperm function can arise from a wide range of primary genetic, lifestyle and environmental factors acting alone or, more frequently, in combination. Recently, Selvaraju et al. (2020) reviewed the effects of environmental contaminants on male reproductive function and their potential mechanisms of action. They concluded that environmental contaminants, which are typically chemicals, have deleterious effects on male reproduction [1]. According to the United States Environmental Protection Agency (US-EPA), an endocrine disrupting chemical (EDC) is “an exogenous agent that interferes with synthesis, secretion, transport, metabolism, binding action, or elimination of natural blood-borne hormones that are present in the body and are responsible for homeostasis, reproduction, and developmental process” [2, 3]. EDCs, which have been deemed a global threat to public health by the World Health Organization (WHO), are arousing increasing interest [4]. These compounds are highly heterogeneous in nature and have been classified according a number of factors [2] including physico-chemical properties, environmental persistence and bioaccumulation in humans [5]. The production and use of various chemicals as additives in agriculture has grown substantially in recent decades. Some such chemicals can have harmful effects on health, so their release and/or accumulation in the environment or in food chains is a cause for concern. Among those harmful chemicals are triazine pesticides, a family of organic compounds differing in the substituents on the triazine ring.

s-Triazines (particularly atrazine, simazine and propazine) are used worldwide as selective pre- and post-emergence herbicides for weed control on many agricultural crops such as corn, wheat and barley, as well as on railways, roadsides and golf courses [6]. Atrazine is the second most widely used herbicide in agriculture [7] after glyphosate, while propazine is used mainly as an herbicide for indoor greenhouse plants, and also to control broadleaf and grassy weeds on sorghum [8].

Agriculturally used triazines can undergo biotic and non-biotic degradation through de-alkylation of amine groups at positions 4 and 6 on the triazine ring, dechlorination, de-amination or hydrolysis of the substituent at 2 [9], and to a lesser extent, even ring cleavage [10,11,12,13], to variety of derivatives. Atrazine, propazine and also their derivatives can accumulate in soil and contaminate ground and surface water as a result. In this way, they can reach various organisms and have mutagenic, teratogenic or endocrine disrupting effects on them [14]. Also, they can reach the human body through consumption of contaminated food or water, or exposure to aerosols—which can enter the respiratory tract or be absorbed through the skin [15].

Physiologically, heavy exposure to these herbicides can alter hepatic microsomal metabolism to a variable extent depending on the particular species [16]. However, no metabolic or pharmacokinetic studies on atrazine or propazine in humans, the potentials effects of the parent compounds or their metabolites on living organisms, or their bioaccumulation, have been conducted to date. In fact, only a few studies have explored the metabolism of atrazine and propazine in vitro or in vivo. Atrazine is metabolized primarily by cytochrome P450s (CYPs) and, to a lesser extent, by glutathione transferases (GSTs) [16,17,18]. The major CYP-derived metabolites of atrazine are deethylatrazine (DEA) and deisopropylatrazine (DIA). Both are metabolized to diamino-s-chlorotriazine (DACT) [8, 19], which is the major atrazine metabolite detected in vivo in rats [20]; however, the enzyme effecting its formation remains unknown [16, 21]. Between 8–12 metabolites of atrazine conjugated [22] via glutathione s-transferases [23] have been identified in urinary metabolites profile [24].

In 2016, US EPA deemed the chlorometabolites DIA, DEA and deethyldeisopropyl atrazine (DD) toxicologically equipotent to the parent triazines, but considered the conjugated derivatives toxicologically inactive metabolites [8]. The metabolism of propazine has scarcely been examined in vivo or in vitro [16, 18]. Hanioka et al. (1999) detected no N-bidealkylation or 2-hydroxylation metabolites in any of the previous systems. However, propazine 2-hydroxy (PP-2OH), which is similarly toxic to the parent triazine, has been identified among the degradation products formed in the natural environment [9]. Because it is hardly metabolized under physiological conditions, PP-2OH may be an effective marker for bioaccumulation. Owing to their biological activity and high mobility, triazine pesticides have aroused great environmental concern for many years [25, 26]. Some studies have focused on the detection of s-triazine herbicides in diverse environments [13] by examining atrazine and its major transformation products in waters and soils, mainly [13, 25, 27, 28]. Their presence in biological samples has been less frequently studied [29], and mainly in urine and plasma [20, 24], even though fluids such as semen and seminal plasma can contain highly useful information about bioaccumulation of pollutants [30] potentially associated to male infertility [31,32,33].

Seminal plasma represents 95% of human semen, which includes secretions from accessory sex glands and plays a key role in natural fertilization as it contributes to timely capacitation, acrosome reaction and sperm–oocyte interaction [34]. Its complex proteomic composition, and growth and transcription factors, provide a safe environment for spermatozoa; also, ejaculated semen serves as a vehicle for spermatozoa to the female genital tract. Human seminal plasma is a rich source of potential biomarkers for male infertility and reproduction disorders [32]. Exposure to some drugs, toxins or pollutants can affect seminal plasma and alter sperm function even after ejaculation [14], and molecular alterations may contribute to male infertility [35]. Information on the metabolome of healthy human semen is rather scant, however [36]. For example, propazine has scarcely been examined in this respect, and the effects of atrazine on sperm have been studied to a limited extent only. As found in other studies, atrazine can behave as an anti-androgen, xenoestrogen and oestrogen agonist [37]. Epidemiological studies conducted in USA have revealed sperm concentration and motility to be reduced by atrazine exposure in humans [38]. Based on the foregoing, s-triazines can have a deleterious impact on human reproductive health.

Although the analysis of compounds present in complex biological matrices such as seminal plasma is challenging, recent advances have enabled the identification of toxins and pharmaceuticals such as nicotine [39] elvitegravir [40] and tadalafil [41], and endocrine disruptors (bisphenol A [42,43,44] and phthalates [45], mainly), in seminal plasma. To our knowledge, however, no determinations of triazine compounds and/or their metabolites in human semen or seminal plasma have been reported to date. The scarcity of pharmacokinetic and metabolic information on triazines such as atrazine and propazine, and the potential oestrogenic activity of some metabolites (DIA and DEA) and degradation products (PP-2OH) according EPA [46], could be expanded by developing an effective analytical method for their determination in human seminal plasma. In this work, we developed the first accurate, sensitive, selective method for the simultaneous determination of two active intermediate metabolites of atrazine (DIA and DEA), and the degradation product of propazine PP-2OH, which US EPA has deemed endocrine disruptors. Under the optimum conditions established here, the proposed method, which uses liquid chromatography coupled to mass spectrometry detection (MSD) via an electrospray ionization interface (LC–ESI/MS), allowed the unequivocal identification and accurate quantification of the target analytes in seminal plasma. The samples were previously subjected to enzymatic hydrolysis (EH) and solid-phase extraction (SPE) in order to isolate the analytes, clean-up and preconcentrate the final extract.

Materials and methods


The atrazine and propazine metabolites 2-OH-propazine (99.0% pure), deethyl and deisopropyl atrazine (97.5% and 99.5%, respectively) were purchased from Dr Ehrenstorfer GmbH (Augsburg, Germany) and stored at –20 °C. Five times deuterated (d5)-atrazine [viz., 6-chloro-2-N-(1,1,2,2,2-pentadeuteredethyl)-4-N-propan-2-il-1,3,5-triazine-2,4-diamine) from Sigma-Aldrich (St. Louis, MO, USA) was used as internal standard (IS). Acetonitrile and methanol in HPLC grade were purchased from Honeywell Research Chemicals Riedel-de Häen (Seelze, Germany) and ethanol (analytical-grade) was obtained from Panreac (Barcelona, Spain). Acetic and phosphoric acid 99% and 85% pure, respectively, were supplied by VWR International Eurolab and Scharlab (Barcelona, Spain), respectively. The enzyme (type HP2 β-glucuronidase, 116 300 IU mL−1) was obtained from Sigma-Aldrich (St. Louis, MO, USA).

All solutions were prepared in de-ionized water (18.2 mΩ cm–1) from a Milli-Q apparatus (Millipore Ibérica S.A., Madrid, Spain), and high-purity, zero-grade nitrogen was used for the ESI source and detector (triple quadrupole).

Standard and stock solutions

A known amount of each analyte was dissolved in 50 mL of ethanol to a final concentration of 1008 μg mL–1 for DIA, and 1000 μg mL–1 for DEA and PP-2OH. All stock solutions were stored at –20 °C. Medium solutions of each individual compound (IS included) at a 50 μg mL–1 concentration were prepared in ethanol and stored at 4–8 °C in the dark. Finally, working mixed solutions were prepared by diluting the medium-solutions to a concentration of 500 ng mL–1 in mobile phase (a 85:15 v/v mixture of 0.1% acetic acid and acetonitrile) and stored at 4–8 °C. The working solutions were used in all validation tests irrespective of matrix type.

Biological samples: collection, storage and treatment

Collection of sperm and storage of seminal plasma

Human sperm was obtained from six healthy sperm donors selected according to ESHRE guidelines for gamete donation of the Bernabeu Institute (Albacete, Spain). Samples were collected after 48–72 h of abstinence and handled according to the WHO’s 2010 guidelines. Seminal plasma was extracted by centrifuging the ejaculates at 12.000 × g at 4 °C for 20 min. The resulting supernatants were stored at − 20 °C until they were further used following re-centrifugation under the same conditions.

Ovine sperm for validation purposes was obtained from three adult rams of the Manchega breed aged 3 years or more reared on the farm of the University of Castilla–La Mancha. Semen was collected by using an artificial vagina and seminal plasma extracted by centrifuging the ejaculates al 12.000 × g at 4 °C for 20 min. The resulting supernatants were stored at –20 °C until they were further used following re-centrifugation under the same conditions. All animal procedures were performed in accordance with Spanish Animal Protection Regulation RD53/2013, which conforms to European Union Regulation 2010/63/UE.

Sample treatment

Stored seminal plasma samples were treated according to previously established protocols. Briefly, a volume 500 μL of seminal plasma was centrifuged at 16,000 × g at 4 °C for 10 min and subsequently subjected to enzymatic hydrolysis. For this purpose, 5 μL of β-glucuronidase and a known amount of IS (d5-AT) were added to centrifuged plasma, which was then vortexed for 2 min and incubated at 37 °C for 12 h. Then, a supernatant volume was further vortexed and re-centrifuged under the same conditions. Isolation and preconcentration were done by using a Manifold Visiprep™ solid-phase extractor (SPE) from Sep-Pack (Madrid, Spain) coupled to an XF 54 23050 vacuum pump from Millipore. The SPE process was conducted with Sep-Pack Plus Bond Elut C18 cartridges (200 mg, 3 mL, 50/pk) from Waters (Milford, CT, USA). The extraction–preconcentration procedure involved the following steps: (1) conditioning of the cartridge by washing with 2.0 mL of methanol and 2.0 mL of de-ionized water; (2) loading of organic extract (500 μL) at 0.5 mL min–1; (3) drying of the cartridge for 2 min; (4) washing with 2.0 mL of de-ionized water three times to minimize interferences from the seminal plasma matrix; (5) drying for 5 min and (6) elution of the analytes with 4.0 mL of an 80:20 v/v acetonitrile:methanol mixture three times. The eluate thus obtained was transferred into 5.0-mL conical glass vessels and the organic extract evaporated with nitrogen gas for dissolution in 100 μL of mobile phase and injection into the LC/ESI-MS/MS system.

Liquid chromatography and mass spectrometry conditions

Analytes were separated on an Agilent 1260 Infinity HPLC system equipped with a binary pump and a vacuum degasser. Samples were injected with an Agilent autosampler furnished with a needle of 25 µL and analysed on a model 6460 triple quadrupole mass spectrometer from Agilent Technologies (Santa Clara, CA, USA) equipped with an ESI interface. Zero-grade nitrogen was supplied by a nitrogen generator from PEAK Scientific (Chicago, IL, USA) and high-purity hydrogen was obtained from Linde (Valencia, Spain).

Analytes were separated by gradient elution at 0.3 mL min–1 from a Zorbax SB-Aq column (2.1 × 100 mm, 1.8 μm) at 25 °C. The mobile phase was a 85:15 v/v mixture of 0.1% acetic acid (A) and acetonitrile (B). The elution programme was as follows: 15% B for 4 min, 85% B in 1 min for 4 min and back to 15% B in 1 min holding 5 min. The injected volumes of standard and sample were always 10 μL.

The optimum operating conditions for the ESI source were a dry gas temperature of 300 °C, a gas flow-rate of 11 L min–1, a nebulizer pressure of 15 p.s.i, a capillary voltage of 4000 V and a chamber/corona current of 0.26 μA. Analytes were detected and quantified by applying the Multiple Reaction Monitoring (MRM) mode to positive ions to acquire at least three transitions for each metabolite (see Table 1), the most abundant transition of the three being used for quantitative analysis and the other two for qualitative analysis.

Table 1 Chemical features, response to electrospray ionization and chromatographic retention time for each metabolite


The reliability of the proposed method for determining male infertility-related metabolites was established by using triplicate injections to assess signal intensity, relative peak area (RPA) and signal-to-noise (S/N) ratio. Also, analytical performance-related parameters such as precision, limit of detection (LOD), limit of quantitation (LOQ) and linearity were assessed in bio-extracts from spiked blank samples treated as described in “Biological samples: collection, storage and treatment” Section (sample treatment).

Results and discussion

Development of the analytical method

The operational chromatographic and mass spectrometry conditions were adjusted for optimal separation and determination of the analytes and maximization of chromatographic peaks and analytical signals (abundance and stability).

Preliminary studies

The chromatographic conditions for the simultaneous separation of DIA, DEA, PP-2OH and the internal standard (deuterated atrazine, d5-AT) were established in preliminary tests. The initially selected chromatographic conditions were as follows: the reverse mode; a C18 column 100 mm long × 2.1 mm i.d. packed with particles 1.8 μm in diameter as stationary phase; and isocratic elution with a mobile phase consisting of a 70:30 v/v mixture of 0.1% formic acid and methanol. These conditions resulted in split and rather broad chromatographic peaks, a low efficacy (N) and poor resolution (RS) between peaks.

Because the target metabolites were highly polar (see their chemical structures in Fig. 1), they had a low affinity for the stationary phase and were thus weakly retained on it. This led us to increase the proportion of aqueous phase in order to delay elution of the analytes for increased contact with the stationary phase of the column in order to facilitate their chromatographic separation. We thus considered other stationary phases allowing higher proportions of aqueous component to be used in the mobile phase. For this purpose, we replaced conventional C18 column previously used, with a 100 mm long × 2.1 mm i.d. Zorbax SB-Aq column packed with particles 1.8 μm in diameter. This column is chemically similar to a C18 column and can operate in the reverse mode, but allows a very low proportion or even no organic component to be used for elution. As a result, it provided better peak shapes and higher efficiency throughout. Peak shape, and hence separation between peaks, was improved by increasing the proportion of water in the mobile phase. This, however, diminished peak height and S/N ratio or even led to no signal being obtained with high proportions of water, which led us to consider other types of mobile phase and alternative conditions.

Fig. 1
figure 1

MS fragmentation precursor ion for each metabolites

Optimization of LC conditions

The chromatographic variables composition, elution mode and mobile phase flow-rate were adjusted for optimal signal strength, and peak shape and separation. The procedure was as follows:

  1. (a)

    Because formic acid does not affect ionization, it was removed from the organic phase and replaced with acetic acid in the same proportion in the aqueous phase.

  2. (b)

    Methanol was replaced with acetonitrile as organic solvent in the mobile phase, which substantially improved peak shape and signal stability.

  3. (c)

    Mobile phases containing 0.1% acetic acid:acetonitrile ranged between 70 and 100% acetic acid were used in the isocratic and gradient modes.

With isocratic elution, an 85:15 v/v acetic acid (A)–acetonitrile (B) mobile phase provided acceptable resolution among analytes, albeit with an overall analysis time longer than 25 min owing to the IS. Tests were therefore repeated in the gradient mode, using variable proportions of acetic acid in the mobile phase to reduce analysis times, and improve chromatographic separation and peak shape.

The most effective elution gradient was using an initial mobile phase composition of 85:15 (A:B v/v) for 4 min, reducing the proportion of acetic acid from 85 to 15% in 1 min keeping for 4 min and then back to the initial conditions (85:15 v/v) in 1 min for 5 min to decrease the IS retention time (RT). Under these conditions, the three metabolites and the IS were separated within 10 min (Fig. 2).

Fig. 2
figure 2

Extracted ion chromatograms for atrazine and propazine metabolites as obtained under selected instrumental conditions as MRM window: 1º) internal standard (d5-atrazine); 2º) PP-2OH (propazine metabolite); 3º) DIA and 4º) DEA (atrazine metabolites)

None of the other chromatographic variables studied (viz., mobile phase flow-rate, column temperature and injected volume) had a critical effect on the analyte separation efficiency. The influence of the mobile phase flow-rate and column temperature was examined over the ranges 0.2–0.6 mL min–1 and 20–40 °C, respectively. A flow-rate of 0.3 mL min–1 and a temperature 25 °C were deemed optimal in terms of peak shape, efficiency and retention time for the three analytes. With biological samples, however, it is essential to use an optimal injected volume as well. An increased injected volume (i.e. an increased amount of sample) is expected to introduce greater amounts of biological components into the system—and hence to result in stronger interferences of the biological matrix with the column leading to impaired analyte separation. By contrast, very low injected volumes led to scarcely reproducible results subject to large errors. The influence of the injected volume was examined over the range 5–20 μL and 10 μL selected as the best trade-off between sensitivity and reproducibility.

Optimization of MS/MS parameters

The main purpose of optimizing the MS/MS variables was ensuring stable, reproducible, selective signals. To this end, the influence of ionization-related parameters such as nebulizer flow-rate, temperature and pressure, and that of other variables such as precursor ion, product and transitions were also examined.

Firstly, we selected the best precursor ion to characterize each analyte from the most abundant ions detected in the full-scan mode. Specific precursor ion-related variables such as transitions, fragmentor voltage (V) and collision energy (eV) were automatically proposed by using the Optimizer function in the software MassHunter from Agilent. At least three transitions from the precursor to the product ions must be selected to ensure accurate quantification and unambiguous identification of each compound.

The assignment of product ion from precursor ion mass of PP-2OH, DEA and DIA is given in Fig. 1. The highest transitions of each precursor ion are used for quantification and the remainder for qualitative identification. In all analytes, ionization was more stable and sensitive in the positive ion mode ([M + H]+) than it was in the negative mode ([M–H]). The m/z values for the transitions of each compound, and their collision energies, were as follows:

  1. (a)

    PP-2OH. [M + H]+  = 212.1 → [170.1]+, 16 eV; [212.1]+  → [128.0]+, 20 eV; and [212.1]+  → [86.1]+, 32 eV. Fragmentor = 166 V.

  2. (b)

    DEA. [M + H]+  = 188.1 → [146]+, 16 eV; [188.1]+  → [79.0]+, 28 eV; and [188.1]+  → [68.1]+, 32 eV. Fragmentor = 98 V.

  3. (c)

    DIA. [M + H]+  = 174.1 → 96.1, 20 eV; [174.1]+  → [68.1]+, 32 eV; and [174.1]+  → [62.1]+, 56 eV. Fragmentor = 98 V.

Table 1 shows the chemical structure, formula, molecular weight, characteristic transitions, collision energy, fragmentor value and retention time for each analyte.

Related operational variables such as dry gas flow-rate, gas temperature and nebulizer pressure have a direct impact on the ionization process and were thus also examined over the ranges afforded by the equipment, namely: 5–13 L min–1, 250–350 °C and 10–60 p.s.i. A flow-rate of 11 L min–1, a temperature of 300 °C and a pressure of 15 p.s.i were selected as optimal as they provided the highest RPA, stable signals and the highest possible S/N ratio. A capillary voltage of 4000 V and chamber/corona current of 0.26 μA were also used.

Analytes were detected and later quantified by using positive ion polarity in the multiple reaction monitoring (MRM) mode in addition to the total ion chromatogram (TIC) obtained in the full scan and the combination of selected transitions, respectively, for each compound.

Validation of the proposed method

The proposed method was validated by confirming that it fulfilled the requirements for which it was developed and provided the results expected from it. For this purpose, the method was assessed in terms of precision, LOD and LOQ, response linearity, recoveries and matrix effects by using bio-extracts from ovine seminal plasma. Specifically, a pooled sample (n = 3) of previously analysed ram seminal plasma was used as a blank matrix for validation.

Treatment of biological samples: recovery and matrix effects

The general procedure for extraction of biological samples can include the following steps: (a) optional protein denaturation, protein precipitation or deproteination; (b) extraction or isolation by liquid–liquid extraction (LLE), solid-phase extraction (SPE), dilution, shooting, etc.; and (c) preconcentration (optional) and reconstitution. Each step in the previous, provenly effective process is intended to facilitate complete extraction of analytes from biological samples. Based on previous work [21, 34], and on the specific type of biological sample used (seminal plasma), we examined the effectiveness of various sample treatments after SPE, namely: (a) enzymatic hydrolysis (EH); (b) acid hydrolysis (AH) and (c) protein precipitation (PP) with an organic solvent. All were performed in two steps different in purpose. Thus, EH, AH and PP were intended to remove the largest possible amounts of interferents from the samples in order to reduce matrix effects; on the other hand, SPE was used to facilitate isolation and preconcentration of the target analytes.

The previous treatments were used to assessed for performance by using working-strength standards and seminal plasma blanks (viz., samples containing no detectable concentrations of the analytes). The latter samples were spiked with the analytes at the beginning of each treatment or after extraction in order to determine recoveries and matrix effects, respectively. The seminal plasma samples were first defrosted at room temperature to obtain 500 μL aliquots that were centrifuged at 16.000 × g at 4 °C for 10 min. The influence of the experimental variables (viz., nature and volume of the organic and aqueous solvents used in the washing steps, sample volume, eluted volume and final extract volume, among others) was examined after each step of the SPE process. The high complexity of the seminal plasma matrix, where the analytes were present at very low levels, required using SPE for preconcentration and clean-up in addition to separation.

The procedure for each analyte was as follows:

  • EH-SPE. A volume of 5 μL of β-glucuronidase solution was added to the supernatant, vortexed for 2 min and incubated at 37 °C for 12 h. SPE was done with Bond Elut™ C18 SPE (200 mg, 3 mL), the reversed-phase sorbent being previously conditioned by passing 2.0 mL of methanol and 2.0 mL of de-ionized water. Then, each incubated sample (approximately 500 μL) was slowly loaded onto the cartridge at flow-rate of 0.5 mL min–1, the cartridge being washed at 1.0 mL min–1 with 2.0 mL of water three times. Next, the metabolites were eluted with 4 mL of 80:20 v/v acetonitrile:methanol and the eluates dried under a stream of nitrogen. The final residue was redissolved in 100 μL of previously used mobile phase for injection into the LC–MS equipment.

  • AH-SPE. The supernatant obtained by centrifugation (around 500 μL) was given up to 2.0 mL of 5 % phosphoric acid and subjected to SPE like the previous analyte but using an appropriate initial volume of sample. Also, the final residue was redissolved in mobile phase and injected into the LC–MS equipment.

  • PP-SPE. A 250-μL aliquot of the supernatant obtained by centrifugation was supplied with an identical volume of ethanol and centrifuged under the same conditions as the previous analytes for 10 min. Then, the analytes were isolated by using an appropriate volume in each SPE step. The resulting residue was redissolved in mobile phase for injection into the LC–MS equipment.

Analyte recovery with the EH-SPE treatment was 89.2% for PP-2OH, 90.9% for DEA and 92.1% for DIA by contrast, recoveries with AH-SPE and PP-SPE were all less than 50%. Comparing RPA between samples spiked after extraction and those for working-strength standards of identical concentration allowed us to estimate matrix effects, which were deemed not significant when the difference from the normalized value for each analyte was less than 10%. The differences were 15–18% with the EH-SPE treatment and 28–43% with the others.

Based on the previous results, the EH-SPE treatment was the best choice as it provided recoveries about of 90% with relative standard deviations (RSD) less than 20%. In fact, the other two treatments gave poor recoveries (< 50%) and were subject to heavy matrix effects. Further validation testing provided RSD values fulfilling the US FDA guidelines for bioanalysis methods.

Analytical quality: precision, LOD, LOQ and linear range

Precision was assessed as repeatability and reproducibility, both in terms of RSD. Repeatability was estimated from the retention time (RT), absolutes (A) and relative peak areas (RPA) for each analyte by replicate analysis (n = 10) of a 100 ng mL–1 working-strength solution. RSD was less than 2 and 4% for RT, A and RPA, respectively, in all cases.

Within-day and between-day reproducibility were estimated in terms of Snedecor’s F-value as determined by sequentially injecting 10 freshly prepared samples under identical conditions at 24-h intervals. Differences between variances (S2) were not significant, so Fexp was less than Ftab for all instrumental variables.

The limits of determination (LOD) and quantification (LOQ) were calculated from replicate analyses (n = 5) of working-strength solutions diluted in mobile phase. LOD ranged from 150 to 210 pg mL–1 and LOQ from 500 to 700 pg mL–1, both with RSD < 20% in all cases.

Linearity in the analytical response was assessed by relating the concentration of each analyte to RPA in tests with mixtures of standards containing PP-2OH, DIA and DEA at concentrations from 10 and 240 ng mL–1 in mobile phase and the internal standard at a fixed concentration of 100 ng mL–1. Aliquots (10 μL) of these solutions were injected in triplicate into the chromatographic system and processed as described above. Figure 3 shows the equation of the curve for each analyte as determined by least-squares regression and their coefficients.

Fig. 3
figure 3

Calibration plot spanning the linear range 10.0–240.0 ng mL–1 for PP-2OH metabolite and calibration data for all metabolites

Application of the proposed method to human semen samples

The proposed method was applied by determining the analytes in human semen samples. Whole semen samples were previously centrifuged to obtain seminal plasma as described in “Collection of sperm and storage of seminal plasma” Section and then subjected to EH-SPE. Table 2 summarizes the quantitative and semi-qualitative results obtained by subjecting 6 samples to the overall analytical process. MRM was used for targeted analysis and the SCAN mode for untargeted analysis in order to obtain more information and detect other suspected compounds potentially eluted together with the analytes.

Table 2 Semi-qualitative and quantitative analysis of targeted (DEA, DIA and PP-2OH) and suspected molecules in human semen samples (n = 6)

PP-2OH metabolite was detected and quantified in four of the six samples, at concentrations from 1.1 to 11.3 ng mL–1. Figure 4 shows the extracted ion chromatograms for sample 2, which allowed the PP-2OH and DIA metabolites to be quantified at a concentration of 11.3 and 9.6 ng mL–1, respectively. These metabolites were unequivocally identified from chromatographic RT and characteristic quantitative and qualitative transitions. Only two of the six samples contained no detectable concentrations of any metabolites (DEA, DIA or PP-2OH).

Fig. 4
figure 4

Extracted ion chromatograms for sample 2 including quantitative and qualitative transitions of a d5-AT (IS), b PP-2OH and c DIA in seminal plasma

In other way untargeted analysis in the SCAN mode allowed three different types of ions to be detected as suspected molecules: (a) precursor molecules such as AT and/or PP; (b) other s-triazines and their metabolites (ametrine, prometrine, terbutrine, DACT and DD, among others) and (c) unknown ions. As can be seen from Table 2, all samples contained at least one type of named untargeted compound. Thus, samples 1, 3 and 6 gave several chromatographic peaks for unknown compounds. Also, sample 1 exhibited ions at a RT of 1.53 and 2.26 min with an m/z ratio of 146.0 and 228.0, respectively, for [M + H]+. These ions could correspond to deethyldeisopropyl atrazine or diamino s-chlorotriazine (mw = 145.5 g mol–1) and ametrine (mw 227.3 g mol–1), respectively. Another major ion, [349.9]+, was observed at RT of 4.57 min. Samples 3 and 6 gave an identical chromatographic peak with a quantitative transition coinciding with that of DEA metabolite but at different RT (1.2 min). Samples 4 and 5 also gave an identical chromatographic peak with RT = 8.5 min and a m/z ratio of 230.7 for the [M + H]+ ion possibly corresponding to propazine (mw = 229.7 g mol–1) as it had a higher RT than its metabolite but close to that for deuterated-AT. Both samples were found to contain PP-2OH metabolite at trace levels (1.1–2.7 ng mL–1), which suggests that propazine was still largely in non-metabolized form.

Because it was containing the greatest number of metabolites, sample 2 was subjected to exhaustive untargeted analysis (results not shown). The full-scan chromatogram for this sample included peaks for the most polar ions eluted at a near-zero time (0.98 min) such as [104.0]+ and [197.0]+, which are chemically similar to those for the targets metabolites at RT of 2.0–3.5 min (viz., [506.1]+ and [508.2]+), in addition to a group of more strongly retained—and hence less polar—ions including [375.1]+, [391.0]+ and [393.0]+, with RT similar to those for atrazine and propazine.

After everything discussed above, the proposed method allowed the accurate identification and quantification of targeted and monitoring of untargeted suspected s-triazines potentially associated to sperm viability, mitochondrial activity, oxidative stress and DNA damage. Seminal plasma could be the ideal model sample for further testing with a view to the unequivocal identification of unknown compounds with a high-resolution mass spectrometry detector (e.g., TOF) that may have been previously detected through the use of targeted mass spectrometry detectors (e.g., QQQ).


A selective, fast analytical method was developed for the simultaneous determination of three atrazine and propazine metabolites (DIA, DEA and PP-2OH) in human seminal plasma by using a deuterated internal standard. The samples were previously subjected to enzymatic hydrolysis (EH) and SPE, and the resulting extract was preconcentrated to obtain recoveries around 90% with RSD < 20%. Only 10 μL of biological extract was needed to successfully quantify the target analytes at trace (nanogram-per-millilitre) concentration levels by LC/ESI-MS/MS. Validation procedure confirmed that the proposed method is an accurate, precise, sensitive analytical tool with a broad linearity range for the intended purpose. Application to human semen samples from six donors revealed that the method could be useful to relate the quality of semen to its contents in endocrine disruptors. PP-2OH and DIA were found in four of the six samples studied, at concentrations over the range 1.10–11.3 ng mL–1 and 9.60 ng mL–1, respectively. This result provides for first time potential evidence for the bioaccumulation of s-triazine metabolites in humans. Other, suspected compounds and metabolites such as PP, DD, and DACT might have also been present in the samples. Therefore, in order to confirm the results and to conclude on the presence of unknown molecule it will be mandatory to made others studies using high-resolution mass spectrometry detector.

Our optimized, validated analytical method for the qualitative and quantitative determination of triazine metabolites in human seminal plasma may be very useful for practical purposes since their concentration levels in biological fluids may be related to male infertility. The method may therefore open up new avenues for research into the effects of endocrine disruptors present in seminal plasma on various sperm-related parameters—and hence on sperm physiology. Thus, the method could be used to conduct broad-based studies on the potential association of endocrine disruptors and their metabolites in seminal plasma to male infertility, and may thus be useful to examine the impact of sperm physiology on male reproduction function (especially when male fertility is compromised).

To our knowledge, ours is the first method enabling the detection of s-triazine metabolites in seminal plasma, which might be useful with a view to developing effective treatments for male infertility associated to endocrine disruption in the future.

Availability of data and materials

The data presented in this study are available on request from the corresponding author.



Liquid chromatography


Mass spectrometry


Liquid chromatography-electrospray ionization


Mass spectrometry


Triple quadrupole


Endocrine disrupting chemical


Relative standard deviation


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The authors thank the Bernabeu Institute for its collaboration in this work and for allowing the collection of the seminal plasma samples.


The authors thank the financial support given by the 01110AB025 I + D + i research project given by the Diputación de Albacete and was also funded by the financial support given by the University of Castilla–La Mancha, Spain. The authors have no other relevant affiliations or financial involvement with any organization or entity with a financial interest in or financial conflict with the subject matter or materials discussed in the manuscript apart from those disclosed. No writing assistance was utilized in the production of this manuscript. Ministerio de Ciencia, Innovación y Universidades.

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VRR has contributed to the conception and design of the work and has drafted the work. VRR, AV and AG-C have participated to the acquisition and analysis of data. NV-G and CG-C have contributed to the analysis and interpretation of data. LLM has provided the human samples and contributed to the acquisition and analysis of data. JJG and MRF-S have participates to the conception of the research and approved the submitted version and substantively revised the work. All authors read and approved the final manuscript.

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Correspondence to Virginia Rodríguez-Robledo or María Rocío Fernández-Santos.

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Rodríguez-Robledo, V., Vendrell, A., García-Cifuentes, A. et al. Determination of atrazine and propazine metabolites deemed endocrine disruptors in human seminal plasma by LC–ESI-MS/MS. Chem. Biol. Technol. Agric. 9, 22 (2022).

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  • Endocrine disruptors
  • s-Triazine metabolites
  • Male infertility
  • Human seminal plasma