Literature DB >> 32765110

Fetal Programming of Semen Quality (FEPOS) Cohort - A DNBC Male-Offspring Cohort.

Birgit Bjerre Høyer1, Sandra Søgaard Tøttenborg1, Katia Keglberg Hærvig1,2, Jens Peter Bonde1,2, Cecilia Høst Ramlau-Hansen3, Gunnar Toft4, Karin Sørig Hougaard2,5, Ina Olmer Specht6, Aleksander Giwercman7, Anne-Marie Nybo Andersen2, Jørn Olsen3, Christian Lindh8.   

Abstract

BACKGROUND: Prenatal exposures may contribute to male infertility in adult life, but large-scale epidemiological evidence is still lacking. The Fetal Programming of Semen quality (FEPOS) cohort was founded to provide means to examine if fetal exposures can interfere with fetal reproductive development and ultimately lead to reduced semen quality and reproductive hormone imbalances in young adult men.
METHODS: Young adult men at least 18 years and 9 months of age born to women in the Danish National Birth Cohort living in relative proximity to Copenhagen or Aarhus and for whom a maternal blood sample and two maternal interviews during pregnancy were available were invited to FEPOS. Recruitment began in March 2017 and ended in December 2019. The participants answered a comprehensive questionnaire and underwent a physical examination where they delivered a semen, urine, and hair sample, measured their own testicular volume, and had blood drawn.
RESULTS: In total 21,623 sons fulfilled eligibility criteria of whom 5697 were invited and 1058 participated making the response rate 19%. Semen characteristics did not differ between sons from the Copenhagen and Aarhus clinics. When comparing the FEPOS semen parameters to similar cohorts, the median across all semen characteristics was slightly lower for FEPOS participants, although with smaller variation.
CONCLUSION: With its 1058 young adult men, the FEPOS cohort is the largest population-based male-offspring cohort worldwide specifically designed to investigate prenatal determinants of semen quality. Wide-ranging information on maternal health, lifestyle, socioeconomic status, occupation, and serum concentrations of potential reproductive toxicants during pregnancy combined with biological markers of fertility in their sons collected after puberty allow for in-depth investigations of the 'fetal origins of adult disease hypothesis'.
© 2020 Keglberg Hærvig et al.

Entities:  

Keywords:  fetal exposure; male infertility; maternal-fetal exchange; prenatal exposure; semen analysis; semen quality

Year:  2020        PMID: 32765110      PMCID: PMC7373412          DOI: 10.2147/CLEP.S242631

Source DB:  PubMed          Journal:  Clin Epidemiol        ISSN: 1179-1349            Impact factor:   4.790


Introduction

Infertility is the most common chronic disease among people of reproductive age, and affects up to 15–25% of all couples trying to achieve a pregnancy.1–3 Male factor infertility is a contributing factor in up to half of these cases.4 Around 40% of Danish men have a semen concentration below 40 million/mL, from where the probability for conception gradually decreases.5 Several factors in adult life have been linked to reduced semen quality, including lifestyle such as smoking, chronic alcohol use, obesity, sleep, and nutrition6–12 and occupational and environmental exposures such as sedentary work, radiation, air pollution, bisphenol A, parabens, organophosphate pesticides, pyrethroids, and phthalates.13–17 Still, subfertility remains unexplained for many, and the underlying causes are far from understood. According to the ‘fetal origins of adult disease hypothesis’ suggested by Barker and Osmond in 1986, the environment encountered during fetal life is strongly related to the risk of developing non-communicable diseases later in life.18 This was supported by Sharpe and Skakkebæk,19 who subsequently proposed that hypospadias, cryptorchidism, poor semen quality, and testicular cancer are symptoms of one underlying entity with a common fetal origin.20,21 Although an increasing number of studies of maternal lifestyle and health during pregnancy, such as maternal diet, alcohol consumption, smoking, medication use, and obesity support this fetal programming hypothesis,22–27 large-scale epidemiological evidence is still lacking – especially regarding maternal exposure to endocrine disrupting chemicals at home and at work.28 The limited body of evidence is likely explained by the complex logistics and high costs of establishing long-term longitudinal population-based studies of male reproductive function, with information on exposures during early life, such as the need for detailed maternal information and bio-specimens stored for decades before follow-up. The Fetal Programming of Semen quality (FEPOS) cohort is nested within the Danish National Birth Cohort (DNBC)29,30 and was founded to provide means to examine if fetal exposures can interfere with fetal reproductive development and ultimately lead to reduced semen quality and reproductive hormone imbalances in young adult men.

Methods

Study Population

In March 2017, FEPOS was established as a male-offspring sub-cohort within the DNBC. In total, 49,653 sons were born into the DNBC cohort. A full flow chart of the sampling strategy is depicted in Figure 1. Sons eligible to participate in FEPOS should still be enrolled in the DNBC (N=46,911) with mothers having participated in the two maternal computer-assisted telephone interviews conducted around gestational week 16 and 31 (N=41,518) and with a stored gestational blood sample in the DNBC biobank (N=39,725).30 Further, the FEPOS participants had to be at least 18 years and 9 months of age within the study period (N=24,024) (this arbitrary age cut off was due to an 18-year follow-up in the original DNBC cohort), not dead or emigrated (N=23,425) and live in Zealand (N=8817) or Jutland (N=12,806) in relative proximity to the FEPOS clinics in Copenhagen or Aarhus. Thus, the total number of young men eligible for invitation was 21,623.
Figure 1

Flowchart of the sampling strategy and recruitment process of the FEPOS cohort.

Flowchart of the sampling strategy and recruitment process of the FEPOS cohort. The Aarhus clinic included participants until June 2018 where it was closed due to a lack of funding. The Copenhagen clinic included participants in the entire study period that ended in December 2019. In total, 5697 men were invited and 1058 participated making the response rate 19%.

Recruitment Logistics

Using a digitalized and comprehensive recruitment system, eligible sons were randomly selected for invitation to participate on an ongoing basis during the study period (Figure 2). The monthly number of sons invited varied in the two clinics according to capacity. An invitation letter was sent to the young men’s personal and secure digital mailbox “e-Boks” linked to the unique personal identification number. E-Boks is automatically created at the age of 15 years and used for bi-directional communication with public and private authorities, eg to receive pay checks or bank statements.31 The invitation letter included information about the study and an electronic option to be contacted for additional information or decline participation. The invitation letter specified that participants who had undergone sterilization, cancer treatment, orchidectomy, or had one or no testicles were ineligible. Of the 5697 invited sons 1880 requested more information and were contacted by telephone by a member of the project group. Those still wishing to participate after the verbal information was given (N=1453), received an electronic informed consent form by e-Boks. Upon digitally consenting using their common secure login “NemID” (N=1248), participants received links to an online questionnaire and booking system to schedule an appointment for a clinical examination at the clinic closest to their home (Figure 3). After answering the online questionnaire (N=1174) participants underwent a clinical examination (N=1058). At each step of contact, non-responders were sent two reminders by e-Boks, with 14 days interval, and at the initial invitation a final reminder was sent by regular mail. Participants were each remunerated 500 DKK (≈ 67 Euro).
Figure 2

Overview of the cumulative number of invited and participants in the FEPOS cohort during the study period from March 2017 to December 2019.

Figure 3

Map of the residence of participants in the FEPOS cohort.

Overview of the cumulative number of invited and participants in the FEPOS cohort during the study period from March 2017 to December 2019. Map of the residence of participants in the FEPOS cohort.

Data and Measurements

An overview of data collected from the questionnaire and clinical examination data is presented in Table 1.
Table 1

Overview of Data Available on the FEPOS Cohort

CategoryData SourceVariables
Prenatal exposure data*
LifestyleDNBC telephone interview at gestational weeks 16 and 31AlcoholCaffeineSmokingPhysical activityPre-pregnancy body mass indexStressDietary supplements
EmploymentDNBC telephone interview at gestational weeks 16 and 31WorkWorkload (only first interview)
Health and medicine useDNBC telephone interview at gestational weeks 16 and 31DiseasesOver the counter pain medicationPrescribed medicationNonsteroidal anti-inflammatory drugs (NSAIDs)
ReproductionDNBC telephone interview at gestational weeks 16 and 31Age of onset of pubertyMenstrual cycle characteristicsBirth controlInfertility treatmentWeight gain during pregnancy
VitaminsMaternal plasma from gestational week 7 or 26Vitamin D3
Biomarkers of perfluoroalkyl acid exposure (PFFA)Maternal plasma from gestational week 7 or 26Perfluorohexane sulfonic acid (PFHxS)Perfluorooctanoic acid (PFOA)Perfluorooctane sulfonic acid (PFOS)Perfluoroheptanoic acid (PFHpA) Perfluorononanoic acid (PFNA)Perfluorodecanoic acid (PFDA)Perfluoroundecanoic acid (PFUnDA)Perfluorododecanoic acid (PFDoDA)
Biomarkers of phthalate exposureMaternal plasma from gestational week 7 or 26Mono-(2-ethyl-5-oxohexyl) phthalate (5-oxo-MEHP) Mono-(2-ethyl-5-hydroxyhexyl) phthalate (5-OH-MEHP)Mono-(2-ethyl-5-carboxypentyl) phthalate (5-cx-MEPP)Mono-(4-methyl-7-carboxyheptyl) phthalate (cx-MiNP)
Biomarkers of additional xenobioticsMaternal plasma from gestational week 7 or 26Triclosan§Cotinine§Acetaminophen (APAP)
Data on sons’ own exposures
LifestyleFEPOS questionnaireDietAlcoholCaffeineSmokingPhysical activityNarcotic drugs
Education and workFEPOS questionnaireEducational levelWork
HealthFEPOS questionnaireDiseasesMedication
Puberty and sexual experienceFEPOS questionnairePubertySexual experience
Physical testsClinical examinationBlood pressureFat and muscle distributionLung functionTesticle size
Semen sampleSemen sample delivered at the clinical examinationSperm concentrationSemen volumeTotal sperm countMorphologyMotilityDNA fragmentation index (DFI)ǂ
VitaminsBlood sample taken at the clinical examinationVitamin D3
HormonesBlood sample taken at the clinical examinationHemoglobin A1c (HbA1c)Follitropin (FSH)Insulin-like Growth Factor I (IGF-1)InsulinLutropin (LH)Thyrotropine (TSH)Thyroxine (T4)Sexual Hormone Binding Globulin (SHBG)TestosteroneThyroxine (Free T4)OestradiolInhibin B
Biomarkers of perfluoroalkyl acid exposure (PFFA)Blood sample taken at the clinical examinationPerfluorohexane sulfonic acid (PFHxS)Perfluorooctane sulfonic acid (PFOS)Perfluoroheptanoic acid (PFHpA)Perfluorooctanoic acid (PFOA) Perfluorononanoic acid (PFNA) Perfluorodecanoic acid (PFDA) Perfluoroundecanoic acid (PFUnDA) Perfluorododecanoic acid (PFDoDA)
Biomarkers of phthalate exposure†§Urine sample taken at the clinical examinationMonoethyl phthalate (MEP)Monobutyl phthalate (MBP)Monobenzyl phthalate (MBzP)Mono-(2-ethylhexyl) phthalate (MEHP)Mono-[2-(carboxymethyl)hexyl] Phthalate (2cx-MEHP) Mono-(4-methyl-7-hydroxyloctyl) phthalate (OH-MiNP)Mono-(4-methyl-7oxo octyl) phthalate (oxo-MiNP) Monocarboxyisonoyl Phthalate (cx-MiDP) Mono-(propyl-6-hydroxyheptyl) phthalate (OH-MPHP)
Biomarkers of phthalate exposure†§Blood and urine taken at the clinical examinationMono-(2-ethyl-5-oxohexyl) phthalate (5-oxo-MEHP) Mono-(2-ethyl-5-hydroxyhexyl) phthalate (5-OH-MEHP)Mono-(2-ethyl-5-carboxypentyl) phthalate (5-cx-MEPP)Mono-(4-methyl-7-carboxyheptyl) phthalate (cx-MiNP)
Biomarkers of bisphenol exposure†§Urine sample taken at the clinical examinationBisphenol A (BPA)Bisphenol S (BPS)Bisphenol F (BPF)
Biomarker of pesticide exposure†§Urine sample taken at the clinical examination3-Phenoxybenzoic acid (3PBA)Trichloropyridinol (TCP)
Biomarker of exposure from urban pollution to polycyclic aromatic hydrocarbons†§Urine sample taken at the clinical examination1-Hydroxypyrene (1-HP)
Biomarker of smoking†§Blood and urine taken at the clinical examinationCotinine
Additional xenobiotic chemicals†§Urine sample taken at the clinical examinationDi-phenylphosphate (DPP)
Additional xenobiotic chemicals†§Blood and urine taken at the clinical examinationTriclosan

Notes: *See DNBC website () for all data available on mothers. †Analyses are ongoing. ‡Analyses await funding. §Information on dilution with density or creatinine is available on all analyses in urine.

Overview of Data Available on the FEPOS Cohort Notes: *See DNBC website () for all data available on mothers. †Analyses are ongoing. ‡Analyses await funding. §Information on dilution with density or creatinine is available on all analyses in urine.

Questionnaire Information

Participants filled out a comprehensive web-based questionnaire administered electronically using SurveyXact. The questionnaire included questions regarding education, work, health, and health behavior (Table 1). Nationally validated questionnaire scales were used where possible.32–35 To ensure that questions were explicit and easily understood by this age group, the questionnaire was tested and revised in a group of nine young men before being sent to the FEPOS participants.

Clinical Examination

The clinical examination was performed by a trained biomedical laboratory technician at either the Department of Occupational and Environmental Medicine at Bispebjerg and Frederiksberg Hospital (Copenhagen) or the Department of Occupational Medicine at Aarhus University Hospital (Aarhus). Height and waist circumference in centimeters were measured using a seca® 213 Height Measure and seca® 201 measuring tape, respectively (seca®, Hamburg, Germany). Body weight in kilos, fat percentage (including visceral fat), fat mass, fat-free mass, water percentage, muscle mass, basal metabolic rate, metabolic age, and bone weight were measured using a MC-780MA Body Composition Analyzer (Tanita®, Tokyo, Japan). Blood pressure was measured three times with 2–3 min interval on the right arm, with a BP A3 Plus monitor (Microlife®, Taipei, Taiwan) at the Aarhus clinic and with an Omron M6 Comfort IT (OMRON Corporation, Kyoto, Japan) at the Copenhagen clinic. Measurements of pulmonary function forced expiratory volume in one second (FEV1) and forced vital capacity (FVC) was measured using an EasyOne® spirometer with EasyOne® disposable Spirette® tubes (ndd Medical Technologies, Inc., Andover, Massachusetts, USA). Testicular size was measured in privacy at the clinic by the participants themselves using a Prader Orchidometer (Bayer AG, Leverkusen, Germany). This method has previously been found valid when compared to measurements by an experienced examiner.36

Assessment of Reproductive Hormones

Nonfasting venous blood samples were collected using VACUETTE® SAFETY Blood Collection Set + Holder (Greiner Bio-One GmbH, Kremsmünster, Austria). Plasma, serum, and whole blood were stored in CryoPure Tubes (Sarstedt, Nümbrecht, Germany) at −80°C until analysis of reproductive hormones including hemoglobin A1c (HbA1c), follitropin (FSH), Insulin-like Growth Factor I (IGF-1), testosterone, Sex hormone-binding globulin (SHBG), insulin, lutropin (LH), thyrotropine (TSH), thyroxine (free T4 and T4), oestradial, and inhibin B. Analyses currently await funding.

Exposure Biomarkers of Xenobiotic Chemicals

Besides blood samples urine samples were collected at the clinics in 150 mL Frascos clear polypropylene containers with polyethylene leak proof screw caps (DELTALAB S.L., Barcelona, Spain), both free of phthalates. Samples were stored at 3–8°C for a maximum of 12 hours before transfer to polypropylene Microtubes (Sarstedt, Nümbrecht, Germany) and storage at −80°C. Maternal plasma (100 µL) was retrieved from the Danish National Biobank (DNB). First trimester plasma samples were preferred, if these were not available, we used second or third trimester plasma samples, in that prioritized order. Vitamin D, cotinine, and a range of exposure biomarkers of several xenobiotic chemicals (Table 1) were analyzed in urine and blood, from both mother and son, using liquid chromatography-triple quadrupole mass spectrometry (QTRAP 5500, AB Sciex, Foster City, CA, USA; LC-MS/MS).37–40 The analysis was performed at the Division of Occupational and Environmental Medicine at Lund University, Sweden. Analyses are ongoing – thus far 559 urine samples, 555 blood samples and 533 maternal plasma samples have been analyzed. The laboratory in Lund is a reference laboratory for bisphenol A (BPA) analysis in urine and is part of Erlangen Round Robin inter-laboratory control program for analysis for triclosan, cotinine, trichloropyridinol (TCP), 3-phenoxybencoic acid (3-PBA) and perfluoroalkyl acid (PFAA). The laboratory has qualified as HBM4EU laboratory for the analysis of: BPA, Bisphenol F (BPF), Bisphenol S (BPS), 1-Hydroxypyren (1-HP) and Cyclohexane-1,2-dicarboxylate-mono(oxo-isononyl) ester (oxo-MINCH) and the phthalates; Monobenzyl (MBzP), Mono-(2-ethylhexyl) (MEHP), Mono-(4-methyl-7-carboxyheptyl) (cx-MiNP), Mono-(4-methyl-7-hydroxyloctyl) (OH-MiNP), Mono-(4-methyl-7oxo octyl) (oxo-MiNP), Mono (2-ethyl-5-oxohexyl) (5-oxo-MEHP), Mono(2-ethyl-5-hydroxyhexyl) (5-OH-MEHP), Mono-(2-ethyl-5-carboxypentyl) (5-cx-MEPP), Perfluoroheptanoic acid (PFHpA), Perfluorooctanoic acid (PFOA), Perfluorononanoic acid (PFNA), Perfluorodecanoic acid (PFDA), Perfluoroundecanoic acid (PFUnDA), Perfluorododecanoic acid (PFDoDA), Perfluorohexane sulfonic acid (PFHxS), and Perfluorooctane sulfonic acid (PFOS).

Hair Samples

Approximately 150 hair strands (~10–20 mg) were cut from the vertex posterior as close to the scalp as possible. The hair strands were stuck on paper with adhesive tape (Lyreco, Marly, France) with clear indication of the hair root, and stored in an envelope at room temperature. The thought was to conduct hair analysis as an indicator of eg stress,41,42 but no specific studies are planned yet.

Semen Samples

Participants had the option to collect the semen sample at the clinic or at home. When choosing the latter, detailed instructions on collection and transportation was sent to the participant together with a polypropylene sample container with a diameter of 79 mm and a height of 22mm, with polyethylene snap-lid (Nerbe Plus GmbH, Winsen/Luhe, Germany) for sample collection. This container was also used to collect the semen sample in the clinic. Participants were informed that they should be sexually abstinent 48–72 hours prior to semen collection. All semen analyses followed the recommendations by the World Health Organization (WHO) 2010.43 Immediately upon receipt in the laboratory, the semen volume was measured by weighing (Scout® SKX222 Portable Precision Balance, OHAU®, Parsippany, New Jersey, USA) of the sample in the pre-weighed container. The sample was then placed in a 37°C HERATherm™ Compact Microbiological Incubator (Thermo Fisher Scientific, Waltham, Massachusetts, USA) for liquefaction. After liquefaction using a TrioMix (Triolab, Brøndby, Denmark), samples were analyzed manually for sperm concentration, total sperm count, and motility using a Compudiff 2000–16 Semen Analyzer (Molek AB, Arsta, Sweden). One trained biomedical laboratory technician affiliated to the clinic in Copenhagen and another to the clinic in Aarhus performed all in-house semen analyses. Sperm concentration was determined on two aliquots of semen samples using a BLAUBRAND® Improved Neubauer Hemocytometer (BRAND®, Wertheim, Germany) diluted with NaHCO3 resolution according to concentration. The diluted semen was transferred to each chamber of the hemocytometer and put in a humid chamber for 10 minutes. Each chamber was examined until at least 200 cells had been counted. Sperm cell motility was determined by counting the proportion of a) progressive sperm; b) non-progressive sperm; c) immotile sperm, on 200 spermatozoa within each of two fresh drops of semen, placed on a preheated (37°C), clean glass slide covered with a cover slip using a Compudiff 2000–16 Semen Analyzer (Molek AB, Arsta, Sweden). Morphology was analyzed at the Reproductive Medicine Centre, Skaane University Hospital, in Malmö, Sweden. DNA fragmentation Index (DFI), measured by flow cytometry semen chromatin structure assay44 was analyzed at the Reproductive Medicine Centre, Skaane University Hospital, in Malmö, Sweden (no results yet). The FEPOS biomedical laboratory technicians participated in a follow-up quality control with the Reproductive Medicine Centre in Malmö where they were originally trained to perform the semen analyses. In January 2018, based on five semen samples, the average coefficient of variation and range for the FEPOS biomedical laboratory technicians versus the reference laboratory were 18.4% (10.1–31.4%) versus 17.6% (1.3–28.3%) for sperm concentration and 12.7% (2.0–26.0%) versus 38.6% (9.1–81.6%) for sperm motility. As the Aarhus clinic would only include participants until June 2018, only the Copenhagen-based clinic followed the ESHRE External Quality Assessment scheme (Centre for Andrology, Karolinska University Hospital, Stockholm, Sweden). The average Z-scores based on four semen samples at each test period; winter 2017, spring 2018, and winter 2018, were −0.04 for semen concentration, −0.60 for motility, and 0.27 for all progressive compared to expert reference examiners. This was comparable to previous studies and well below ± 3, considered acceptable for semen quality measures.45

Biobank

Additional quantities of biological material were collected for long-term storage at −80°C in the DNB at Statens Serum Institut, Copenhagen, Denmark, where all other samples collected within DNBC are also stored. The amounts sent to the DNB were three 2 mL MaxxLine tubes each containing 250 µL semen, three 2 mL MaxxLine tubes with 1.5 mL urine, four 2 mL MaxxLine tubes with 600 µL plasma, four 2 mL MaxxLine tubes containing 600 µL serum, and two 4.5 mL CryoPure tubes with 3.5 mL EDTA whole blood.

Ethical Approval

This study was conducted in accordance with the Declaration of Helsinki. The establishment of the FEPOS cohort was approved by the Scientific Research Ethics Committee for Copenhagen and Frederiksberg (No. H-16,015,857) and the Danish Data Protection Agency (P-2019-503). Recruitment and data collection were also permitted by the Steering Committee of the DNBC (Ref. no. 2016–08).

Results

Cohort Characteristics

Selected maternal characteristics are presented in Table 2. Mean age of the mothers was 30.5 years. Smoking during first trimester was relatively common (23%) and most maternal plasma samples were from the first trimester (92%). Median concentration of mono-(4-methyl-7-carboxyheptyl) phthalate measured in blood was 0.3 ng/mL (10th-90th percentile (p10-p90): 0.2 ng/mL, 0.8 ng/mL) and median PFOS was 26.3 ng/mL (p10-p90: 17.0 ng/mL, 40.1 ng/mL). Selected characteristics of the sons are presented in Table 3. Besides more sons from the Aarhus clinic donating hair samples (90% versus 58% in the Copenhagen clinic) no big differences between sons from the Aarhus clinic and the Copenhagen clinic were observed. Of the 1054 sons who delivered a semen sample 87% chose to do so at the clinics. Azoospermia was detected in 17 (2%) young men. Median mono-(4-methyl-7-carboxyheptyl) phthalate measured in urine was 3.6 ng/mL (p10-p90: 1.0 ng/mL, 12.6 ng/mL) and median PFOS was 4.3 ng/mL (p10-p90: 2.6 ng/mL, 7.2 ng/mL).
Table 2

Selected Maternal Characteristics of the 1057 Mothers to the 1058 Included Sons in the FEPOS Cohort*

CharacteristicsAll
N=1057
Age in years, mean [SD]30.5 [4.2]
Pre-pregnancy body mass index (kg/m2), mean [SD]22.8 [3.6]
Infertility treated, N (%)67 (6)
Smokers, N (%)245 (23)
Cotinine plasma levels (ng/mL), median [p10-p90]0.4 [0.1–50.4]
 Number of samples <LOD of 0.2 ng/mL, N (%)146 (27)
Alcohol consumption (units/week), mean [SD]0.7 [1.1]
Family occupational status, N (%)
 High grade professional357 (34)
 Low grade professional350 (33)
 Skilled worker203 (19)
 Unskilled worker98 (9)
 Student45 (4)
 Unclassified≤5
Plasma sample available, N (%)
 1st trimester blood sample489 (92)
 2nd trimester blood sample42 (8)
 3rd trimester blood sample≤5
Biomarkers of perfluoroalkyl acid exposure (PFFA), median [p10-p90]
 Perfluorooctanoic acid (PFOA) (ng/mL)4.6 [2.5–7.2]
  Number of samples <LOD of 0.02 ng/mL, N (%)0 (0)
 Perfluorooctane sulfonic acid (PFOS) (ng/mL)26.3 [17.0–40.1]
  Number of samples <LOD of 0.02 ng/mL, N (%)0 (0)
Biomarkers of phthalate exposure, median [p10-p90]
 Mono-(2-ethyl-5-oxohexyl) phthalate (5-oxo-MEHP) (ng/mL)0.1 [<LOD-0.3]
  Number of samples <LOD of 0.1 ng/mL, N (%)271 (51)
 Mono-(2-ethyl-5-hydroxyhexyl) phthalate (5-OH-MEHP) (ng/mL)0.2 [0.1–0.9]
  Number of samples <LOD of 0.05 ng/mL, N (%)52 (10)
 Mono-(2-ethyl-5-carboxypentyl) phthalate (5-cx-MEPP) (ng/mL)0.7 [0.4–1.5]
  Number of samples <LOD of 0.05 ng/mL, N (%)0 (0)
 Mono-(4-methyl-7-carboxyheptyl) phthalate (cx-MiNP) (ng/mL)0.3 [0.2–0.8]
  Number of samples <LOD of 0.02 ng/mL, N (%)0 (0)
Biomarkers of additional xenobiotics, median [p10-p90]
 Triclosan (ng/mL)1.3 [<LOD-15.1]
  Number of samples <LOD of 0.1 ng/mL, N (%)107 (20)
 Acetaminophen (APAP) (ng/mL)<LOD [<LOD-1.4]
  Number of samples <LOD of 0.5 ng/mL, N (%)424 (80)

Notes: *One mother had twins. †Analysis is ongoing, so far 532 samples have been analysed. p10-p90: 10th-90th percentile.

Abbreviation: LOD, Limit of detection.

Table 3

Selected Characteristics of 1058 Sons Included in the FEPOS Cohort*

CharacteristicsAllCopenhagen ClinicAarhus Clinic
N=1058N=830N=228
Body Mass Index (kg/m2), mean [SD]22.5 [3.4]22.5 [3.3]22.7 [3.6]
Body Composition analysed, N (%)1055 (100)829 (100)226 (99)
 Body fat mass (kg), mean [SD]11.5 [6.7]11.3 [6.6]12.3 [6.8]
 Muscle mass (kg), mean [SD]60.8 [7.1]61.0 [7.1]60.0 [7.1]
Smoking habits, N (%)
 Daily smoking250 (24)198 (24)52 (23)
 Occasional/former smoker296 (28)241 (29)55 (24)
 Never smoker508 (480)389 (47)119 (52)
Cotinine plasma levels (ng/mL)†§, median [p10-p90]5.8 [0.3–2951.9]11.5 [0.4–2540.1]1.5 [0.3–3124.4]
 Number of samples <LOD of 0.3 ng/mL, N (%)46 (8)24 (7)22 (10)
Alcohol drinker, N (%)984 (93)769 (93)215 (94)
Physical activity, N (%)
 No physical activity184 (18)149 (18)35 (16)
 1 time a week139 (13)107 (13)32 (14)
 2 times a week201 (19)165 (20)36 (16)
 3 times a week220 (21)164 (20)56 (25)
 4 times a week155 (15)121 (15)34 (15)
 ≥5 times a week155 (15)122 (15)33 (15)
Biospecimens collected, N (%)
 Semen1054 (100)829 (100)225 (99)
 Blood1047 (99)821 (99)226 (99)
 Urine1042 (99)819 (99)223 (98)
 Hair690 (65)484 (58)206 (90)
Lung function measured, N (%)1052 (100)826 (100)226 (99)
 Forced Expiratory Volume (FVC), mean [SD]5.6 [0.8]5.6 [0.8]5.3 [1.0]
 Forced Expired Volume in the first second (FEV1), mean [SD]4.6 [0.7]4.7 [0.6]4.4 [0.9]
Ejaculation at the clinic, N (%)910 (87)720 (87)190 (86)
Spillage of semen sample, N (%)182 (17)146 (18)36 (16)
Season of ejaculation, N (%)
 Winter199 (19)146 (18)53 (23)
 Spring205 (19)142 (17)63 (28)
 Summer258 (24)213 (26)45 (20)
 Autumn396 (37)329 (40)67 (29)
Biomarkers of perfluoroalkyl acid exposure (PFFA)†‡, median [p10-p90]
 Perfluorooctanoic acid (PFOA) (ng/mL)1.3 [0.9–2.0]1.4 [0.9–2.1]1.3 [0.9–2.0]
  Number of samples <LOD of 0.02 ng/mL, N (%)0 (0)0 (0)0 (0)
 Perfluorooctane sulfonic acid (PFOS) (ng/mL)4.3 [2.6–7.2]4.1 [2.6–6.5]4.4 [2.8–7.7]
  Number of samples <LOD of 0.02 ng/mL, N (%)0 (0)0 (0)0 (0)
Biomarkers of pesticide exposure§, median [p10-p90]
 Trichloropyridinol (TCP)§ (ng/mL)1.0 [0.3–3.5]1.0 [0.4–3.7]0.9 [0.3–3.2]
  Number of samples <LOD of 0.1 ng/mL, N (%)0 (0)0 (0)0 (0)
 3-Phenoxybencoic acid (3PBA)§ (ng/mL)0.3 [0.1–1.1]0.3 [0.1–1.1]0.3 [0.1–1.3]
  Number of samples <LOD of 0.05 ng/mL, N (%)31 (6)20 (6)11 (5)
Bisphenol A (BPA)†§, median [p10-p90]1.3 [0.3–5.5]1.4 [0.4–6.6]1.2 [0.3–4.7]
 Number of samples <LOD of 0.2 ng/mL, N (%)19 (3)7 (2)12 (5)
Biomarkers of phthalate exposure measured in urine†§, median [p10-p90]
 Mono-(4-methyl-7-carboxyheptyl) phthalate (cx-MiNP)§ (ng/mL)3.6 [1.0–12.6]3.7 [1.0–13.4]3.5 [1.0–10.5]
  Number of samples <LOD of 0.05 ng/mL, N (%)0 (0)0 (0)0 (0)
 Mono-(2-ethyl-5-oxohexyl) phthalate (5-oxo-MEHP)§ (ng/mL)2.6 [0.8–8.1]2.7 [0.8–8.2]2.4 [0.7–7.5]
  Number of samples <LOD of 0.2 ng/mL, N (%)≤5≤50 (0)
 Mono-(2-ethyl-5-hydroxyhexyl) phthalate (5-OH-MEHP)§ (ng/mL)4.5 [1.5–14.3]4.7 [1.6–15.2]4.3 [1.3–13.0]
  Number of samples <LOD of 0.1 ng/mL, N (%)0 (0)0 (0)0 (0)
 Mono-(2-ethyl-5-carboxypentyl) phthalate (5-cx-MEPP)§ (ng/mL)3.7 [1.1–11.9]3.9 [1.3–12.4]3.5 [1.0–10.1]
  Number of samples <LOD of 0.07 ng/mL, N (%)0 (0)0 (0)0 (0)
Biomarkers of phthalate exposure measured in blood†‡, median [p10-p90]
 Mono-(4-methyl-7-carboxyheptyl) phthalate (cx-MiNP)0.5 [0.2–1.5]0.5 [0.2–1.5]0.5 [0.2–1.5]
  Number of samples <LOD of 0.02 ng/mL, N (%)0 (0)0 (0)0 (0)
 Mono-(2-ethyl-5-oxohexyl) phthalate (5-oxo-MEHP)<LOD [<LOD-0.1]<LOD [<LOD-0.1]<LOD [<LOD-0.1]
  Number of samples <LOD of 0.1 ng/mL, N (%)532 (96)314 (95)218 (96)
 Mono-(2-ethyl-5-hydroxyhexyl) phthalate (5-OH-MEHP)<LOD [<LOD-0.1]<LOD [<LOD-0.1]0.1 [<LOD-0.1]
  Number of samples <LOD of 0.05 ng/mL, N (%)305 (55)193 (59)112 (50)
 Mono-(2-ethyl-5-carboxypentyl) phthalate (5-cx-MEPP)0.2 [0.1–0.4]0.2 [0.1–0.4]0.2 [0.1–0.3]
  Number of samples <LOD of 0.05 ng/mL, N (%)12 (2)7 (2)≤5
Triclosan†‡, median [p10-p90]<LOD [<LOD-0.2]<LOD [<LOD-0.2]<LOD [<LOD-0.2]
  Number of samples <LOD of 0.1 ng/mL, N (%)451 (81)262 (80)189 (84)

Notes: *One mother had twins. †Analysis is ongoing, so far 559 urine samples and 555 blood samples have been analysed. ‡Measured in blood. §Measured in urine. p10-p90: 10th-90th percentile.

Abbreviation: LOD, limit of detection.

Selected Maternal Characteristics of the 1057 Mothers to the 1058 Included Sons in the FEPOS Cohort* Notes: *One mother had twins. †Analysis is ongoing, so far 532 samples have been analysed. p10-p90: 10th-90th percentile. Abbreviation: LOD, Limit of detection. Selected Characteristics of 1058 Sons Included in the FEPOS Cohort* Notes: *One mother had twins. †Analysis is ongoing, so far 559 urine samples and 555 blood samples have been analysed. ‡Measured in blood. §Measured in urine. p10-p90: 10th-90th percentile. Abbreviation: LOD, limit of detection. Semen parameters are presented in Table 4. The median total sperm count was 104.9 million for sons from the Copenhagen clinic compared to 95.9 million among sons from the Aarhus clinic. The median time from ejaculation until motility analysis was longer in the Copenhagen clinic (45 versus 35 minutes). The median values across all other semen parameters were similar among sons from the Copenhagen and Aarhus clinics.
Table 4

Semen Characteristics of 1054 Sons Who Delivered a Semen Sample in the FEPOS Cohort

CharacteristicsAllCopenhagen ClinicAarhus Clinic
N=1054N=829N=225
Median (5–95 Percentile)Median (5–95 Percentile)Median (5–95 Percentile)
Abstinence time (days)2.0 (0.5–4.5)2.0 (0.5–4.5)2.5 (0.5–4.5)
Semen volume (mL)*2.7 (1.0–5.4)2.7 (1.0–5.4)2.6 (1.0–5.2)
Sperm concentration (million/mL)38.7 (2.7–138.0)38.7 (2.8–138.8)38.6 (2.4–134.8)
Total sperm count (million)*102.6 (8.1–409.2)104.9 (7.2–407.2)95.9 (8.4–417.1)
Motile sperm (%)63 (30–83)64 (31–84)63 (28–80)
Morphologically normal sperm (%)6 (0–15)6 (0–15)6 (1–15)
Testicular size (mL)15 (8–25)15 (8–25)15 (8–25)
Minutes until motility analysis45 (30–90)45 (35–90)35 (25–90)

Notes: *182 samples excluded due to spillage. †Motility and morphology not available for 17 sons with azoospermia.

Semen Characteristics of 1054 Sons Who Delivered a Semen Sample in the FEPOS Cohort Notes: *182 samples excluded due to spillage. †Motility and morphology not available for 17 sons with azoospermia. Compared to semen parameters of 365 male cohort members 20–22 years of age in the Testicular Function Study nested in the Western Australian Pregnancy Cohort (Raine)46 the median across all semen parameters were a little lower for FEPOS participants. A slightly lower median across all semen parameters was also found compared to those of young Danish men presenting for compulsory medical examination upon military conscription,47 although the variation in FEPOS was smaller. The most pronounced differences were for semen volume and total sperm count which might be due to a slightly longer ejaculatory abstinence among conscripts than FEPOS participant (median 2.5 days versus 2 days). The longer abstinence time in conscripts can largely be ascribed to stricter requirements regarding abstinence (participants not complying were rescheduled) whereas all FEPOS participants were included even though they did not comply with abstinence time instructions. Compared to WHO’s lower reference limits43,48 86% had a semen volume of ≥1.5 mL, 83% had a sperm concentration of ≥15 million/mL, 79% had a total sperm count of ≥39 million, 95% had ≥32% motile sperm, and 74% had ≥4% morphologically normal sperm. As the WHO reference limits were derived by studies of fertile men who recently became fathers it is to be expected that less than 95% of an unselected cohort like FEPOS have semen parameters above the reference limits.46,48–50

Discussion

To date, only few birth cohorts have detailed maternal information and biological specimens and a sufficient follow-up period and population size that enables assessment of prenatal determinants of reproductive parameters in the offspring.14,51–55 Of these, the Raine Testicular Function Study46,54 compares best to the FEPOS cohort. With 1058 participants the FEPOS cohort is the largest population-based male-offspring cohort worldwide with wide-ranging information on maternal health, lifestyle, socioeconomic status, occupation, and a maternal blood sample analyzed for exposure biomarkers of several xenobiotic chemicals combined with biological markers of fertility in their sons collected after puberty. The detailed and prospectively collected prenatal information allow for comprehensive confounder control and reduces the risk of information bias.56 Data collected from the mothers and children at different timepoints in the children’s lives by the DNBC and information on environmental exposures collected in the FEPOS cohort further enables studies on childhood and adolescence mediators. The possibility for linkage of the FEPOS cohort to the comprehensive Danish national health registers further increase the value of the FEPOS cohort. The response rate of 19% is in line with response rates from previous semen studies56–58 including the semen study among young Danish conscripts.59 It is lower compared to the Raine Testicular Function Study of 46% (40% delivered a semen sample)56 and the Danish study including sons of mothers from Healthy Habits for Two with a response rate of 49%.23 The lower participation in FEPOS may be explained by the contact via E-boks which can be challenging for this younger age group, but the alternatives were too costly and possibly not more effective. Another reason for the lower participation could be the demanding recruitment process. To be in accordance with Danish ethical regulations, the recruitment process involved four steps entirely depending on action from the young men. This included verbal confirmation of participation, online informed consent, self-administered questionnaire, and online booking of clinical visit, between the initial invitation and final participation at the clinics. Future research studies assessing reproductive health among young men should focus on how to get hold of participants in a less demanding way. Differential selection related to exposures, as well as semen quality has the potential to bias the risk estimates. In studies of fertility, selection bias is often caused by the higher propensity for participation by men concerned about their fertility, trying to father children or previously diagnosed with urogenital disorders or suspected infertility.60 Participants in the FEPOS cohort were 18–19 years of age and presumably not yet concerned or aware of their fertility status, which minimizes the risk of self-selection bias. Moreover, a Danish study found that biomarkers of spermatogenesis, such as inhibin B level, did not differ between men who chose to participate in a semen study and men who did not.59 The sons were intentionally not informed about the specific exposures of interest but only that the focus was fetal exposure. Therefore, the sons’ participation is unlikely to depend on exposure status. However, differential selection together with potential misclassification of exposure and outcomes should be considered in each specific hypothesis tested in this population. To minimize the risk of selection bias it is possible to use selection weights61 in the upcoming FEPOS studies.

Perspectives

The FEPOS cohort provides opportunity to study the “fetal origins of adult disease hypothesis” related to several suspected exposures.18 Analyses of biological samples for several xenobiotic chemicals and questionnaire information from both the mother and son combined with linkage to nationwide Danish health registers provide countless research opportunities. The first two publications using the FEPOS cohort have just been published.62,63 The first study investigated fetal exposure to paternal smoking and semen quality in the adult son and found a lower semen concentration and total sperm count among sons paternally, but not maternally, exposed to smoking. Indication of a higher risk of small testicular volume among sons of smoking fathers, compared to sons of non-smoking fathers were also observed.62 The second study investigated semen quality among young men taking protein supplements and found no association between use of protein supplements and semen parameters.63
  57 in total

1.  Quality assurance of semen analysis in multicenter studies. Asclepios.

Authors:  A Giwercman; M Spano; J Lähdetie; J P Bonde
Journal:  Scand J Work Environ Health       Date:  1999       Impact factor: 5.024

2.  Maternal alcohol consumption during pregnancy and semen quality in the male offspring: two decades of follow-up.

Authors:  C H Ramlau-Hansen; G Toft; M S Jensen; K Strandberg-Larsen; M L Hansen; J Olsen
Journal:  Hum Reprod       Date:  2010-06-29       Impact factor: 6.918

3.  Is maternal obesity related to semen quality in the male offspring? A pilot study.

Authors:  C H Ramlau-Hansen; E A Nohr; A M Thulstrup; J P Bonde; L Storgaard; J Olsen
Journal:  Hum Reprod       Date:  2007-08-17       Impact factor: 6.918

4.  Cohort Profile: The Western Australian Pregnancy Cohort (Raine) Study-Generation 2.

Authors:  Leon Straker; Jenny Mountain; Angela Jacques; Scott White; Anne Smith; Louis Landau; Fiona Stanley; John Newnham; Craig Pennell; Peter Eastwood
Journal:  Int J Epidemiol       Date:  2017-10-01       Impact factor: 7.196

5.  Is self-measuring of testicular volume by a Prader orchidometer a valid method?

Authors:  Cecilia Høst Ramlau-Hansen; Ane Marie Thulstrup; Jens Peter Bonde; Erik Ernst
Journal:  Fertil Steril       Date:  2007-02-12       Impact factor: 7.329

6.  Blood serum concentrations of perfluorinated compounds in men from Greenlandic Inuit and European populations.

Authors:  Christian H Lindh; Lars Rylander; Gunnar Toft; Anna Axmon; Anna Rignell-Hydbom; Aleksander Giwercman; Henning S Pedersen; Katarzyna Góalczyk; Jan K Ludwicki; Valentyna Zvyezday; Roel Vermeulen; Virissa Lenters; Dick Heederik; Jens Peter Bonde; Bo A G Jönsson
Journal:  Chemosphere       Date:  2012-04-10       Impact factor: 7.086

7.  Is prenatal exposure to tobacco smoking a cause of poor semen quality? A follow-up study.

Authors:  Cecilia Høst Ramlau-Hansen; Ane Marie Thulstrup; Lone Storgaard; Gunnar Toft; Jørn Olsen; Jens Peter Bonde
Journal:  Am J Epidemiol       Date:  2007-03-16       Impact factor: 4.897

8.  Infant mortality, childhood nutrition, and ischaemic heart disease in England and Wales.

Authors:  D J Barker; C Osmond
Journal:  Lancet       Date:  1986-05-10       Impact factor: 79.321

9.  Associations of in utero exposure to perfluorinated alkyl acids with human semen quality and reproductive hormones in adult men.

Authors:  Anne Vested; Cecilia Høst Ramlau-Hansen; Sjurdur Frodi Olsen; Jens Peter Bonde; Susanne Lund Kristensen; Thorhallur Ingi Halldorsson; Georg Becher; Line Småstuen Haug; Emil Hagen Ernst; Gunnar Toft
Journal:  Environ Health Perspect       Date:  2013-01-28       Impact factor: 9.031

Review 10.  The epidemiologic evidence linking prenatal and postnatal exposure to endocrine disrupting chemicals with male reproductive disorders: a systematic review and meta-analysis.

Authors:  Jens Peter Bonde; Esben Meulengracht Flachs; Susie Rimborg; Clara Helene Glazer; Aleksander Giwercman; Cecilia Høst Ramlau-Hansen; Karin Sørig Hougaard; Birgit Bjerre Høyer; Katia Keglberg Hærvig; Sesilje Bondo Petersen; Lars Rylander; Ina Olmer Specht; Gunnar Toft; Elvira Vaclavik Bräuner
Journal:  Hum Reprod Update       Date:  2016-09-21       Impact factor: 15.610

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  5 in total

1.  Gamete and embryo donation for research: what might shape the willingness to donate among gamete donors and recipients?

Authors:  Sandra Pinto da Silva; Cláudia de Freitas; Milton Severo; Susana Silva
Journal:  J Assist Reprod Genet       Date:  2022-08-20       Impact factor: 3.357

2.  Urinary Bisphenol A, F and S Levels and Semen Quality in Young Adult Danish Men.

Authors:  Thea Emily Benson; Anne Gaml-Sørensen; Andreas Ernst; Nis Brix; Karin Sørig Hougaard; Katia Keglberg Hærvig; Jens Peter Ellekilde Bonde; Sandra Søgaard Tøttenborg; Christian H Lindh; Cecilia Høst Ramlau-Hansen; Gunnar Toft
Journal:  Int J Environ Res Public Health       Date:  2021-02-11       Impact factor: 3.390

3.  Maternal Exposure to Per- and Polyfluoroalkyl Substances (PFAS) and Male Reproductive Function in Young Adulthood: Combined Exposure to Seven PFAS.

Authors:  Katia Keglberg Hærvig; Kajsa Ugelvig Petersen; Karin Sørig Hougaard; Christian Lindh; Cecilia Høst Ramlau-Hansen; Gunnar Toft; Aleksander Giwercman; Birgit Bjerre Høyer; Esben Meulengracht Flachs; Jens Peter Bonde; Sandra Søgaard Tøttenborg
Journal:  Environ Health Perspect       Date:  2022-10-05       Impact factor: 11.035

4.  Consumption of Sugar-Sweetened or Artificially Sweetened Beverages and Semen Quality in Young Men: A Cross-Sectional Study.

Authors:  Maiken Meldgaard; Nis Brix; Anne Gaml-Sørensen; Andreas Ernst; Cecilia Høst Ramlau-Hansen; Sandra Søgaard Tøttenborg; Karin Sørig Hougaard; Jens Peter Ellekilde Bonde; Gunnar Toft
Journal:  Int J Environ Res Public Health       Date:  2022-01-07       Impact factor: 3.390

5.  Parental Separation and Semen Quality in Young Men: A Population-Based Cohort Study.

Authors:  Anne Gaml-Sørensen; Nis Brix; Gunnar Toft; Tine Brink Henriksen; Andreas Ernst; Linn Håkonsen Arendt; Sandra Søgaard Tøttenborg; Katia Keglberg Hærvig; Karin Sørig Hougaard; Jens Peter Ellekilde Bonde; Cecilia Høst Ramlau-Hansen
Journal:  Clin Epidemiol       Date:  2022-01-26       Impact factor: 4.790

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