Lucas M. Leveau, Adriana Ruggiero, Thomas J. Matthews, M. Isabel Bellocq. 2019: A global consistent positive effect of urban green area size on bird richness. Avian Research, 10(1): 30. DOI: 10.1186/s40657-019-0168-3
Citation: Lucas M. Leveau, Adriana Ruggiero, Thomas J. Matthews, M. Isabel Bellocq. 2019: A global consistent positive effect of urban green area size on bird richness. Avian Research, 10(1): 30. DOI: 10.1186/s40657-019-0168-3

A global consistent positive effect of urban green area size on bird richness

More Information
  • Corresponding author:

    Lucas M. Leveau, leveau@ege.fcen.uba.ar

  • M. Isabel Bellocq—Deceased on 9 July 2019

  • Received Date: 25 Feb 2019
  • Accepted Date: 23 Jul 2019
  • Available Online: 24 Apr 2022
  • Published Date: 20 Aug 2019
  • Background 

    Although the species-urban green area relationship (SARu) has been analyzed worldwide, the global consistency of its parameters, such as the fit and the slope of models, remains unexplored. Moreover, the SARu can be explained by 20 different models. Therefore, our objective was to evaluate which models provide a better explanation of SARus and, focusing on the power model, to evaluate the global heterogeneity in its fit and slope.

    Methods 

    We tested the performance of multiple statistical models in accounting for the way in which species richness increases with area, and examined whether variability in model form was associated with various methodological and environmental factors. Focusing on the power model, we analyzed the global heterogeneity in the fit and slope of the models through a meta-analysis.

    Results 

    Among 20 analyzed models, the linear model provided the best fit to the most datasets, was the top ranked model according to our efficiency criterion, and was the top overall ranked model. The Kobayashi and power models were the second and third overall ranked models, respectively. The number of green areas and the minimum number of species within a green area were the only significant variables explaining the variation in model form and performance, accounting for less than 10% of the variation. Based on the power model, there was a consistent overall fit (r2 = 0.50) and positive slope of 0.20 for the species richness increase with area worldwide.

    Conclusions 

    The good fit of the linear model to our SARu datasets contrasts with the non-linear SAR frequently found in true and non-urban habitat island systems; however, this finding may be a result of the small sample size of many SARu datasets. The overall power model slope of 0.20 suggests low levels of isolation among urban green patches, or alternatively that habitat specialist and area sensitive species have already been extirpated from urban green areas.

  • Evolutionary biology endeavours to explain biological diversity, and as such it is critical to develop an understanding of the adaptive and functional significance of trait variation. Spermatozoa exhibit remarkable levels of morphological diversification. However, our understanding of the evolutionary causes and functional significance of this variation is limited, especially at the intraspecific level.

    We quantified variation in sperm morphology and performance between two subspecies of Long-tailed Finch (Poephila acuticauda acuticauda and P. a. hecki), a small grassfinch found in tropical northern Australia. Despite a zone of secondary contact, these subspecies are maintained as two distinct forms: P. a. acuticauda occurs in the western part of the species' range and has a yellow bill, while P. a. hecki exhibits a red bill and is found in the eastern part of the range.

    We found small, but significant differences in sperm size between these subspecies (P. a. acuticauda had longer and narrower sperm than P. a. hecki), which was surprising given the recent evolutionary origins of these two taxa (i.e. 0.3 million years ago). Additionally, both subspecies exhibited high values of between- and within-male variation in sperm morphology, though in the case of sperm midpiece length this variation was significantly lower in P. a. acuticauda relative to P. a. hecki.

    We suggest these observed differences in sperm morphology are the result of genetic drift and reflect historical processes associated with divergence between the eastern and western populations of these two subspecies. Finally, we discuss the potential implications of our findings for the process of population divergence and reproductive isolation.

    Despite their common role as fertilisers of ova, sperm cells exhibit remarkable interspecific variability in size and shape (reviewed in ). Sperm also show considerable variation among subspecies and between populations of the same species in a range of taxa. For example, significant intraspecific differences in sperm length have been reported for Drosophila (), frogs (), land snails () and birds (; ; ; ). In fact, sperm cells are the most variable cell type known (). Surprisingly, however, our understanding of the evolutionary causes and adaptive significance of this variation remains somewhat limited. Moreover, our knowledge of sperm morphological and functional variation within-species is relatively poor compared to what is known at the interspecific level. Thus studies describing variation in sperm morphology and quantifying how variation in sperm morphology corresponds to variation in sperm function are warranted, especially at the intraspecific level.

    Sperm competition is generally thought to be an important driver of evolutionary change in sperm phenotype (; ). For example, sperm competition is thought to favour the evolution of faster swimming sperm in a range of taxa, including fish (), mammals (; ), and birds (). Similarly, comparative studies have reported a positive association between sperm competition strength and sperm length (e.g. ; ; ), though this pattern is far from universal and the nature of this relationship appears to be variable (reviewed in ; and see ) for a non-linear relationship in birds. Variation in sperm size has also been linked to among-species variation in body size (; ; ), mass-specific metabolic rate () and the degree of genetic divergence among subspecies and populations (; ). Finally, sperm traits also appear to evolve as an adaptation to the female reproductive environment; sperm length is correlated with the length of sperm storage organs or their associated ducts in a variety of taxa (reviewed in ), including birds ().

    Divergence in sperm morphology among closely related taxa suggests that sperm form may evolve rapidly (; ; ), as has been shown for other ejaculatory traits (e.g. seminal fluid proteins, ). Other studies, however, have shown that total sperm size can remain relatively constant among populations over time (; ). In birds, variable rates of evolutionary change in sperm size have been linked to variation in the intensity of postcopulatory sexual selection. For example, subspecies of Bluethroat (Luscinia svecica) exhibit significant differences in sperm length, despite being a group of relatively 'young' taxa (c. 0.15-0.35 million years since divergence), and appear to experience relatively strong sperm competition (). In contrast, sperm competition is presumed absent in both the Eurasian (Pyrrhula pyrrhula) and Azores (P. murina) Bullfinch, and sperm length does not differ between the sister species despite the longer time since divergence (c. 0.6-1.5 mya) (; ). More recently, a comparative study of passerine birds found a significant, positive association between the rate of evolutionary divergence in sperm size between closely related taxa and the strength of sperm competition (). Further investigation of variation in sperm morphology between closely related taxa is thus likely to contribute to our understanding of the evolutionary processes responsible for the remarkable evolutionary diversification of sperm form.

    Variation in both sperm length () and sperm motile performance (; ; ) has been linked to fertilization success in birds. Here, we examine intraspecific variation in sperm morphology and sperm swimming speed in the Long-tailed Finch (Poephila acuticauda), a small grassfinch (family: Estrildidae) endemic to tropical northern Australia. Two subspecies of Long-tailed Finch, P. a. acuticauda and P. a. hecki, are recognized. Although phenotypically similar, the subspecies can be distinguished on the basis of bill color; The nominate P. a. acuticauda exhibits a yellow bill and occurs in the western part of the species' range, while P. a. hecki has a red bill and is found in the eastern part of the range. Differences in song structure have also been identified between the two subspecies (). A recent analysis based on multiple nuclear loci suggests that P. a. acuticauda diverged from P. a. hecki approximately 0.3 million years ago across the Ord Arid Intrusion, a minor biogeographic barrier splitting Arnhem Land and the Kimberley Plateau (). Recent mtDNA data supports the presence of these two distinct groups (western P. a. acuticauda and eastern P. a. hecki), along with the occurrence of a central region in the vicinity of the Ord Arid Intrusion where the subspecies are in contact (). We therefore tested for differences in sperm length (i.e. total sperm length and length of the individual sperm components—head, midpiece and flagellum) and sperm swimming speed between the two subspecies. We also explored variation in a relatively poorly studied aspect of sperm morphology—the ratio of acrosome length to nuclear length (A:N ratio). Although the adaptive significance of the A:N ratio is unknown, this trait appears variable in the small number of passerine species for which it has been investigated (), suggesting further investigation of the trait may be informative. Finally, we quantified how within-subspecies variation in sperm morphology corresponds to variation in sperm performance (i.e. sperm swimming speed).

    We compared sperm morphology and sperm performance in the two subspecies of Long-tailed Finch (P. a. acuticauda and P. a. hecki) using both wild-caught birds held in captivity and first generation (F1) captive bred birds. Sperm samples were collected from 43 sexually mature males over 2 days: 21 December 2011 and 9 January 2012. At the time of sampling, all birds were held in aviaries located at Macquarie University in Sydney. All individuals from P. a. hecki (n = 23) were initially captured from a breeding population in October Creek, Northern Territory (eastern region population sensu, ; 16°37′S, 134°51′E) in October 2010 and subsequently held in captivity. For P. a. acuticauda (n = 20), we sampled both wild-caught birdsheld in captivity (n = 9) and F1 captive bred birds (n = 11). Wild-caught birds were initially captured from two sites (Mt House: 17°02′S, 125°35′E and Nelson's hole: 15°49′S, 127°30′E) in Western Australia in September 2009 and subsequently held in captivity. These sites were located 250 km apart, but comprise a single breeding population (western region population sensu, ). F1 captive bred birds were hatched during January 2010 and March 2011 in the Macquarie University aviaries. Finches were maintained in captivity in mixed-sex aviaries under male-biased sex-ratio conditions and provided with food and water ad lib. The subspecies were housed separately. Nest boxes and nesting material was placed in aviaries approximately 4 weeks prior to sampling to encourage breeding activity. We noticed that eggs were found more frequently in aviaries containing P. a. hecki individuals, which may reflect inter-individual variation in the reproductive state of females. Alternatively, it may suggest that P. a. hecki were mating more actively than P. a. acuticauda males, which may have implications for variation in sperm function. Importantly, however, all males had the opportunity to breed (i.e. females and nesting materials were present in all aviaries) and were actively producing sperm at the time of sampling.

    We captured males from their aviaries using mist nets and hand nets, and placed birds in small holding cages prior to sampling. Fresh sperm samples were collected from males using cloacal massage (), and we immediately measured sperm swimming speed. Specifically, we collected exuded semen in a 10 µL capillary tube and immediately mixed it with (c. 20-40 µL) pre-heated (40 ℃) Dulbecco's Modified Eagle Medium (DMEM, Invitrogen Ltd). Next, we pipetted 6 µL of the diluted semen into a pre-heated microscopy counting chamber (depth 20 µm, Leja, Nieuw-Vennep, Netherlands) mounted on a MiniTherm slide warmer (Hamilton Thorne Inc) maintained at 40 ℃. Finally, sperm movement was recorded using a phase contrast scope (CX41, Olympus, Japan) connected to a digital video camera (Legria HF S200 Canon, Japan). For each male we recorded six different fields of view for 5 s, for a total recording time of 30 s.

    Videos of sperm motion were analysed at a later date using computer-assisted sperm analysis (CASA; HTM-CEROS sperm tracker, CEROS v.12, Hamilton Thorne Research), and all analyses were conducted without knowledge of the males' subspecies identity. In each field of view, sperm were tracked for 0.5 s and the image analyser was set with a frame rate of 50 frames/s. We also set the following cell detection parameters to exclude non-sperm particles: minimum contrast, 80-120; minimum cell size, 8-12 pixels; sperm head elongation (i.e. width/length), < 70. Additionally, we excluded non-continuous sperm tracks or sperm tracked for less than 10 frames, as well as tracks for which the maximum frame-to-frame movement exceeded the average frame-to-frame movement by 4 SDs for the same track, as such tracks tended to represent tracking errors in the software. Finally, to exclude the effects of drift in the chamber, sperm cells having a straight-line velocity (VSL, i.e. average velocity on a straight line between the start and end point of the sperm track) < 25 µm s-1, or a average path velocity (VAP, i.e. average velocity over a smoothed sperm track) < 30 µm s-1 were counted as immotile and excluded from calculations of sperm swimming speed. These criteria were based on visual inspection of cells in all analyses, which was undertaken to optimize the detection of motile sperm, and are in line with previous studies of passerine sperm (e.g. ; ). Finally, following this filtering process, males with fewer than 20 motile sperm tracks were excluded from all analyses of sperm motile performance.

    The total number of motile sperm that were tracked for each male ranged from 23 to 465 (median = 219, mean = 218.4 ± 18.5 s.e.). For each sperm we recorded curvilinear velocity (VCL, i.e. velocity over the actual sperm track), VSL and VAP. However, we choose to use VCL for statistical analyses because this metric measures the actual path of sperm movement and thus is likely to represent sperm velocity better than simpler approximations. Nonetheless, sperm motility parameters were strongly intercorrelated (all r > 0.77, p < 0.001), and analyses using VAP and VSL returned qualitatively similar results (data not shown). Finally, we calculated the proportion of motile sperm as the number of motile tracks divided by the total number of cells.

    After assessing sperm swimming speed, we fixed the remainder of the sperm sample in 5 % buffered formaldehyde solution. For examination of sperm morphology, we placed an aliquot of the fixed sperm sample on a microscope slide and allowed it to air dry. We then captured high magnification (320×) digital images of sperm using a light microscope (DM6000 B Leica digital microscope) fitted with a digital camera (DFC420, Leica Microsystems) and measured sperm morphology using digital image analysis (Leica Application suite v. 2.6.0 R1). Following recommendations in the literature (; ), 10 morphologically normal and undamaged sperm were analysed from each individual to obtain measurements (to the nearest 0.1 µm) of the following sperm traits: (1) head length, (2) midpiece length, (3) flagellum length, and (4) total sperm length. All measurements were taken blind to the subspecies identity of individuals. Additionally, these measures were used to calculate the following composite measures: (5) ratio of flagellum length to head length and (6) ratio of midpiece length to flagellum length.

    We also used scanning electron microscopy (SEM) to obtain high-resolution images of sperm from 10 individuals from each subspecies. To prepare sperm for SEM, we first attached sperm cells to glass coverslips precoated with poly-lysine (1 mg mL-1; Sigma P1274) by placing a small (c. 10 μL) aliquot of formalin-fixed sperm onto each coverslip and incubating samples overnight in a wet chamber at room temperature. Next, sperm were dehydrated using a graded ethanol series consisting of a 10-min treatment with 70, 80, 90, and 96 % ethanol, followed by 4 × 15-min treatments with 100 % ethanol. Samples were then critical point dried (BAL-TEC CPD 030 Critical Point Dryer) and coverslips were mounted on SEM stubs using carbon tape. Finally, samples were sputter coated with 6 nm platinum using a Cressington 308R coating system, and samples were examined and digital images recorded using a Hitachi S-4800 Field Emission Scanning Electron Microscope operated at 5.0 kV.

    SEM images were used toobtain the following additional measures: (1) sperm head width, and (2) ratio of acrosome length to nuclear length (A:N ratio). For these measures, images were taken at 9000× magnification and, for each individual, 10-15 intact and undamaged sperm cells were selected for imaging and measurement by systematic uniform random sampling. We then used standard stereological methods to obtain accurate measures of head width, total head length (HL) and the length of the sperm nucleus (NL). More specifically, measurements were obtained using a counting grid and the Buffon formula for length of a line trace L = (π/4) × l × d, in which L = length in micrometres, l = the sum of the intersections between L and the grid lines, and d = the grid line spacing in micrometres (). Sperm head width was measured at the boundary between the acrosome and the nucleus, and the A:N ratio was obtained using the formula, A:N ratio = (HL - NL)/NL.

    Data for P. a. acuticauda included samples from both wild-caught and captive bred (F1) birds. Thus we first tested for potential differences in sperm morphology and swimming speed between these groups using t tests or Wilcoxon rank sum tests. However, we found no significant differences in any of the sperm traits measured (all p > 0.21), and therefore these birds were treated as a single group in all subsequent analyses.

    To test for differences in sperm morphology and swimming speed (i.e. VCL) between P. a. acuticauda and P. a. hecki, we used linear mixed-effects models with subspecies included as a fixed factor and male identity as a random factor, running separate models for each sperm trait. To account for heteroskedasticity in some models, we specified the variance structure of models: inter-factor variation was modeled using the VarIdent variance structure in the sperm midpiece length and A:N ratio models and we applied the varExp variance structure using the fitted values to the model of VCL. The decision to include variance structure in models and choose between potential variance structures was based on likelihood ratio tests and AIC values, and modeling assumptions (i.e. heterogeneity of variance, normality of residuals) were validated through visual inspection of residual plots (). Additionally, we used Fisher's F test to compare variance in sperm traits between the subspecies using the mean values within individuals, and tested for differences between species in the proportion of motile sperm using a two-sample t test.

    Next, we calculated the within-male coefficient of variation (CV) in sperm traits as CVwm = (standard deviation [SD]/mean) × 100, and compared values between subspecies using a two-sample t test. We also calculated the among-male CV in total sperm length for both subspecies as CVam = (SD/mean) × 100, and adjusted these values for small sample size according to the formula: adjusted CVam = (1 + 1/4n) × CVam (). Finally, separately for each subspecies, we used linear models to determine the relationships between sperm morphology and sperm swimming speed. Because the number of sperm cells tracked varied considerably between individuals (see above) we also included the number of tracked sperm as a covariate in all models, and, as before, model validity was assessed through inspection of residual plots. All analyses were performed with R (v. 3.0.2; ) and, where appropriate, the R package 'nlme' (). All proportion data was arcsine square-root transformed and, when necessary, other data were ln-transformed to meet modeling assumptions.

    Scanning electron microscopy showed that sperm from both subspecies exhibit the typical helical shaped head of passerine sperm, with a helical membrane restricted to the acrosome and the mitochondrial helix extending along a large proportion of the flagellum (Fig. 1). However, sperm size differed slightly, but significantly, between the subspecies. Specifically, P. a. acuticauda had longer sperm (i.e. total sperm length) and narrower sperm (i.e. sperm head width) than P. a. hecki, while the ratio of midpiece to flagellum length (i.e. relative midpiece length) was greatest in P. a. hecki (Table 1). In contrast, there was no significant difference between the subspecies in sperm head, midpiece or flagellum length; though in the case of flagellum length there was a nearly significant difference between the subspecies (P. a. acuticauda tended to have a longer flagellum compared to P. a. hecki; Table 1). There was also no difference between the subspecies in the ratio of flagellum length to head length, and no difference in sperm swimming speed or the proportion of motile sperm in ejaculates (Table 1). Similarly, there was no difference between the subspecies in the mean A:N ratio (Table 1), though in both subspecies, males showed considerable variation in A:N ratio: values in P. a. acuticauda ranged from 0.60 to 0.85, while values ranged from 0.65 to 0.94 in P. a. hecki. Finally, in the comparison of variance in trait mean values between the subspecies we found no difference between P. a. acuticauda and P. a. hecki in sperm morphology (head: F = 0.66, p = 0.35; midpiece: F = 1.45, p = 0.43; flagellum: F = 1.79, p = 0.22; total: F = 1.81, p = 0.21; width: F = 0.32, p = 0.10; midpiece:flagellum: F = 0.88, p = 0.76; flagellum:head ratio: F = 1.48, p = 0.41; A:N ratio: F = 0.93, p = 0.92), sperm performance (VCL: F = 0.99, p = 0.97) or the proportion of motile sperm in ejaculates (F = 1.21, p = 0.70).

    Figure 1. Scanning electron micrographs of sperm cells from the Long-tailed Finch. Typical sperm of the Long-tailed Finch showing a the head and anterior portion of the flagellum with the helical midpiece (P. a. acuticauda shown here), and sperm head morphology of b P. a. heckiand and c P. a. acuticauda. Arrows indicate the junctions between the acrosome and nucleus and the nucleus and flagellum
    Figure  1.  Scanning electron micrographs of sperm cells from the Long-tailed Finch. Typical sperm of the Long-tailed Finch showing a the head and anterior portion of the flagellum with the helical midpiece (P. a. acuticauda shown here), and sperm head morphology of b P. a. heckiand and c P. a. acuticauda. Arrows indicate the junctions between the acrosome and nucleus and the nucleus and flagellum
    Table  1.  Data on sperm morphology and performance for male Long-tailed Finches for each of the two subspecies, P. a. acuticauda and P. a. hecki
    Trait P. a. acuticauda
    Mean ± SD
    P. a. hecki
    Mean ± SD
    t p
    Total length (μm) 75.50 ± 4.35 (n = 19) 72.02 ± 5.85 (n = 23) 2.15 0.038
    Head length (μm) 12.80 ± 0.73 (n = 19) 12.77 ± 0.59 (n = 23) 0.19 0.85
    Midpiece length (μm) 39.98 ± 4.41 (n = 19) 40.97 ± 5.30 (n = 23) −0.65 0.52
    Flagellum length (μm) 62.70 ± 4.61 (n = 19) 59.25 ± 6.17 (n = 23) 2.01 0.051
    Head width (μm) 6.61 ± 0.27 (n = 10) 7.03 ± 0.49 (n = 10) 2.43 0.026
    Midpiece:flagellum 0.64 ± 0.07 (n = 19) 0.69 ± 0.06 (n = 23) 2.79 0.008
    Flagellum:head 4.92 ± 0.51 (n = 19) 4.66 ± 0.62 (n = 23) 1.43 0.16
    Acrosome:nucleus 0.75 ± 0.09 (n = 10) 0.77 ± 0.09 (n = 10) −0.45 0.66
    Total sperm length CVwm 2.71 ± 0.89 (n = 19) 3.00 ± 1.45 (n = 23) 0.54 0.60
    VCL (μm s−1) 91.33 ± 15.00 (n = 18) 86.70 ± 14.88 (n = 22) 0.99 0.33
    Proportion of motile sperm 0.70 ± 0.15 (n = 18) 0.75 ± 0.16 (n = 22) 0.98 0.33
    Descriptive statistics are based on mean values calculated from ten sperm cells for each male, while significance testing used linear mixed-effects models with subspecies included as a fixed factor and male identity as a random factor
    VCL curvilinear velocity in μm s−1
    Significant values shown in italics (p < 0.05)
     | Show Table
    DownLoad: CSV

    The subspecies showed different values of among-male coefficient of variation in total sperm length (CVam: P. a. acuticauda, 5.82; P. a. hecki, 8.21); though as there was no significant difference in variance in total sperm length between the two subspecies (see above) this difference cannot be considered statistically significant. Within-male coefficient of variation in sperm total length also differed between the subspecies, and as before values for P. a. hecki exceeded those for P. a. acuticauda (CVwm: P. a. acuticauda, 2.71; P. a. hecki, 3.00), though again this difference was not significant (Table 1). Similarly, there was no difference between the subspecies in within-male variation in sperm head length (t = 0.38, p = 0.71) or flagellum length (t = 1.27, p = 0.21). In contrast, within-male variation in sperm midpiece length was (marginally) significantly greater in P. a. hecki compared to P. a. acuticauda (t = -2.00, p = 0.05).

    The relationship between sperm morphology and swimming performance also differed between the subspecies. In P. a. acuticauda, sperm swimming speed was significantly, positively related to both absolute and relative midpiece length, but was not associated with sperm head length, flagellum length, total sperm length or the ratio of flagellum length to head length (Table 2; Fig. 2a). In contrast, sperm swimming speed was significantly, positively related to sperm midpiece and flagellum length, as well as total sperm length and the ratio of flagellum length to head length, but unrelated to either sperm head length or relative midpiece length in P. a. hecki (Table 2; Fig. 2b). Finally, sperm swimming speed was positively associated with the number of tracked sperm in P. a. hecki (all p < 0.01), whereas these traits showed no association in P. a. acuticauda (all p > 0.35).

    Table  2.  Results from linear models testing the relationship between sperm swimming speed (i.e. VCL) and a number of sperm morphological traits in (a) P. a. acuticauda and (b) P. a. hecki
    Sperm trait Coefficient (±SE) t p
    (a) P. a. acuticauda
    Head length −1.03 ± 0.8 −1.28 0.22
    Midpiece length 1.14 ± 0.27 4.20 0.0008
    Flagellum length 0.44 ± 0.55 0.80 0.44
    Total sperm length 0.44 ± 0.72 0.61 0.55
    Flagellum:head 0.44 ± 0.38 1.16 0.26
    Midpiece:flagellum 1.59 ± 0.52 3.04 0.008
    (b) P. a. hecki
    Head length −1.27 ± 0.70 −1.80 0.09
    Midpiece length 1.03 ± 0.09 11.13 < 0.0001
    Flagellum length 1.10 ± 0.16 6.79 < 0.0001
    Total sperm length 1.44 ± 0.21 6.73 < 0.0001
    Flagellum:head 0.82 ± 0.15 5.60 < 0.0001
    Midpiece:flagellum 78.57 ± 39.56 1.99 0.06
    Sperm count data was also included in each model, but for simplicity and because the results of the covariate are not relevant to the relationships being tested, we present only the results of the correlation between sperm morphology and velocity
    Significant relationships shown in italics (p < 0.05)
     | Show Table
    DownLoad: CSV
    Figure 2. Relationship between sperm swimming speed (VCL) and the ratio of the lengths of the sperm flagellum and head in the two subspecies of Long-tailed Finch. a P. a. acuticauda, and b P. a. hecki. In b line represents a simple regression line. See main text for full statistical details
    Figure  2.  Relationship between sperm swimming speed (VCL) and the ratio of the lengths of the sperm flagellum and head in the two subspecies of Long-tailed Finch. a P. a. acuticauda, and b P. a. hecki. In b line represents a simple regression line. See main text for full statistical details

    In the current study, we show that the two subspecies of Long-tailed Finch exhibit typical passerine sperm morphology: sperm are filiform, the acrosome bears a helical membrane (or keel) and the single fused mitochondria twists along much of the length of the flagellum (i.e. mitochondrial helix; ). However, we also found significant differences in sperm size between the two subspecies. Specifically, P. a. acuticauda had slightly longer, but narrower sperm relative to P. a. hecki.

    Variation in sperm size may be attributed to either selection or genetic drift over evolutionary time. In the case of the Long-tailed Finch, we suggest that the subspecies differences in sperm morphology are likely to have primarily resulted from genetic drift. Though it is perhaps surprising to observe any difference in sperm size given the relatively short time since these taxa split (i.e. 0.3 Mya, ), there is some evidence that the western P. a. acuticauda has experienced a genetic bottleneck due to a small founding population size (). Under such a scenario, it is possible that sperm size in individuals in the founder population represented values from the upper portion of the distribution (i.e. sperm tended to be longer), allowing the differences observed between the contemporary taxa to evolve relatively rapidly via genetic drift. Interestingly, the trend towards lower phenotypic variation in sperm morphology observed between males (i.e. CVam) in P. a. acuticauda is also indicative of a bottleneck followed by genetic drift. Specifically, given the strong genetic basis of sperm length (; ), reduced among-male variance in sperm size is predicted under conditions of small effective population sizes with reduced genetic variation due to drift. Thus, we suggest the subspecies differences observed here may simply reflect the historical processes associated with the divergence of the western and eastern populations.

    An alternate explanation for the differences observed between the subspecies is that sperm size has diverged rapidly as a result of high levels of sperm competition experienced by the two taxa () or because the two populations vary in the strength or direction of selection. However, we consider these explanations unlikely for the following reasons. First, the one available estimate of extra-pair paternity in the Long-tailed Finch (in P. a. acuticauda) indicates low to moderate rates of extra-pair paternity (i.e. 12.8 %, Griffith, pers comm), implying sperm competition is not especially strong in this species. Second, relative testes size is extremely low in both subspecies (just 0.26 and 0.34 % of male body mass, P. a. acuticauda and P. a. hecki respectively; see Additional file 1), suggesting sperm competition is in fact extremely low or absent in these taxa (cf. ; ; ; ; ; ). Finally, in both subspecies, we found high phenotypic variance in sperm morphology both among- (CVam) and within-males (CVwm). Moreover, while values of CVam and CVwm tended to be higher in P. a. hecki relative to P. a. acuticauda, in general these differences were not significant (with the exception of CVwm for midpiece length). In a range of taxa, including birds, comparative studies have shown that among- and within-male variation in sperm length decreases with increasing values of extra-pair paternity rates and relative testes size (; ; ; ; ; ). Consequently, sperm competition appears to be low in both subspecies, and data on phenotypic variance in sperm length suggests the potential for selection via sperm competition is unlikely to differ between P. a. acuticauda and P. a. hecki.

    In this study, we also examined the ratio of acrosome length to nucleus length, a trait that has received relatively little attention in studies of avian sperm biology to date. Available data, however, suggests this ratio is variable, ranging from < 0.1 to 4 across passerine species (). suggested that the Passerida are characterized by having an acrosome that is longer than the nucleus (i.e. A:N ratio > 1). In contrast to this, however, we found A:N ratio was less than 1 (i.e. the acrosome was shorter than the nucleus) in both subspecies of Long-tailed Finch. Though the adaptive significance of this trait is unclear, we also found that there was considerable variability in this trait: values across both subspecies ranged from 0.6 to 0.94. Thus, there appears to be sufficient variation in this trait on which selection could potentially act, and we suggest it may be valuable to investigate the relative roles of phylogeny, drift and selection in shaping variation in this trait in future comparative studies of avian sperm biology.

    In order to understand the remarkable evolutionary diversification of sperm morphology, it is helpful to develop an understanding of the adaptive and functional significance of sperm trait variation. Sperm swimming speed has been linked to fertilization success under non-competitive and competitive mating scenarios in a broad range of species (, but see ; ), including birds (; ; ). Similarly, a recent study found that longer sperm fertilize more eggs under competitive mating conditions in the Zebra Finch (Taeniopygia guttata, ). Moreover, sperm length is generally thought to be an important determinant of sperm swimming speed, and indeed theoretical () and both intra- and inter-specific empirical studies provide evidence for such a link (e.g. in birds ; ). However, further studies show no relationship (e.g. ; ) or a negative relationship between these traits (e.g. ; reviewed in ; ; ). Thus no clear patterns are evident regarding how sperm length influences swimming speed. It has therefore been suggested that, rather than the absolute length of a sperm's constituent parts, the ratio of flagellum length to head size may be a better predictor of sperm swimming speed as this trait balances the drag produced from the head with the propulsive thrust of the flagellum (). Yet even this trait appears to be inconsistently associated with sperm velocity, even within a single species (e.g. ; ). Similarly, in the current study we found the ratio of flagellum to head length was positively correlated with sperm velocity in P. a. hecki, but not P. a. acuticauda. Thus, our results add to the growing body of evidence suggesting that the mechanism linking sperm structure and function may not be straightforward and that simply incorporating the flagellum to head length ratio in studies of sperm performance is unlikely to fully resolve sperm structure-function relationships. At least for passerines, we suggest future investigations of sperm shape may help further elucidate how sperm morphology translates into sperm performance.

    The differences in sperm morphology observed in the current study, combined with knowledge of the general breeding ecology of the Long-tailed Finch, suggest this species may be an interesting system for investigations into processes associated with population divergence and reproductive isolation. Specifically, although the subspecies currently meet and interbreed in a zone of secondary contact in the vicinity of the Ord Arid Intrusion (), mitochondrial data do not support the idea of contemporary gene flow between the eastern and western regions (). Moreover, there is little variation in the expression of both yellow and red bill color within each of the subspecies' ranges (Griffith, unpublished data) until the area of the relatively narrow contact zone where intermediate phenotypes have been observed (; also Griffith unpublished data), suggesting that the genes underlying this trait are not being readily introgressed from one subspecies to another. The subspecies are thought to have diverged 300, 000 years ago when separated by an arid intrusion through the savannah belt that runs across the top end of Australia in the Pleistocene Ord Arid Intrusion (; ). The aridification of the Australian continent occurred in cycles throughout the Quaternary period with the last major event occurring over 10, 000 years ago ( ), and the subspecies of Long-tailed Finch have likely been in contact for around that period of time. The maintenance of the two subspecies despite the length of time that they are likely to have been in contact suggests the existence of reproductive isolating mechanisms that have prevented, or at least slowed, the rate of admixture between the genes of the two lineages.

    Significant differences between the subspecies in the expression of both song () and bill color () imply that pre-copulatory mate choice may play a role in the maintenance of the subspecies in the contact zone. However, we suggest that post-copulatory processes, including those involving sperm traits, are also worth investigating in this system for a number of reasons. First, preliminary evidence suggests assortative mating based on bill color may be weak (; Griffith unpublished data). Next, given the positive correlation between sperm length and the length of female sperm storage organs (reviewed in ; see for evidence in birds), it has been widely hypothesized that divergence in sperm traits between allopatric populations may lead to incompatibilities between males and females upon secondary contact (), and there is growing empirical evidence that divergence in sperm traits can have implications for the generation and maintenance of reproductive barriers in closely related taxa (e.g. Drosophila, ; , ; mice, ; ). Finally, variation in sperm length has been linked to fertilization success in birds (). Thus it is possible that the differences in sperm size observed in the subspecies of Long-tailed Finch may influence the breeding dynamics of the species, especially in the current contact zone. For example, heterosubspecific pairings (i.e. P. a. acuticauda × P. a. hecki) might experience a sperm-sperm storage tubule mismatch leading to lower sperm fertilization success and reduced fertility, which could in turn generate selection for elevated levels of extra-pair paternity in such heterosubspecific pairs, equivalent to the pattern observed in Ficedula flycatcher species in a contact zone (). Consequently, we recommend future studies investigate the fertility effects of heterosubspecies pairings (relative to consubspecific pairings) and examine the potential role of sperm variation in individual fitness in this system.

    In summary, we examined differences in sperm morphology, sperm swimming speed and sperm structure-function relationships between two genetically distinct subspecies of Long-tailed Finch. We found significant differences in sperm size between the closely related taxa and suggest that these differences may have arisen via drift during a period of allopatry. Though these differences were relatively small, we discuss the potential implications of our findings for the process of population divergence and reproductive isolation and suggest that these taxa would make an interesting model system for the study of how post-copulatory processes, and sperm traits in particular, may contribute to reproductive isolation between intergrading populations.

    Additional file 1. Relative testes mass in the Long-tailed Finch.

    MR conceived the study, collected and analyzed the sperm samples, analyzed the data and wrote the paper. SCG conceived the study, contributed reagents/ material/analysis tools and helped to draft the manuscript. AH performed electron microscopy, implemented stereological methods for obtaining measurements and helped draft the manuscript. JTL contributed reagents/ material/analysis tools and helped to draft the manuscript. All authors read and approved the final manuscript.

    We would like to thank Lars Erik Johannessen for help with sperm measurements, and Becky Cramer and Anna Kearns for useful discussion. This work was conducted under the authority of the Macquarie University Animal Ethics Committee (ARA No. 2007/037). SCG and the Long-tailed Finchresearch were supported by Australian Research Council Discovery Project Grant DP0881019 (to SCG). MR and JTL were supported by the Research Council of Norway Grant 196554, and MR acknowledges a Young Research Talent grant from the Research Council of Norway (230434/F20).

    The authors declare that they have no competing interests.

  • Anderson MJ, Willis TJ. Canonical analysis of principal coordinates: a useful method of constrained ordination for ecology. Ecology. 2003;84:511-25.
    Batllori X, Uribe F. Aves nidificantes de los jardines de Barcelona. Misc Zool. 1998;12:283-93.
    Beninde J, Veith M, Hochkirch A. Biodiversity in cities needs space: a meta-analysis of factors determining intra-urban biodiversity variation. Ecol Lett. 2015;18:581-92.
    Bino G, Levin N, Darawshi S, Van Der Hal N, Reich-Solomon A, Kark S. Accurate prediction of bird species richness patterns in an urban environment using Landsat-derived NDVI and spectral unmixing. Int J Remote Sens. 2008;29:3675-700.
    Blair RB. Land use and avian species diversity along an urban gradient. Ecol Appl. 1996;6:506-19.
    Borenstein MH, Higgins LV, Rothstein JPT. Introduction to meta-analysis. Chichester: Wiley; 2009.
    Burghardt KT, Tallamy DW, Gregory Shriver W. Impact of native plants on bird and butterfly biodiversity in suburban landscapes. Conserv Biol. 2009;23:219-24.
    Burnham KP, Anderson DR. Model selection and multimodel inference: a practical information-theoretic approach. New York: Springer Science & Business Media; 2002.
    Chace JF, Walsh JJ. Urban effects on native avifauna: a review. Landsc Urban Plan. 2006;74:46-69.
    Chavez-Almonacid CA. Relación entre la avifauna, la vegetación y las construcciones en plazas y parques de la ciudad de Valdivia. Tesis de licenciatura: Universidad Austral de Chile, Valdivia; 2014.
    Chivian E, Bernstein AS. Embedded in nature: human health and biodiversity. Environ Health Perspect. 2004;112:A12.
    Connor EF, McCoy ED. The statistics and biology of the species-area relationship. Am Nat. 1979;113:791-833.
    Croci S, Butet A, Georges A, Aguejdad R, Clergeau P. Small urban woodlands as biodiversity conservation hot-spot: a multi-taxon approach. Landsc Ecol. 2008;23:1171-86.
    De la Peña M. Nidos de aves argentinas. Santa Fe: Universidad Nacional del Litoral; 2010.
    Del Hoyo J, Elliott A, Christie D (1994-2011) Handbook of the birds of the world. Barcelona: Lynx editions
    Dengler J. Which function describes the species-area relationship best? A review and empirical evaluation. J Biogeogr. 2009;36:728-44.
    Drakare S, Lennon JJ, Hillebrand H. The imprint of the geographical, evolutionary and ecological context on species-area relationships. Ecol Lett. 2006;9:215-27.
    Dunn RR, Gavin MC, Sanchez MC, Solomon JN. The pigeon paradox: dependence of global conservation on urban nature. Conserv Biol. 2006;20:1814-6.
    Evans BS, Reitsma R, Hurlbert AH, Marra PP. Environmental filtering of avian communities along a rural-to-urban gradient in Greater Washington, DC, USA. Ecosphere. 2018;9:2402.
    Faeth SH, Bang C, Saari S. Urban biodiversity: patterns and mechanisms. Ann NY Acad Sci. 2011;1223:69-81.
    Faggi A, Perepelizin P. Riqueza de aves a lo largo de un gradiente de urbanización en la ciudad de Buenos Aires. Revista del Museo Argentino de Ciencias Naturales nueva serie. 2006;8:289-97.
    Fattorini S, Mantoni C, De Simoni L, Galassi D. Island biogeography of insect conservation in urban green spaces. Environ Conserv. 2018a;45:1-10.
    Fattorini S, Lin G, Mantoni C. Avian species-area relationships indicate that towns are not different from natural areas. Environ Conserv. 2018b;45:419-24.
    Fernández-Juricic E. Avian spatial segregation at edges and interiors of urban parks in Madrid, Spain. Biodivers Conserv. 2001;10:1303-16.
    Fernández-Juricic E, Jokimäki J. A habitat island approach to conserving birds in urban landscapes: case studies from southern and northern Europe. Biodivers Conserv. 2001;10:2023-43.
    Fuller RA, Irvine KN, Devine-Wright P, Warren PH, Gaston KJ. Psychological benefits of greenspace increase with biodiversity. Biol Lett. 2007;3:390-4.
    Garaffa PI, Filloy J, Bellocq MI. Bird community responses along urban-rural gradients: does town size matter? Landsc Urban Plan. 2009;90:33-41.
    Garden J, Mcalpine C, Peterson ANN, Jones D, Possingham H. Review of the ecology of Australian urban fauna: a focus on spatially explicit processes. Austral Ecol. 2006;31:126-48.
    Grimm NB, Faeth SH, Golubiewski NE, Redman CL, Wu J, Bai X, Briggs JM. Global change and the ecology of cities. Science. 2008;319:756-60.
    Gurevitch J, Hedges LV. Statistical issues in ecological meta-analyses. Ecology. 1999;80:1142-9.
    Guilhaumon F, Mouillot D, Gimenez O. mmSAR: an R-package for multimodel species-area relationship inference. Ecography. 2010;33:420-4.
    Hanski I, Zurita GA, Bellocq MI, Rybicki J. The species-fragmented area relationship. P Natl Acad Sci USA. 2013;110:12715-20.
    He F, Legendre P. On species-area relations. Am Nat. 1995;148:719-37.
    Hedges L, Olkin I. Statistical models for meta-analysis. New York: Academic Press; 1985.
    Hilty SL. Birds of Venezuela. New Jersey: Princeton University Press; 2002.
    Hilty SL, Brown WL, Brown B. A guide to the birds of Colombia. New Jersey: Princeton University Press; 1986.
    Hopewell S, McDonald S, Clarke M, Egger M. Grey literature in meta-analyses of randomized trials of health care interventions. Cochrane Database Syst Rev. 2007. .
    Hubbell SP. The unified neutral theory of biodiversity and biogeography. California: Princeton University Press; 2001.
    Hume R. Complete birds of Britain and Europe. London: Dorling Kindersley; 2002.
    Husté A, Boulinier T. Determinants of bird community composition on patches in the suburbs of Paris, France. Biol Conserv. 2011;144:243-52.
    Jokimäki J, Huhta E. Artificial nest predation and abundance of birds along an urban gradient. Condor. 2000;102:838-47.
    Kazmierczak K, van Perlo B. A field guide to the birds of India, Sri Lanka, Pakistan, Nepal, Bhutan, Bangladesh, and the Maldives. New Delhi: Om Book Service; 2000.
    La Sorte FA, Lepczyk CA, Aronson MF, Goddard MA, Hedblom M, Katti M, MacGregor-Fors I, Mörtberg U, Nilon CH, Warren PS, Williams NS. The phylogenetic and functional diversity of regional breeding bird assemblages is reduced and constricted through urbanization. Divers Distrib. 2018;24:928-38.
    Leveau LM, Leveau CM. Does urbanization affect the seasonal dynamics of bird communities in urban parks? Urban Ecosyst. 2016;19:631-47.
    Lizée MH, Mauffrey JF, Tatoni T, Deschamps-Cottin M. Monitoring urban environments on the basis of biological traits. Ecol Indicat. 2011;11:353-361.
    MacArthur RH, Wilson EO. The theory of island biogeography. Monographs in Population Biology, vol. 1. New Jersey: Princeton University Press; 1967.
    MacGregor-Fors I, Ortega-Álvarez R. Fading from the forest: bird community shifts related to urban park site-specific and landscape traits. Urban For Urban Green. 2011;10:239-46.
    MacGregor-Fors I, Morales-Pérez L, Schondube JE. Migrating to the city: responses of neotropical migrant bird communities to urbanization. Condor. 2010;112:711-7.
    Magle SB, Hunt VM, Vernon M, Crooks KR. Urban wildlife research: past, present, and future. Biol Conserv. 2012;155:23-32.
    Matthews TJ. Analysing and modelling the impact of habitat fragmentation on species diversity: a macroecological perspective. Front Biogeogr. 2015;7:60-8.
    Matthews TJ, Guilhaumon F, Triantis KA, Borregaard MK, Whittaker RJ. On the form of species-area relationships in habitat islands and true islands. Global Ecol Biogeogr. 2016a;25:847-58.
    Matthews TJ, Triantis KA, Rigal F, Borregaard MK, Guilhaumon F, Whittaker RJ. Island species-area relationships and species accumulation curves are not equivalent: an analysis of habitat island datasets. Global Ecol Biogeogr. 2016b;25:607-18.
    Matthews TJ, Triantis K, Whittaker RJ, Guilhaumon F. sars: an R package for fitting, evaluating and comparing species-area relationship models. Ecography. 2019;42:1446-55.
    McKinney ML. Urbanization as a major cause of biotic homogenization. Biol Conserv. 2006;127:247-60.
    Miller JR. Hobbs RJ Conservation where people live and work. Conserv Biol. 2002;16:330-7.
    Mitchell MH. Observations on birds of southeastern Brazil. Toronto: University of Toronto Press; 1957.
    Møller AP, Diaz M, Flensted-Jensen E, Grim T, Ibáñez-Álamo JD, Jokimäki J, Mänd R, Markó G, Tryjanowski P. High urban population density of birds reflects their timing of urbanization. Oecologia. 2012;170:867-75.
    Munyenyembe F, Harris J, Hone J, Nix H. Determinants of bird populations in an urban area. Aust J Ecol. 1989;14:549-57.
    Murgui E. Effects of seasonality on the species-area relationship: a case study with birds in urban parks. Global Ecol Biogeogr. 2007;16:319-29.
    National Geographic Society (US). Field guide to the birds of North America. New York: National Geographic Society; 1999.
    Natuhara Y, Imai C. Prediction of species richness of breeding birds by landscape-level factors of urban woods in Osaka Prefecture, Japan. Biodivers Conserv. 1999;8:239-53.
    Nielsen AB, van den Bosch M, Maruthaveeran S, van den Bosch CK. Species richness in urban parks and its drivers: a review of empirical evidence. Urban Ecosyst. 2014;17:305-27.
    Olson DM, Dinerstein E, Wikramanayake ED, Burgess ND, Powell GVN, Underwood EC, D'amico JA, Itoua I, Strand HE, Morrison JC, Loucks CJ, Allnutt TF, Ricketts TH, Kura Y, Lamoreux JF, Wettengel WW, Hedao P, Kassem KR. Terrestrial ecoregions of the world: a new map of life on earth. Bioscience. 2001;51:933-8.
    Ortega-Álvarez R, MacGregor-Fors I. Dusting-off the file: a review of knowledge on urban ornithology in Latin America. Landsc Urban Plan. 2011;101:1-10.
    Paradis E, Baillie SR, Sutherland WJ, Gregory RD. Patterns of natal and breeding dispersal in birds. J Anim Ecol. 1998;67:518-36.
    Park CR, Lee WS. Relationship between species composition and area in breeding birds of urban woods in Seoul, Korea. Landsc Urban Plan. 2000;51:29-36.
    Pautasso M, Böhning-Gaese K, Clergeau P, et al. Global macroecology of bird assemblages in urbanized and semi-natural ecosystems. Global Ecol Biogeogr. 2011;20:426-36.
    Peterson R, Mountfort G, Hollom PAD, Díaz G. Guía de campo de las aves de España y demás países de Europa. Barcelona: Omega; 1973.
    Preston FW. The canonical distribution of commonness and rarity: part Ⅰ. Ecology. 1962;43:185-215.
    Rahbek C. The relationship among area, elevation, and regional species richness in neotropical birds. Am Nat. 1997;149:875-902.
    R Core Team. R: A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria, 2019. .
    Rosenberg MS. The file-drawer problem revisited: a general weighted method for calculating fail-safe numbers in meta-analysis. Evolution. 2005;59:464-8.
    Rosenberg MS, Adams DC, Gurevitch J. MetaWin: statistical software for meta-analysis. Sunderland: Sinauer Associates; 2000.
    Rosenthal R. The file drawer problem and tolerance for null results. Psychol Bull. 1979;86:638.
    Rosenzweig ML. Species diversity in space and time. Cambridge: Cambridge University Press; 1985.
    Scheiner SM, Chiarucci A, Fox GA, Helmus MR, McGlinn DJ, Willig MR. The underpinnings of the relationship of species richness with space and time. Ecol Monogr. 2011;81:195-213.
    Seto KC, Fragkias M, Güneralp B, Reilly MK. A meta-analysis of global urban land expansion. PLoS ONE. 2011;6:e23777.
    Shochat E, Warren PS, Faeth SH, McIntyre NE, Hope D. From patterns to emerging processes in mechanistic urban ecology. Trends Ecol Evol. 2006;21:186-91.
    Stott I, Soga M, Inger R, Gaston KJ. Land sparing is crucial for urban ecosystem services. Front Ecol Environ. 2015;13:387-93.
    Szlavecz K, Warren P, Pickett S. Biodiversity on the urban landscape. In: Concotta RP, Gorenflo LJ, editors. Human populations, its influences on biological diversity. Ecological studies, vol. 214. Berlin: Springer-Verlag; 2011.
    Sukhdev P. Foreword. In: Elmqvist T, Fragkias M, Goodness J, Güneralp B, Marcotullio PJ, McDonald RI, Parnell S, Schewenius M, Sendstad M, Seto KC, Wilkinson C, editors. Urbanization, biodiversity and ecosystems services: Challenges and opportunities. Dordrecht: Springer; 2013.
    Sutherland GD, Harestad AS, Price K, Lertzman KP. Scaling of natal dispersal distances in terrestrial birds and mammals. Conserv ecol. 2000. .
    Tjørve E. Shapes and functions of species-area curves: a review of possible models. J Biogeogr. 2003;30:827-35.
    Tjørve E. Shapes and functions of species-area curves (Ⅱ): a review of new models and parameterizations. J Biogeogr. 2009;36:1435-45.
    Tjørve E, Turner WR. The importance of samples and isolates for species-area relationships. Ecography. 2009;32:391-400.
    Triantis KA, Guilhaumon F, Whittaker RJ. The island species-area relationship: biology and statistics. J Biogeogr. 2012;39:215-31.
    Tummers B. Data Thief Ⅲ (v. 1.1). 2006. . Accessed 25 Mar 2017.
    United Nations. World urbanization prospects: the 2014 revision. Highlights (ST/ESA/SER.A/352). 2014.
    Urquiza A, Mella JE. Riqueza y diversidad de aves en parques de Santiago durante el período estival. Boletín Chileno de Ornitología. 2002;9:12-21.
    Vaccaro AS, Filloy J, Bellocq MI. What land use better preserves taxonomic and functional diversity of birds in a grassland biome? Avian Conserv Ecol. 2019;14:1.
    Watling JI, Donnelly MA. Fragments as islands: a synthesis of faunal responses to habitat patchiness. Conserv Biol. 2006;20:1016-25.
    Wild Bird Society of Japan. A field guide to the birds of Japan. Tokyo: Kodansha International Limited; 1982.
    Yamashina Y. Birds in Japan: a field guide. Tokyo: Tokyo news Limited; 1961. p. 1961.
    Zhou D, Chu LM. How would size, age, human disturbance, and vegetation structure affect bird communities of urban parks in different seasons? J Ornithol. 2012;153:1101-12.
  • Related Articles

  • Cited by

    Periodical cited type(24)

    1. Rowe, M., Hooper, D.M., Hofgaard, A. et al. Independent evolution of atypical sperm morphology in a passerine bird. Journal of Evolutionary Biology, 2025, 38(10): 1373-1386. DOI:10.1093/jeb/voaf087
    2. McDiarmid, C.S., Hooper, D.M., Stier, A. et al. Mitonuclear interactions impact aerobic metabolism in hybrids and may explain mitonuclear discordance in young, naturally hybridizing bird lineages. Molecular Ecology, 2024, 33(12): e17374. DOI:10.1111/mec.17374
    3. Dubey, K., McDiarmid, C.S., Griffith, S.C. The impact of diet on sperm length in the long-tailed finch (Poephila acuticauda). Journal of Avian Biology, 2024, 2024(1-2): e03141. DOI:10.1111/jav.03141
    4. DeCicco, L.H., DeRaad, D.A., Ostrow, E.N. et al. A complete species-level phylogeny of the Erythrura parrotfinches (Aves: Estrildidae). Molecular Phylogenetics and Evolution, 2023. DOI:10.1016/j.ympev.2023.107883
    5. McDiarmid, C.S., Finch, F., Peso, M. et al. Experimentally testing mate preference in an avian system with unidirectional bill color introgression. Ecology and Evolution, 2023, 13(2): e9812. DOI:10.1002/ece3.9812
    6. McDiarmid, C.S., Hurley, L.L., Le Mesurier, M. et al. The impact of diet quality on the velocity, morphology and normality of sperm in the zebra finch Taeniopygia guttata. Journal of Experimental Biology, 2022, 255(9): jeb243715. DOI:10.1242/jeb.243715
    7. Mccarthy, E., Mcdiarmid, C.S., Hurley, L.L. et al. Highly variable sperm morphology in the masked finch (Poephila personata) and other estrildid finches. Biological Journal of the Linnean Society, 2021, 133(4): 1099-1109. DOI:10.1093/biolinnean/blab048
    8. Lopez, K.A., McDiarmid, C.S., Griffith, S.C. et al. Evaluating evidence of mitonuclear incompatibilities with the sex chromosomes in an avian hybrid zone. Evolution, 2021, 75(6): 1395-1414. DOI:10.1111/evo.14243
    9. McDiarmid, C.S., Li, R., Kahrl, A.F. et al. Sperm Sizer: a program to semi-automate the measurement of sperm length. Behavioral Ecology and Sociobiology, 2021, 75(5): 84. DOI:10.1007/s00265-021-03013-4
    10. Korneev, D., Merriner, D.J., Gervinskas, G. et al. New Insights Into Sperm Ultrastructure Through Enhanced Scanning Electron Microscopy. Frontiers in Cell and Developmental Biology, 2021. DOI:10.3389/fcell.2021.672592
    11. Hurley, L.L., Rowe, M., Griffith, S.C. Reproductive coordination breeds success: the importance of the partnership in avian sperm biology. Behavioral Ecology and Sociobiology, 2020, 74(1): 3. DOI:10.1007/s00265-019-2782-9
    12. Yang, Y., Zhang, Y., Ding, J. et al. Optimal analysis conditions for sperm motility parameters with a CASA system in a passerine bird, Passer montanus. Avian Research, 2019, 10(1): 35. DOI:10.1186/s40657-019-0174-5
    13. Støstad, H.N., Rowe, M., Johnsen, A. et al. Sperm head abnormalities are associated with excessive omega-6 fatty acids in two finch species feeding on sunflower seeds. Journal of Avian Biology, 2019, 50(3): e02056. DOI:10.1111/jav.02056
    14. Hooper, D.M., Griffith, S.C., Price, T.D. Sex chromosome inversions enforce reproductive isolation across an avian hybrid zone. Molecular Ecology, 2019, 28(6): 1246-1262. DOI:10.1111/mec.14874
    15. Hurley, L.L., Rowe, M., Griffith, S.C. Differential sperm-egg interactions in experimental pairings between two subspecies and their hybrids in a passerine bird. Ecology and Evolution, 2018, 8(23): 11725-11732. DOI:10.1002/ece3.4624
    16. Støstad, H.N., Johnsen, A., Lifjeld, J.T. et al. Sperm head morphology is associated with sperm swimming speed: A comparative study of songbirds using electron microscopy. Evolution, 2018, 72(9): 1918-1932. DOI:10.1111/evo.13555
    17. Hurley, L.L., McDiarmid, C.S., Friesen, C.R. et al. Experimental heatwaves negatively impact sperm quality in the zebra finch. Proceedings of the Royal Society B Biological Sciences, 2018, 285(1871): 20172547. DOI:10.1098/rspb.2017.2547
    18. Javanbakht, H., Vaissi, S. Intraspecific Variation in Ejaculate Traits of the Kuhl’s Pipistrelle Pipistrellus kuhlii (Kuhl, 1817) (Mammalia: Chiroptera: Vespertilionidae) in Iran. Acta Zoologica Bulgarica, 2018, 70(3): 359-365.
    19. Alund, M., Schmiterlöw, S.P., McFarlane, S.E. et al. Optimal sperm length for high siring success depends on forehead patch size in collared flycatchers. Behavioral Ecology, 2018, 29(6): 1436-1443. DOI:10.1093/beheco/ary115
    20. Skinner, B.M., Johnson, E.E.P. Nuclear morphologies: their diversity and functional relevance. Chromosoma, 2017, 126(2): 195-212. DOI:10.1007/s00412-016-0614-5
    21. Schilthuizen, M., Langelaan, R., Hemmings, N. et al. An unexpected twist: Sperm cells coil to the right in land snails and to the left in song birds. Contributions to Zoology, 2017, 86(4): 297-302. DOI:10.1163/18759866-08604003
    22. Støstad, H.N., Rekdal, S.L., Kleven, O. et al. Weak geographical structure in sperm morphology across the range of two willow warbler Phylloscopus trochilus subspecies in Scandinavia. Journal of Avian Biology, 2016, 47(5): 731-741. DOI:10.1111/jav.00981
    23. van Rooij, E.P., Rollins, L.A., Holleley, C.E. et al. Extra-pair paternity in the long-tailed finch Poephila acuticauda. Peerj, 2016, 2016(1): e1550. DOI:10.7717/peerj.1550
    24. Lifjeld, J.T., Anmarkrud, J.A., Calabuig, P. et al. Species-level divergences in multiple functional traits between the two endemic subspecies of Blue Chaffinches Fringilla teydea in Canary Islands. BMC Zoology, 2016, 1(1): 4. DOI:10.1186/s40850-016-0008-4

    Other cited types(0)

Catalog

    M. Isabel Bellocq

    1. On this Site
    2. On Google Scholar
    3. On PubMed

    Figures(5)  /  Tables(3)

    Article Metrics

    Article views (457) PDF downloads (26) Cited by(24)

    /

    DownLoad:  Full-Size Img  PowerPoint
    Return
    Return