Introduction
Testis cancer rates have increased in western countries although with significant variations between countries (Chia et al., 2010; Engholm et al., 2010). Thus, for several decades, the incidence rates among Finnish men were lower than for men from most other countries, and at the same time, the Finnish men were found to have higher sperm counts than men from other Nordic countries (Vierula et al., 1996; Jørgensen et al., 2002). However, recent publications have indicated a change towards accelerated testis cancer rates among Finns (Richiardi et al., 2004).
Testis cancer and other male reproductive problems including impaired semen quality have been suggested to be linked through a testicular dysgenesis syndrome of foetal origin due to impact of environmental factors (Skakkebæk et al., 2001). Thus, such reproductive health problems may be related to year of birth, although not manifested until adulthood.
A question is whether the reported better reproductive health of Finnish men could be due to different environmental exposures or caused by genetic differences. We hypothesized that the better situation in Finland could be due to the fact that Finland ‘lagged behind’ in exposures to modern industrial pollution. Therefore, we carried out semen studies on cohorts of young Finnish men, and a registry study of testis cancer to explore recent temporal trends.
Discussion
The investigation of men from the general population of young Finns from the Turku area showed lower sperm counts in the most recent birth cohort compared with only few years older cohort. Additionally, the younger and more recently born men also had higher incidences of testis cancer than the older generations. This increase seemed more pronounced for men from the Turku area where the semen quality study was undertaken than for the entire Finnish population. Thus, the currently young Finnish men in general may suffer from more reproductive health problems than previous cohorts.
We described the detected adverse trends both as a birth cohort phenomenon and as an effect related to the study period. The birth cohort and investigation period are linked, and statistical evaluations cannot help distinguish which is most relevant. However, the risk of testis cancer is linked to birth cohorts (Bergström et al., 1996), and the incidence rate is 8–10 times higher for Finns born around 1980 compared with men born around 1950 (Bray et al., 2006). Furthermore, testicular germ-cell cancers in adults arise from carcinoma-in situ cells which are of foetal origin (Skakkebæk et al., 1987; Jørgensen et al., 1995a,b; Rajpert-De Meyts, 2006; Sonne et al., 2009). Thus, the increase in the testicular cancer incidences should be interpreted as a birth cohort effect.
The described increase for the testicular cancer incidence for the youngest men relies on only a rather small number of men and should therefore be interpreted cautiously. Nevertheless, we find it striking that there seems to be a tendency for an increased risk in all age groups above 15 years old and a higher increase in the Turku area than in the entire country. However, the results can only be regarded as preliminary, and a longer observation period is needed to corroborate or refute whether the indicated trends will last. Nevertheless, the findings can be used as an important indication of the validity of the study hypothesis (e.g. a falsification if trends showed opposite results). Most testicular cancers arise in men 10–60 years-old (Møller, 2001), which we also detected in the current study. A vast majority of tumours in this age-group are germ-cell tumours (>95%) arising from carcinoma-in situ cells, whereas those arising at earlier or later age have a different origin (Jørgensen et al. 1995a, Rajpert-De Meyts, 2006). We could not separate the registry information into germ-cell tumours or other testicular tumour types and therefore we chose to show the incidence only for men 10–59 years, which thus can be expected to represent mainly trends for germ-cell tumours.
The TDS concept proposes that an impaired development of foetal testes may lead to an increased risk of cryptorchidism, hypospadias, testicular cancer and decreased spermatogenesis (Skakkebæk et al., 2001), but does not imply that all affected men develop all the four symptoms (Jørgensen et al., 2010). Animal studies illustrate that in utero exposures to anti-androgenic agents may reduce Sertoli cell numbers that are the major factor determining sperm count in an individual (Scott et al., 2007; Sharpe, 2010). Interestingly, a continued post-natal exposure was needed to suppress a post-natal recovery of Sertoli cells after pre-natal exposure to an anti-androgen (Auharek et al., 2010). This indicates that both pre- and post-natal exposures are needed to affect Sertoli cell number permanently, at least if gross abnormalities are otherwise not present. Thus, the low sperm counts may be the result of both pre- and post-natal events.
An increasing number of the young Finns had a sperm concentration below the new WHO reference level of 15 million/mL (World Health Organization, 2010). From a biological point of view, this cut-off level may be too low to indicate normal fecundity (Skakkebæk, 2010) because the chances of achieving a pregnancy decrease with sperm concentrations below 40 million/mL (Bonde et al., 1998). A suggestion of a higher borderline value was also corroborated by a study of European fertile men showing a decrease in waiting time to pregnancy (TTP) with increasing sperm concentration up to 55 million/mL (Slama et al., 2002). An American study showed that only men with a sperm concentration of more than 48 million/mL could be classified as having a normal fertility chance (Guzick et al., 2001). Taken together, this may indicate that the 15% from the latest birth cohort having less than 15 million/mL may get difficulties in fathering children by natural means and that the remaining 28% (difference up to 43%) that have less than 40 million/mL may experience a longer waiting time to pregnancy than men having higher sperm concentrations. It can be argued that total sperm counts better reflect spermatogenesis than sperm concentrations. In the current study, we did not see any change in semen volume and therefore the same conclusions will be reached irrespective of whether sperm concentrations or total sperm counts were investigated.
The high number of morphologically abnormal spermatozoa of the young men also indicated that reduced fecundity may be a frequent problem. According to Guzick et al. (Guzick et al., 2001), who used sperm morphology – assessed according to the same criteria as here – a man should have at least 12% normal spermatozoa to be classified as fertile. This was the case only for 26% of the men. van Waart et al. detected a reduced pregnancy rate after intra-uterine insemination when the frequency of normal spermatozoa was below 5% (van Waart et al., 2001). Thus, the approximately 22% of the young Finns in our study who had less than 5% normal forms also showed an impaired quality for this important variable for fecundity.
Special caution is needed in the interpretation of the sperm motility data. Sperm motility assessment is highly subjective, and it was not possible for us to undertake a quality control study of the assessment of this variable. However, the distinction between motile and immotile spermatozoa may be more reliable than distinction between different subcategories of motilities (Jørgensen et al., 1997), which is the reason why we have only presented the frequencies of motile spermatozoa.
Only one technician was involved in the study reducing the potential impact by inter-observer variation. The quality control programme showed this technician to assess sperm concentration at a constant level during the years when compared with other participants in the programme. Thus, within-observer variation did not explain the detected trends in sperm count. However, to make the described results directly comparable to those published previously from similar studies from other countries and the initial Finnish study (Jørgensen et al., 2002; Punab et al., 2002; Paasch et al., 2008), a correction has to be applied. These previously published results used the Copenhagen laboratory as reference and adjusted the sperm concentration to the Copenhagen assessment level. Thus, the currently provided results for sperm concentration, total sperm count and total number of morphologically normal spermatozoa should be corrected for the assessment difference of 11% according to the quality control results given in the Materials and methods section (e.g. corrected sperm concentration = observed sperm concentration ×100/111). The effects of potential confounders were accounted for in the statistical analyses, when relevant. The influence of increasing duration of abstinence up to approximately 96 h for semen volume, sperm concentration and total sperm count, and no effect on motility or morphology is in agreement with our initial findings, and with the results of other semen quality studies of men from the Northern European area (Jørgensen et al., 2002; Punab et al., 2002; Paasch et al., 2008). Other studies have shown an adverse effect of maternal smoking during pregnancy on the son’s semen quality (Jensen et al., 2004, 2005; Paasch et al., 2008). In contrast, we did not find such an effect here, probably because the number of smoking mothers was very small.
Despite the participation being low, as it often is in studies requesting delivery of semen, we considered the examined men as representative of the normal population of young men from the Turku area. The men had essentially no prior knowledge of their own fertility potential and therefore attention to possible fertility problem is unlikely to have affected their motivation to participate. As shown in Table 3, the same trends in semen parameters was detected when the analysis was based only on men without any known ‘conditions’ as detailed in Table 1. This indicates that such ‘conditions’ were not the reason for the detected trends. The financial compensation received for participating in the study seems unlikely to have led to the selection of men with reduced semen quality. In fact, if compensation had not been given, it is most likely that men suffering from some kind of disease would be more interested in participating – in the hope of receiving advice – than men without diseases. Furthermore, a Danish study evaluating the reproductive hormones FSH, inhibin-B, LH and testosterone detected that the levels of these hormones did not differ between men who delivered semen samples and a larger group of men who only had a blood sample drawn (Andersen et al., 2000). This indicates that men who participate in a semen quality study using our approach do not differ from non-participants when their testicular functions are assessed according to hormonal levels, indicating that the participation rate does not hamper conclusions from the obtained results.
In addition to previously described differences in the testicular cancer rates and semen quality between Finnish men and Danish men (Jørgensen et al., 2002; Chia et al., 2010), we have shown a significant difference in the prevalence of cryptorchidism and hypospadias in boys born in 1997–2001 in Copenhagen and Turku (Virtanen et al., 2001; Boisen et al., 2004, 2005). Danish boys had a higher incidence of these disorders. Furthermore, Finnish boys with normal testicular descent had larger testes and higher inhibin-B values at 3 months of age than healthy Danish boys (Main et al., 2006). These findings suggested to us that we may see similar differences between the countries when the boys mature to adult age; i.e. better semen quality in Finns than in Danes. As the present data on semen quality show deterioration of semen quality in Finnish men born 10–20 years earlier than the 1997–2001 cohort, we might see deterioration also in the Danish group in the future.
The factors causing the adverse trends in male reproductive health remain elusive. However, only environmental factors can explain the rapidly increasing trends in testicular cancer. Factors related to modern way of living may be involved, including exposure to modern industrial chemicals and pesticides. Recent experimental research has revealed that the foetal gonads are particularly vulnerable to endocrine disruption (Auharek et al., 2010; Fisher et al., 2003; Mahood et al., 2005, 2006). Whatever the cause may be, most likely we should search for complex factors operating 20–30 years ago to explain the current reproductive problems of young men. Some Western European countries experienced more rapid post-war industrial development than Finland, which nevertheless more recently has enjoyed a very high economic growth. Today, Finland and other Western European countries are rather similar with regard to industrialization and economy (Statistical Yearbook of Finland, 2006). Our results seem to indicate that Finland will also adapt to these European countries with regard to male reproductive health.
In conclusion, our surveillance study revealed that the semen quality of recent birth cohorts of Finnish men seemed to deteriorate. In addition, an increase in the incidence of testis cancer was apparent and more pronounced for men from the Turku area of Finland where the semen studies were undertaken. We speculate that the simultaneous adverse trends in semen quality and testis cancer could be linked through an increasing frequency of men with testicular dysgenesis syndrome among Finnish men. The rapid rate of changes may suggest that the underlying causes are environmental and, as such, preventable. Our findings necessitate not only further surveillance of male reproductive health but also more research efforts to detect and remove the environmental factors which most likely are behind these findings.
Acknowledgements
The study was supported financially by several grants: European Union (contract numbers BMH4-CT96-0314, QLK4-CT-1999-01422, QLK4-CT- 2002-00603 and most recently, FP7/2008-2012, DEER grant agreement no. 212844), The Academy of Finland, Turku University Hospital Funds, Sigrid Juselius Foundation. N. Jørgensen received financial support from the Danish Agency for Science, Technology and Innovation (grant no. 271070678). Dr Jyrki Suominen (1939–2010) is thanked for careful and committed physical examination of the study subjects.