Kevin A. Wood, Kane Brides, Maurice E. Durham, Richard D. Hearn. 2021: Adults have more male-biased sex ratios than first-winter juveniles in wintering duck populations. Avian Research, 12(1): 51. DOI: 10.1186/s40657-021-00286-1
Citation:
Kevin A. Wood, Kane Brides, Maurice E. Durham, Richard D. Hearn. 2021: Adults have more male-biased sex ratios than first-winter juveniles in wintering duck populations. Avian Research, 12(1): 51. DOI: 10.1186/s40657-021-00286-1
Kevin A. Wood, Kane Brides, Maurice E. Durham, Richard D. Hearn. 2021: Adults have more male-biased sex ratios than first-winter juveniles in wintering duck populations. Avian Research, 12(1): 51. DOI: 10.1186/s40657-021-00286-1
Citation:
Kevin A. Wood, Kane Brides, Maurice E. Durham, Richard D. Hearn. 2021: Adults have more male-biased sex ratios than first-winter juveniles in wintering duck populations. Avian Research, 12(1): 51. DOI: 10.1186/s40657-021-00286-1
The long-term monitoring of demographic changes in waterbird populations remains limited, but such information can be valuable for conservationists and waterbird managers. Biased sex ratios can indicate differences in survival rates between sexes. In particular, differences in the sex ratios of fledged juveniles and adults can provide insight into the development of male bias among populations.
Methods
In this study, we used data from individual birds captured over a 57-year period to assess the extent, and temporal variability in male bias in nine populations of ducks wintering in the United Kingdom: Gadwall (Mareca strepera), Northern Mallard (Anas platyrhynchos), Northern Pintail (Anas acuta), Common Pochard (Aythya ferina), Common Shelduck (Tadorna tadorna), Northern Shoveler (Spatula clypeata), Eurasian Teal (Anas crecca), Tufted Duck (Aythya fuligula), and Eurasian Wigeon (Mareca penelope).
Results
Overall, eight of these populations were significantly male-biased and adults were more male-biased than first-winter juveniles for all nine populations. The increased male bias among adults is consistent with the hypothesis that factors such as higher mortality of reproductive-age females during the breeding season is a major cause of male bias in duck populations. However, such predation cannot explain the male bias detected in first-winter juveniles in four of the populations. The temporal trends in male bias differed between adults and first-winter juveniles in Northern Mallard, Northern Pintail, Common Pochard, Common Shelduck, Eurasian Teal, Tufted Duck, and Eurasian Wigeon. Over the study period we found increased male bias among adult Northern Mallard, Northern Pintail, Common Pochard, Common Shelduck, and Tufted Duck as well as both adult and first-winter juvenile Northern Shoveler.
Conclusions
We provide evidence that among wintering duck populations, sex ratios are typically male-biased, with adults exhibiting stronger male-biased sex ratios than first-winter juveniles. Improved monitoring of sex ratios of wintering waterbirds would help to increase our understanding of changes in waterbird demography, population structure, and observed population trends; our study shows that birds caught during ringing projects can be a valuable source of such data.
The main function of sperm is to ensure fertility and enhance paternity. Consequently strong selection acts on both sperm quantity and quality, which favors sperm traits that increase fertilization success (Birkhead and Møller 1998). Sperm motility parameters, the common indicators of sperm quality, are generally assessed to reflect the potential fertility of individuals (Froman et al. 1999; Gasparini et al. 2010).
A method allowing the capture of successive images of spermatozoa and the analysis of their individual movement was first reported by Dott and Foster (1979), and since then, the computer-assisted sperm analysis (CASA) has been presented and gradually developed as a method to objectively evaluate sperm motility parameters (Amann and Waberski 2014). The system has long been used to diagnose male reproductive system diseases and evaluate the quality of frozen semen used for artificial insemination in animal husbandry (Contri et al. 2010; Broekhuijse et al. 2011), which currently also plays an important role in pet breeding and animal experiments (Lüpold et al. 2009; Guo et al. 2018). However, various factors prevent sperm motility parameters obtained via a CASA system from being compared across studies. Firstly, CASA systems are based on similar principles (Dott and Foster 1979), but their instrument components (e.g. optics and hardware characteristics, as well as algorithms for sperm identification and trajectory reconstruction) and settings (e.g. frame rate and frames per field) highly influence sperm motility parameters (Boryshpolets et al. 2013; Amann and Waberski 2014). In sperm sample preparation, the media used for dilution, sperm sample concentration, temperature and pH should be considered, which can also impact sperm motion characteristics evaluated by a CASA system (Contri et al. 2010; Kathiravan et al. 2011; Humann-Guilleminot et al. 2018). In addition, some factors during analysis procedure such as the number of sperm captured per slide and the technical competence of user are vital for reflecting sperm kinetic characteristics (Broekhuijse et al. 2011; Mortimer and Mortimer 2013). Therefore, although a CASA system can provide an objective assessment of sperm motility parameters, a standardized protocol has now become necessary. With such a standardized protocol, sperm motion characteristics would be accurately reflected and would then permit comparison across systems and groups.
Passerine birds account for over half of avian species, whose sperm generally have a helical shape and a spiraling forward movement (Humphreys 1972) and remain within the sperm storage tubules for a period of days to weeks after copulation (Birkhead and Møller 1998). Postcopulatory sexual selection, including sperm competition and cryptic female choice, is considered to be an important driver of evolutionary change in sperm traits (Birkhead and Møller 1998; Birkhead and Pizzari 2002), however, the sperm characteristics that are closely related to fertilization success have been unclear in passerine birds. Yet there has been a long-term interest in sperm motion characteristics of passerine birds, because faster sperm are presumed to outcompete rival sperms in the "race" to the ovum and more ejaculated motile sperm are likely to increase the odds of sperm from a certain male fertilizing the ovum. In addition, some passerine sperm motility parameters can also be used as indicators of the impact of pollutants in a wide range of species (Møller et al. 2008, 2014; Leidens et al. 2018).
CASA systems have been repeatedly used to assess sperm swimming ability in passerine birds (Lüpold et al. 2009; Bennison et al. 2016), but the procedure conditions have not been standardized thus far. Concerning the temperature at which the sperm movements should be analyzed, some studies assessed sperm motility parameters of passerine birds around body temperature, i.e. 40 ℃, such as in House Sparrows (Passer domesticus, Mora et al. 2017), Azores Bullfinches (Pyrrhula murina, Lifjeld et al. 2013) and Great Tits (Parus major, Losdat and Helfenstein 2018), while others analyzed sperm movement below the bird's body temperature, such as in Eurasian Bullfinches (Pyrrhula pyrrhula) (35 ℃; Birkhead et al. 2006) and Zebra Finches (Taeniopygia guttata) (38 ℃; Bennison et al. 2016). Unfortunately, non-standardized procedure conditions likely affect the reliability of motility parameters detected by a CASA system, which makes it difficult for researchers to compare sperm motion characteristics estimates across time, studies and species.
The aim of this study was to determine the optimal CASA conditions for assessment of sperm kinetic characteristics in Tree Sparrows (Passer montanus) by comparing sperm motility, sperm velocity and sperm movement trajectory at different analysis time, temperatures and pH values. We wish to make recommendations for the standardized estimation of passerine sperm motility parameters using a CASA system that would allow evaluating sperm motion characteristics more accurately and repeatedly.
Methods
Model species
A total of 63 adult Tree Sparrows (11 females and 12 males in 2017, 40 males in 2018) captured with mist nets in May of 2017 and 2018 were used for this study. The sample area, Liujiaxia (35°56′N, 103°15′E) in a northwestern part of China, is a relatively unpolluted village and provides a suitable habitat for Tree Sparrows. Each bird captured was weighed and measured for their wing length and tarsus length, and also sexed based on the presence of a brood patch (Selander and Yang 1966). The body temperature of the adult captured in 2017 was also estimated. On completion, the females were ringed with a uniquely numbered metal band and then released. And males were protected from light and brought back alive to the laboratory, 48 (8 in 2017 and 40 in 2018) of them were used for evaluating sperm motility parameters under different conditions.
The male Tree Sparrows captured in this study were also used for the analysis of several physiological and biochemical indexes and for histology observations. Therefore, these birds were euthanized according to the "Animal Experimental Ethical Inspection Form" (see Additional file 1: Fig. S1), and their seminal glomera were collected conveniently. However, it is to be noted that a non-invasive method to obtain sperm by gently massaging the bird's cloaca works well in passerine birds (Wolfson 1952), and it should be advocated whenever euthanasia is not absolutely necessary.
CASA system
Sperm motility parameters were assessed using the WLJY-9000 (WEI-LI New Century Technical Development, China) device with the standardized 10 μm-depth slide chambers. This system, based on the WHO laboratory manual for the examination and processing of human semen, has a thermostat that can maintain the temperature from room temperature up to 70 ℃. In addition, the maximum velocity of sperm movement detected by WLJY-9000 is 180 μm/s, up to 20 fields can be captured in each analysis. In each field, 4‒20 frames (20 frames in the present study) were tracked for sperm motility parameters assessment, and no more than 1000 spermatozoa can be identified.
Estimating body temperature
The body temperature of the captured 12 males and 11 females was immediately detected with a UT325 thermometer (Uni-Trend, China). A clean probe was slightly inserted into the cloaca approximately 1 cm deep and removed when the reading was stable.
The test results showed the body temperatures of adult Tree Sparrows were 40.13 ± 1.56 ℃ for male, and 40.38 ± 1.36 ℃ for female. We used these values as bases for exploring the optimal conditions of sperm motility parameters evaluation using the CASA system.
Sperm motility parameters detected by the CASA system
Male Tree Sparrows were acclimatized to the laboratory for 3 h before they were euthanized. Then, they were immediately dissected for a series of experiments, and their right seminal glomus was extracted for obtaining sperm suspension in preheated Hank's Balanced Salt Solution (HBSS, an isotonic solution that can buffer pH and preserve the sample's osmotic pressure). Sperm swam out from the seminal glomus into the surrounding media and diffused, forming a "cloud", and in about 10 s the "cloud" diffused completely in the medium. The sperm suspension was then kept warm (at the corresponding analysis temperature) in a water bath until analysis. Next, 10 μL of diluted semen were dropped on the center of the pre-warmed slide chamber and a coverslip was placed over the sample. And the slide was put in the thermostat and sperm motility parameters were assessed by the WLJY-9000 CASA system at 100× magnification. For each analysis, sperm motility parameters were collected and recorded by the capture of at least 5 nonconsecutive fields (a total of at least 500 spermatozoa) within 30 s. The sperm in each field were selected by adjusting the grayscale threshold, and the selected debris and round cells were manually deleted prior to analysis. The following sperm motility parameters were determined: (1) Sperm motility: rapid progressive motility (the percentage of rapid progressive sperm with a linear velocity ≥ 25 μm/s), slow progressive motility (the percentage of slow progressive sperm with a linear velocity < 25 μm/s), non-progressive motility (all other patterns of motility with an absence of progression), immotility (the percentage of immotile sperm). In addition, progressive motility (the sum of rapid and slow progressive motility) is a vital indicator of ejaculated sperm to evaluate their swimming ability (Kathiravan et al. 2011), which was assessed in this study; (2) Sperm velocity: the curvilinear velocity (VCL), straight-line velocity (VSL) and average path velocity (VAP) can be evaluated by the CASA system, and these three sperm velocity parameters were strongly associated with each other (Pearson's r > 0.96, p < 0.001), thus the present study chose VCL, the velocity over the actual sperm trajectory, as a measure of sperm swimming speed (hereafter referred to as sperm velocity); (3) Sperm movement trajectory: path linearity (the linearity of actual sperm track, LIN = VSL/VCL), path wobble (departure of actual sperm track from average path, WOB = VAP/VCL), and path straightness (linearity of the average path, STR = VSL/VAP).
Effect of time since dilution and until analysis on sperm motility parameters
The right seminal glomus of 8 males brought back to the laboratory and euthanized in 2017 was removed and cut in half in 0.5 mL of HBSS, which could keep the sperm concentration between 2 and 50 × 106 sperm/mL (the recommended concentration for sperm motility parameters assessment in WHO laboratory manual for the examination and processing of human semen). The preheated temperature of HBSS was set to 40 ℃ (the body temperature of Tree Sparrows), and the pH was set to 7.5 (according to the semen pH of poultry) (Orunmuyi et al. 2013) and because weak alkaline pH has shown increased sperm movement (Holm and Wishart 1998). Next, a 10-μL sperm suspension was used for the assessment of the sperm motility parameters by the WLJY-9000 CASA system at 3, 5, 15, 20, and 30 min after dilution.
The initial experiment results showed that the percentage of progressive sperm decreased with time, which largely dropped after 15 min. Based on the results of this first experiment, in 2018, sperm samples of 8 other males were used to assess sperm motility parameters at 1 (the time sperm were suspended fully in medium and load the sperm suspension onto the microscope slides), 3, 5, 7, 9, 11, 13, and 15 min after dilution in HBSS with pH 7.5 at 40 ℃.
Effect of temperature on sperm motility parameters
We evaluated the effect of the temperature on sperm motion characteristics using sperm samples from 8 males, whose right seminal glomus was divided into 3 equal portions with ophthalmic scissors in 2018. Then, the three pieces were put immediately into different Eppendorf tubes containing 0.2 mL of HBSS with pH 7.5 and placed in a water bath at either 38, 40 or 42 ℃. Approximately 4 min after dilution, motility parameters of sperm from different Eppendorf tubes were analyzed by the WLJY-9000 CASA system at 38, 40 and 42 ℃.
Effect of pH on sperm motility parameters
Based on the semen pH of poultry (Orunmuyi et al. 2013) and previous results in other species (Holm and Wishart 1998), the pH values of HBSS in this experiment were set to three groups (7.0, 7.5 and 8.0 in group 1, 6.0, 7.0 and 7.5 in group 2, and 7.5, 8.0 and 9.0 in group 3) to control the impact of individual variation on the comparison of sperm motility parameters between different pH levels. A total of 24 birds (7 in group 1, 8 in group 2 and 9 in group 3) were used in this experiment, the right seminal glomus of which was divided into 3 equal portions with ophthalmic scissors. Then, the 3 sections were immediately put into Eppendorf tubes containing 0.2 mL of 40 ℃ pre-warmed HBSS with different pH values. Approximately 4 min after dilution, sperm motility parameters were assessed by the WLJY-9000 CASA system at 40 ℃.
Statistical analysis
Experimental data are expressed as mean values ± standard deviation (SD) or ratio. Statistical analyses were performed using SPSS 20.0 statistical software (IBM SPSS Inc., USA). Two-tailed Pearson correlation analysis was used to check for relationships between sperm velocity parameters. All proportion data including sperm motility and sperm movement trajectory were logit transformed prior to analysis.
The change of sperm motility parameters at different analysis time was investigated using the repeated measures analysis of general linear model (GLM). In order to validate the univariate F-test, the "Epsilon" values (when the Greenhouse-Geisser was > 0.7, the Huynh-Feldt correction should be used, and if not, the Greenhouse-Geisser correction should be used) would be used to calculate an appropriate adjustment to the degrees of freedom when the assumption of sphericity was not met (p < 0.05). Besides, curve fittings were performed using SigmaPlot 14.0 software (Systat Software Inc., USA) to simulate the association between analysis time (independent variable) and sperm motility parameters (dependent variables), and the equations that most closely fit the actual data were found (large coefficient of determination, and p < 0.05).
To investigate the effect of temperature and pH on sperm motility parameters, the univariate analysis of GLM was conducted. The sperm motility parameters entered as dependent variable, while temperature or pH entered as a fixed factor. Besides, male identity was entered as a random factor to control for individual variation, and the time since dilution and until analysis was a covariate.
The model assumptions were validated by testing the residuals' normality, and pairwise comparisons were corrected by the Bonferroni method. Besides, SigmaPlot 14.0 software was also used for bar graphs, line charts and scatter plot.
Results
Effect of time since dilution and until analysis on sperm motility parameters
We found that the amount of time elapsed since dilution until analysis affected the rapid progressive motility, immotility and progressive motility (Table 1), and high correlation coefficients (R2 > 0.93) were observed when sigmoid model and polynomial model were used to calculate the change of these three parameters with time (Fig. 1a, d, e). The lower rapid progressive motility and progressive motility at 13 min (rapid progressive motility: p = 0.02, progressive motility: p = 0.02) and 15 min (rapid progressive motility: p = 0.009, progressive motility: p = 0.009), as well as higher immotility at 15 min (p = 0.02) were detected compared to 1 min (Fig. 1a, d, e). However, the percentages of slow progressive sperm and non-progressive sperm remained statistically unchanged within 15 min after dilution (Fig. 1b, c).
Table
1.
Degrees of freedom, F-values and significance levels denoting the effect of time since dilution and until analysis, temperature and pH on the sperm motility parameters
Dependent variables
Independent variables
Time since dilution and until analysis
Temperature
pH levels
Fdf
p value
Fdf
p value
Fdf
p value
Rapid progressive motility
23.902.16, 15.10
< 0.001
2.242, 13
0.15
12.384, 39
< 0.001
Slow progressive motility
2.061.85, 12.95
0.17
4.562, 13
0.03
0.584, 39
0.68
Non-progressive motility
1.017, 49
0.44
1.462, 13
0.27
0.464, 39
0.76
Immotility
10.857, 49
< 0.001
6.842, 13
0.01
6.274, 39
0.001
Progressive motility
20.192.05, 14.32
< 0.001
4.282, 13
0.04
15.264, 39
< 0.001
Sperm velocity
11.657, 49
< 0.001
0.972, 13
0.41
11.224, 39
< 0.001
LIN
2.392.19, 15.35
0.12
0.232, 13
0.80
10.354, 39
< 0.001
WOB
3.082.34, 16.40
0.07
0.212, 13
0.81
10.494, 39
< 0.001
STR
0.392.82, 19.75
0.75
0.472, 13
0.64
7.294, 39
< 0.001
The details of the building of general linear models are shown in Additional file : Tables S1‒S3 LIN linearity, WOB wobble, STR straightness Italic values are significant in the analysis
Figure
1.
The change of a rapid progressive motility, b slow progressive motility, c non-progressive motility, d immotility and e progressive motility with the time since dilution and until analysis. The blue curves are the regression lines (R2 > 0.93). #p < 0.05 compared to 1 min
The sperm velocity was also influenced by the analysis time (Table 1), which changing pattern followed a sigmoid model (R2 = 0.96). Until 9 min after dilution, the sperm velocity remained significantly unchanged (p > 0.05), which was significantly decreased at 11 min (p = 0.04), 13 min (p = 0.04) and 15 min (p = 0.004) compared to 1 min (Fig. 2a). The study also indicated no significant difference in sperm LIN, WOB and STR across time (Fig. 2b).
Figure
2.
The change of a sperm velocity (blue curve is the regression line, R2 = 0.96) and b sperm movement trajectory with the time since dilution and until analysis. LIN, WOB and STR are the abbreviations of linearity, wobble and straightness, respectively. #p < 0.05 compared to 1 min
Effect of temperature on sperm motility parameters
The rapid progressive motility and non-progressive motility remained statistically unaffected by different temperatures (Table 1). However, temperature affected the percentages of slow progressive sperm, immotile sperm and progressive sperm (Table 1). More slow progressive sperm was found at 38 ℃ compared to 40 ℃ (p = 0.04) and 42 ℃ (p = 0.01) (Fig. 3b). And at 42 ℃, immotility was higher than 40 ℃ (p = 0.003) and progressive motility was lower than 40 ℃ (p = 0.02) and 38 ℃ (p = 0.03) (Fig. 3d, e).
Figure
3.
Effect of temperature on a rapid progressive motility, b slow progressive motility, c non-progressive motility, d immotility and e progressive motility. Different symbols in each column graph denote significant differences between temperature groups (p < 0.05)
In contrast, no significant differences in sperm velocity and sperm movement trajectory were detected across temperatures groups (Fig. 4).
Figure
4.
Effect of temperature on a sperm velocity and b sperm movement trajectory. The gray dots represent samples, and the hollow diamonds represent average values. Abbreviations are the same as those in Fig. 2
The pH significantly affected sperm motility recorded by the WLJY-9000 CASA system, including rapid progressive motility, immotility and progressive motility (Table 1). And these parameters were statistically similar at pH 7.0, 7.5 and 8.0 (p > 0.05) with the exception of lower percentage of progressive sperm at pH 7.0 compared to pH 7.5 (p = 0.04) (Fig. 5a, d, e). In addition, a significant increase in immotility and a significant decrease in rapid progressive motility and progressive motility were observed at pH 6.0 (all p < 0.001 compared to pH 7.5 and pH 8.0) and 9.0 (rapid progressive motility: p = 0.04 compared to pH 7.5 and pH 8.0; progressive motility: p = 0.002 compared to pH 7.5 and p = 0.001 compared to pH 8.0) (Fig. 5a, d, e).
Figure
5.
Effect of pH on a rapid progressive motility, b slow progressive motility, c non-progressive motility, d immotility and e progressive motility. Different symbols in each column graph denote significant differences between pH values (p < 0.05)
Besides, pH also impacted sperm velocity and sperm movement trajectory (Table 1). Sperm velocity in media with pH 7.0, 7.5, 8.0 and 9.0 was statistically similar (p > 0.05), which was statistically higher compared to pH 6.0 (all p < 0.001) (Fig. 6a). Moreover, lower sperm LIN, WOB and STR were observed at pH 6.0 compared to pH 7.0, 7.5, 8.0 and 9.0 (p < 0.047) (Fig. 6b).
Figure
6.
Effect of pH on a sperm velocity and b sperm movement trajectory. Different symbols in each parameter indicate significant differences between pH values (p < 0.05). The gray dots represent samples, and the hollow diamonds represent average values. Abbreviations are the same as those in Fig. 2
CASA systems have been repeatedly used to assess sperm motility parameters of passerine birds in order to explore the evolution of sperm structure and energetics (Rowe et al. 2013; Bennison et al. 2016) or sperm morphology and velocity (Bennison et al. 2014; Rowe et al. 2015; Mora et al. 2017) in relation to sperm competition, or to assess the toxicity of environmental pollutants on sperm quality (Møller et al. 2014). However, inconsistent CASA operations are performed across these studies, which precludes any accurate and repeatable assessment of sperm swimming ability and prevents any comparison within and across species. In this study, three separate experiments were carried out to compare the sperm motility parameters of Tree Sparrow in different conditions, which allowed us to identify optimal analysis time, temperatures and pH for CASA.
Reliable assessments of sperm motility parameters can be performed provided that the extender does not significantly alter the sperm kinetic characteristics over the time period of the analysis (Davis and Katz 1993). In our study, the progressive motility and sperm velocity decreased with time followed a sigmoid model, but all sperm motility parameters remained statistically unchanged within 9 min after dilution in a balanced salt solution, and this period (from 1 min to 9 min after dilution) provides a possibility for obtaining stable assessment of sperm kinetic characteristics in Tree Sparrow. However, other studies on Great Tits, Blue Tits (Cyanistes caeruleus) and Pied Flycatchers (Ficedula hypoleuca) also show the sperm motile performance declines over time in vitro within about 5 min when sperm stock solution was prepared by a neutral medium, phosphate-buffered saline (PBS) (Cramer et al. 2016a, b), which differs from the findings in our study. Decreased sperm motile performance in birds has been found under the neutral pH conditions (Fig. 5e) or in PBS (Humann-Guilleminot et al. 2018); therefore, the neutral PBS is likely to lead to the short survival of sperm in these studies. Besides, different selection mechanisms of sperm competiton are shown across animal taxa (Birkhead and Møller 1998), and the sperm longevity may be more important for increasing the fertilizing ability of Tree Sparrow compared to the Great Tits, Blue Tits or Pied Flycatchers, so their sperm motility parameters remained longer.
The body temperature of Tree Sparrows that we measured is somewhat on the lower side of the expected mean body temperature of passerine birds (Riley 1937; Binkley et al. 1971; Møller 2010; Skold-Chiriac et al. 2015). It has been reported that the stress caused by capture and detection declined the body temperature of Barn Swallow (Hirundo rustica) and Great Tit (Møller 2010; Andreasson et al. 2019), which may lead to the slightly lower body temperature in Tree Sparrow. After insemination, avian sperm are held in the sperm storage tubules for a period of days to weeks before fertilizing the ova competitively (Birkhead and Møller 1998). Thus, the female reproductive tract provides an optimal environment for sperm motion, and our study likewise showed high sperm kinetic values of Tree Sparrows at their body temperature (40 ℃). Similar to the study about sperm movement of ostriches (Bonato et al. 2012), more slow progressive sperm were observed at low temperatures in the present study. However, the sperm viability of ostriches is unaffected at 20 ℃, and the poor sperm movement at low temperatures is reversible (Bonato et al. 2012). In contrast, we found more immotile sperm at high temperature, which may be related to the damaging effects of high temperature on sperm membrane (Wechalekar et al. 2010) or Na+/K+-ATPase activity (Thundathil et al. 2012). It is also worth noting that sperm motility parameters are sensitive to temperature changes. Low magnitude temperature variations (± 2 ℃) significantly influenced the kinetic parameters in our study, and, as a consequence, strict temperature control during the assessment of sperm motility parameters of passerine birds is key to accurately estimate sperm quality.
Semen of broilers has been shown to be alkaline (Orunmuyi et al. 2013), and in this study, the best sperm movement status was observed at pH 7.5 and 8.0 by comprehensive consideration of sperm motility, sperm velocity and sperm movement trajectory. So, the weakly alkaline environment with a pH close to semen pH is suitable to assess the sperm motility parameters of Tree Sparrow. Similarly, existing research has also shown that sperm movement is stimulated at a certain alkali pH range; for instance, the velocity and total motility of sperm from chickens, turkeys and quails are significantly greater at pH 8.0 compared to pH 7.0, and the sperm velocity is further increased at pH 9.0 for quail and chicken sperm (Holm and Wishart 1998). Ashizawa et al. (1994) found that the increased pH may act directly on axonemal phosphoprotein, mediated by a Ca2+-related substance, which is likely to be a reason why sperm swimming better in the weakly alkaline environment. By contrast, as our study confirms a range of acidic to neutral pH that lead to poor sperm motion (Holm and Wishart 1998; Bonato et al. 2012), which may be related to a reduction in sperm metabolism to conserve energetic resources and promote sperm lifespan (Pinto et al. 1984). In some studies, sperm of passerine birds are suspended by a commercial extender (e.g. Dulbecco's modified Eagle medium) (Lifjeld et al. 2013; Rowe et al. 2013; Mora et al. 2017; Losdat and Helfenstein 2018); however, these neutral media may lead to an underestimate of the sperm kinetic characteristics in passerine birds according to our study.
Conclusions
Our results indicate that the time elapsed since dilution and until analysis, the temperature and the sperm-extender pH all affect sperm motility parameters as computed by the WLJY-9000 CASA system, especially, low magnitude temperature variations (± 2 ℃) can significantly influence the kinetic parameters of Tree Sparrow. We recommend that sperm motility parameters analyses of passerine sperm using a CASA system be performed at 40 ℃ with a pH comprised around 7.5‒8.0 and at 1‒9 min after sperm were suspended in the extender. Under these conditions, the valid motility results will be obtained to reflect sperm swimming ability accurately.
Additional file 2: Table S1. Summary of general linear models examining the effect of time since dilution and until analysis on sperm motility parameters. Table S2. Summary of general linear models examining the effect of temperature on sperm motility parameters. Table S3. Summary of general linear models examining the effect of pH on sperm motility parameters.
Acknowledgements
We are grateful to Huijie Zhang, Shengnan Wang and Hao Sun for their assistance with fieldwork, and three anonymous reviewers for their valuable comments.
Authors' contributions
YZ and YY conceived and designed the study. YY, JD, SA, RG, XB and WY conducted the field work. YY and RG carried out the analyses. YY analyzed the data and wrote the manuscript, and YZ revised it. All authors read and approved the final manuscript.
Tree sparrows were sampled and processed with the permission of Committee on the Ethics of Animal Experiments of School of Life Sciences, Lanzhou University, China.
Consent for publication
Not applicable.
Competing interests
The authors declare that they have no competing interests.
Aebischer NJ. Fifty-year trends in UK hunting bags of birds and mammals, and calibrated estimation of national bag size, using GWCT's National Gamebag Census. Eur J Wildl Res. 2019;65: 64.
Albrecht T, Hořák D, Kreisinger J, Weidinger K, Klvaňa P, Michot TC. Factors determining pochard nest predation along a wetland gradient. J Wildlife Manag. 2006;70: 784–91.
Alexander WC. Differential sex distributions of wintering diving ducks (Aythyini) in North America. Am Birds. 1983;37: 26–9.
Arnold TW. Uninformative parameters and model selection using Akaike's Information Criterion. J Wildlife Manag. 2010;74: 1175–8.
Bartoń K. MuMIn: Model selection and model averaging based on information criteria. R package version 1.13.4. 2012. .
Bates D, Mächler M, Bolker BM, Walker SC. Fitting linear mixed-effects models using lme4. J Stat Software. 2015;67: 1–48.
Bellebaum J, Mädlow W. Survival explains sex ratio in an introduced Mandarin Duck Aix galericulata population. Ardea. 2015;103: 183–7.
Bellrose FC, Scott TG, Hawkins AS, Low JB. Sex ratios and age ratios in North American ducks. Ill Nat Hist Surv Bull. 1961;27: 391–486.
Blums P, Mednis A. Secondary sex ratio in Anatinae. Auk. 1996;113: 505–11.
Bolen EG. Sex ratios in the Black-bellied Tree Duck. J Wildlife Manag. 1970;34: 68–73.
Brides K, Wood KA, Hearn RD, Fijen TPM. Changes in the sex ratio of the Common Pochard Aythya ferina in Europe and North Africa. Wildfowl. 2017;67: 100–12.
Burnham KP, Anderson DR, Huyvaert KP. AIC model selection and multimodel inference in behavioral ecology: some background, observations, and comparisons. Behav Ecol Sociobiol. 2011;65: 23–35.
Carbone C, Owen M. Differential migration of the sexes of Pochard Aythya ferina: results from a European survey. Wildfowl. 1995;46: 99–108.
Carney SM. Species, age and sex identification of ducks using wing plumage. Washington: US Department of the Interior, US Fish and Wildlife Service; 1992.
Choudhury S, Black JM. Testing the behavioural dominance and dispersal hypothesis in Pochard. Ornis Scand. 1991;22: 155–9.
Christensen TK, Fox AD. Changes in age and sex ratios amongst samples of hunter-shot wings from common duck species in Denmark 1982–2010. Eur J Wildl Res. 2014;60: 303–12.
Clutton-Brock TH. Sex-ratio variation in birds. Ibis. 1986;128: 317–29.
Cooper N, Bond AL, Davis JL, Portela Miguez R, Tomsett L, Helgen KM. Sex biases in bird and mammal natural history collections. Proc R Soc B. 2019;286: 20192025.
Cox DR, Snell EJ. Analysis of binary data. 2nd ed. Boca Raton: Chapman and Hall; 1989.
Crawley MJ. Statistics: an introduction using R. Chichester: Wiley; 2005.
Dean WRJ, Skead DM. The sex ratio in Yellowbilled Duck, Redbilled Teal and Southern Pochard. Ostrich. 1977;48: 82–5.
Donald PF. Adult sex ratios in wild bird populations. Ibis. 2007;149: 671–92.
Dormann CF, Elith J, Bacher S, Buchmann C, Carl G, Carré G, et al. Collinearity: a review of methods to deal with it and a simulation study evaluating their performance. Ecography. 2013;36: 27–46.
Eberhart-Phillips LJ, Küpper C, Carmona-Isunza MC, Vincze O, Zefania S, Cruz-López M, et al. Demographic causes of adult sex ratio variation and their consequences for parental cooperation. Nat Commun. 2018;9: 1651.
Evans DM, Day KR. Migration patterns and sex ratios of diving ducks wintering in Northern Ireland with specific reference to Lough Neagh. Ringing Migr. 2001;20: 358–63.
Fox AD, Cristensen TK. Could falling female sex ratios among first-winter northwest European duck populations contribute to skewed adult sex ratios and overall population declines? Ibis. 2018;160: 929–35.
Fox AD, King R, Watkin J. Seasonal variation in weight, body measurements and condition of free-living Teal. Bird Study. 1992;39: 53–62.
Frew RT, Brides K, Clare T, Maclean L, Rigby D, Tomlinson CT, et al. Temporal changes in the sex ratio of the Common Pochard Aythya ferina compared to four other duck species at Martin Mere, Lancashire, UK. Wildfowl. 2018;68: 140–54.
Guillemain M, Fox AD, Pöysä H, Väänänen V-M, Christensen TK, Triplet P, et al. Autumn survival inferred from wing age ratios: Wigeon juvenile survival half that of adults at best? J Ornithol. 2013;154: 351–8.
Hommel G. A stagewise rejective multiple test procedure based on a modified Bonferroni test. Biometrika. 1988;75: 383–6.
Johnson DH, Sargeant AB. Impact of red fox predation on the sex ratio of prairie mallards. Washington: Department of the Interior, Fish and Wildlife Service; 1977.
Kear J, Hulme M. Ducks, geese and swans. Oxford: Oxford University Press; 2005.
Ketterson ED, Nolan V Jr. Geographic variation and its climatic correlates in the sex ratio of eastern-wintering Dark-eyed Juncos (Junco hyemalis hyemalis). Ecology. 1976;57: 679–93.
Korschgen CE. Breeding stress of female eiders in Maine. J Wildl Manag. 1977;41: 360–73.
Lehikoinen A, Christensen TK, Öst M, Kilpi M, Saurola P, Vattulainen A. Large-scale change in the sex ratio of a declining eider Somateria mollissima population. Wildlife Biol. 2008a;14: 288–301.
Lehikoinen A, Öst M, Hollmén T, Kilpi M. Does sex-specific duckling mortality contribute to male bias in adult common eiders. Condor. 2008b;110: 574–8.
Leopold A. Game management. Madison: The University of Wisconsin Press; 1933.
Madge S, Burn H. Wildfowl: an identification guide to the ducks, geese and swans of the world. London: Christopher Helm; 1988.
Mayr E. The sex ratio in wild birds. Am Nat. 1939;73: 156–79.
Metz KJ, Ankney CD. Are brightly coloured male ducks selectively shot by duck hunters? Can J Zool. 1991;69: 279–82.
Mitchell C, Ogilvie M. Fifty years of wildfowl ringing by The Wildfowl & Wetlands Trust. Wildfowl. 1996;47: 240–7.
Mitchell C, Fox AD, Harradine J, Clausager I. Measures of annual breeding success amongst Eurasian Wigeon Anas penelope. Bird Study. 2008;55: 43–51.
Nagelkerke NJD. A note on a general definition of the coefficient of determination. Biometrika. 1991;78: 691–2.
Opermanis O, Mednis A, Bauga I. Duck nests and predators: interaction, specialisation and possible management. Wildlife Biol. 2001;7: 87–96.
Owen M, Cook WA. Variations in body weight, wing length and condition of Mallard Anas platvrhvnchos platyrhynchos and their relationship to environmental changes. J Zool. 1977;183: 377–95.
Owen M, Dix M. Sex ratios in some common British wintering ducks. Wildfowl. 1986;37: 104–12.
Owen M, Mitchell C. Movements and migrations of Wigeon Anas penelope wintering in Britain and Ireland. Bird Study. 1988;35: 47–59.
Owen M, Montgomery S. Body measurements of Mallard caught in Britain. Wildfowl. 1978;29: 123–34.
Perdeck AC, Cavé AJ. Sexual differences in migration and winter quarters of ducks ringed in the Netherlands. Wildfowl. 1983;34: 137–43.
Pöysä H, Linkola P, Paasivaara A. Breeding sex ratios in two declining diving duck species: between-year variation and changes over six decades. J Ornithol. 2019;160: 1015–23.
R Core Team. R: a language and environment for statistical computing [3.6.3]. Vienna, Austria: R Foundation for Statistical Computing; 2020. .
Ramula S, Öst M, Lindén A, Karell P, Kilpi M. Increased male bias in eider ducks can be explained by sex-specific survival of prime-age breeders. PLoS One. 2018;13: e0195415.
Scott P. The decoy. Severn Wildfowl Trust Ann Rep. 1949;1: 57–61.
Sheldon BC. Recent studies of avian sex ratios. Heredity. 1998;80: 397–402.
Signorell A. DescTools: tools for descriptive statistics. R package version 0.99.37. 2020. .
Sun YH, Bridgman CL, Wu HL, Lee CF, Liu M, Chiang PJ, et al. Sex ratio and survival of Mandarin Ducks in the Tachia River of central Taiwan. Waterbirds. 2011;34: 509–13.
Székely T, Weissing FJ, Komdeur J. Adult sex ratio variation: implications for breeding system evolution. J Evol Biol. 2014;27: 1500–12.
Thompson MC, DeLong RL. The use of cannon and rocket-projected nets for trapping shorebirds. Bird-Banding. 1967;38: 214–8.
Wainwright CB. How to make and use duck traps. Wildfowl. 1957;8: 44–7.
Wood KA, Ponting J, D'Costa N, Newth JL, Rose PE, Glazov P, et al. Understanding intrinsic and extrinsic drivers of aggressive behaviour in waterbird assemblages: a meta-analysis. Anim Behav. 2017;126: 209–16.
Clancy A. Hall, Gabriel C. Conroy, Dominique A. Potvin. Ex-situ avian sex skews: determinants and implications for conservation. PeerJ, 2025, 13: e19312.
DOI:10.7717/peerj.19312
2.
Jacob E. Hewitt, Anthony J. Roberts, Kelsey M. Sullivan, et al. Photo survey estimates of annual recruitment in eastern North American sea duck populations. The Journal of Wildlife Management, 2025, 89(3)
DOI:10.1002/jwmg.22714
3.
Laurence Cousseau, Pieter Sanczuk, Seppe de Mits, et al. Long-term genetic and demographic surveys reveal the impact of population history, habitat change, and conservation efforts on the globally endangered Turdus helleri (Taita Thrush). Ornithological Applications, 2025.
DOI:10.1093/ornithapp/duaf010
4.
Adrien Tableau, Iain Henderson, Sébastien Reeber, et al. Delayed dichromatism in waterfowl as a convenient tool for assessing vital rates. Peer Community Journal, 2025, 5
DOI:10.24072/pcjournal.531
5.
Monika Homolková, Petr Musil, Diego Pavón-Jordán, et al. Changes in the adult sex ratio of six duck species breeding populations over two decades. Avian Research, 2024, 15: 100187.
DOI:10.1016/j.avrs.2024.100187
6.
Iván Alambiaga, Juan S. Monrós, Ferran Palero. New Primers for Sexing Juvenile Buntings and to Assist Ex-Situ Conservation of Endangered Eastern Iberian Reed Bunting Emberiza schoeniclus witherbyi Populations. Ardeola, 2023, 71(1)
DOI:10.13157/arla.71.1.2024.sc1
7.
Kjell Larsson. Age and sex ratios of wintering Long-tailed Ducks Clangula hyemalis can be determined by analysis of photos of flying flocks at sea: A method description. Ornis Svecica, 2023, 33: 1.
DOI:10.34080/os.v33.23757
8.
Natalia A. Cossa, Laura Fasola, Ignacio Roesler, et al. Habitat use by threatened sheldgeese (Chloephaga spp.) in Austral Patagonia at two spatial scales. Polar Biology, 2022, 45(1): 13.
DOI:10.1007/s00300-021-02965-7
Table
1.
Degrees of freedom, F-values and significance levels denoting the effect of time since dilution and until analysis, temperature and pH on the sperm motility parameters
Dependent variables
Independent variables
Time since dilution and until analysis
Temperature
pH levels
Fdf
p value
Fdf
p value
Fdf
p value
Rapid progressive motility
23.902.16, 15.10
< 0.001
2.242, 13
0.15
12.384, 39
< 0.001
Slow progressive motility
2.061.85, 12.95
0.17
4.562, 13
0.03
0.584, 39
0.68
Non-progressive motility
1.017, 49
0.44
1.462, 13
0.27
0.464, 39
0.76
Immotility
10.857, 49
< 0.001
6.842, 13
0.01
6.274, 39
0.001
Progressive motility
20.192.05, 14.32
< 0.001
4.282, 13
0.04
15.264, 39
< 0.001
Sperm velocity
11.657, 49
< 0.001
0.972, 13
0.41
11.224, 39
< 0.001
LIN
2.392.19, 15.35
0.12
0.232, 13
0.80
10.354, 39
< 0.001
WOB
3.082.34, 16.40
0.07
0.212, 13
0.81
10.494, 39
< 0.001
STR
0.392.82, 19.75
0.75
0.472, 13
0.64
7.294, 39
< 0.001
The details of the building of general linear models are shown in Additional file : Tables S1‒S3 LIN linearity, WOB wobble, STR straightness Italic values are significant in the analysis