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    Utilization of the zebrafish model to unravel the harmful effects of biomass burning during Amazonian wildfires

    In vivo study: embryotoxicity test
    Zebrafish embryos exposed to tested compounds developed lethal and sub-lethal alterations including different abnormalities and unhatching events. LC50 (for mortality rate) and EC50 (for abnormality and unhatching rate) values were extrapolated from concentration–response curves shown in Fig. 1. The rate of dead, abnormal, and/or unhatched specimens was concentration-dependent for all tested compounds (Fig. 1a–c). The lethality of the negative control group was less than 5%. Compounds 4NC and CAT showed the highest toxicity with LC50 values of 8.16 and 10.95 mg/L, respectively, followed by 4,6DNG  > 5NG  > GUA. Experimental LC50/EC50 values and the predicted ones obtained by ECOlogical Structure Activity Relationship (ECOSAR) v2.0 software (https://www.epa.gov/tsca-screening-tools/ecological-structure-activity-relationships-ecosar-predictive-model) based on Quantitative Structure Activity Relationships (QSAR) models showed 4NC and CAT as the most toxic chemicals (Table 2). However, it is important to notice that experimental values for both compounds were approximately two times lower than the predicted ones. This led to the classification of 4NC into the group of molecules toxic to fish (1  GUA).
    Figure 3

    Recorded sublethal morphological effects in D. rerio embryos/larvae after 48, 72, and 96 h of exposure to CAT, 4NC, GUA, 5NG, and 4,6DNG. Negative control: normally developed embryo at (a) 48, (b) 72, and (c) 96 hpf. During exposure period alterations were manifested as: (d) yolk sac edema (arrow); (e) pericardial edema (asterisk), undeveloped tail region (arrow); (f) hatched fish with malformed spine (arrow); (g) underdeveloped tail and necrosis of its apical part (dashed arrow), rare pigments; (h) pericardial edema (asterisk), scoliosis (arrow), necrosis of the apical part of the tail (dashed arrow), rare pigments, not hatched; (i) scoliosis (arrows), blood accumulation in the brain region (dashed arrow); (j) pericardial edema (asterisk), yolk sac edema (arrow), scoliosis (dashed arrow); (k, l) pericardial edema (asterisk); (m) underdeveloped embryo: underdeveloped head (arrow), tail not detached (asterisk), delay or anomaly in the absorption of the yolk sac; (n) pericardial edema (asterisk), blood accumulation (arrow), not hatched; (o) pericardial edema (asterisk), blood clotting (arrow), not hatched; (p) blood accumulation at the yolk sac (arrow); (r) hatched fish with malformed spine; (s) pericardial edema (black asterisk), blood accumulation above the yolk sac (arrow), swelling of the yolk sac (white asterisk), yolk sac edema (dashed arrow), mild scoliosis. Developmental abnormalities were recorded using LAS EZ 3.2.0 digitizing software (https://www.leica-microsystems.com/products/microscope-software/p/leica-las-ez/).

    Full size image

    The morphometric measurements (Fig. 4) showed that all tested samples significantly affected sensorial (eye area), skeletal (head height), and physiological (yolk and pericardial sac area) parameters in zebrafish. Significant differences among all treatments with exact p values are presented in Table S2.
    Figure 4

    Morphometric measurements of D. rerio larvae after 96-h exposure to tested compounds (CAT, 4NC, GUA, 5NG, and 4,6DNG) and control (C). (a) Lateral view showing eye area (EA), head height (HH), yolk sac area (YSA), and pericardial sac area (PSA). Scale bar = 1000 µm. Morphometric parameters are presented by their mean value (b–e; n = 15). The symbol * indicates a significant difference between tested samples and negative control (*p  More

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    Phenological shifts of abiotic events, producers and consumers across a continent

    Department of Ecology, Swedish University of Agricultural Sciences, Uppsala, Sweden
    Tomas Roslin

    University of Helsinki, Helsinki, Finland
    Tomas Roslin, Laura Antão, Maria Hällfors, Coong Lo, Juri Kurhinen & Otso Ovaskainen

    EarthCape OY, Helsinki, Finland
    Evgeniy Meyke

    Department of Computer Science, Aalto University, Espoo, Finland
    Gleb Tikhonov

    Research Unit of Biodiversity (UMIB, UO-CSIC-PA), Oviedo University, Mieres, Spain
    Maria del Mar Delgado

    3237 Biology-Psychology Building, University of Maryland, College Park, MD, USA
    Eliezer Gurarie

    National Park Orlovskoe Polesie, Oryol, Russian Federation
    Marina Abadonova

    Institute of Botany, Academy of Sciences of the Republic of Uzbekistan, Tashkent, Uzbekistan
    Ozodbek Abduraimov, Azizbek Mahmudov & Mirabdulla Turgunov

    Kostomuksha Nature Reserve, Kostomuksha, Russian Federation
    Olga Adrianova, Irina Gaydysh & Natalia Sikkila

    Altai State Nature Biosphere Reserve, Gorno-Altaysk, Russian Federation
    Tatiana Akimova, Svetlana Chuhontseva, Elena Gorbunova, Yury Kalinkin, Helen Korolyova, Oleg Mitrofanov, Miroslava Sahnevich, Vladimir Yakovlev & Tatyana Zubina

    Kabardino-Balkarski Nature Reserve, Kashkhatau, Russian Federation
    Muzhigit Akkiev

    FSE Zapovednoe Podlemorye, Ust-Bargizin, Russian Federation
    Aleksandr Ananin, Evgeniya Bukharova & Natalia Luzhkova

    Institute of General and Experimental Biology, Siberian Branch, Russian Academy of Sciences, Ulan-Ude, Russian Federation
    Aleksandr Ananin

    State Nature Reserve Stolby, Krasnoyarsk, Russian Federation
    Elena Andreeva, Nadezhda Goncharova, Alexander Hritankov, Anastasia Knorre, Vladimir Kozsheechkin & Vladislav Timoshkin

    Carpathian Biosphere Reserve, Rakhiv, Ukraine
    Natalia Andriychuk, Alla Kozurak & Anatoliy Vekliuk

    Nizhne-Svirsky State Nature Reserve, Lodeinoe Pole, Russian Federation
    Maxim Antipin

    State Nature Reserve Prisursky, Cheboksary, Russian Federation
    Konstantin Arzamascev

    Zapovednoe Pribajkalje (Bajkalo-Lensky State Nature Reserve, Pribajkalsky National Park), Irkutsk, Russian Federation
    Svetlana Babina

    Darwin Nature Biosphere Reserve, Borok, Russian Federation
    Miroslav Babushkin, Andrey Kuznetsov, Natalia Nemtseva, Irina Rybnikova & Nicolay Zelenetskiy

    Volzhsko-Kamsky National Nature Biosphere Rezerve, Sadovy, Russian Federation
    Oleg Bakin, Elena Chakhireva & Alexey Pavlov

    FGBU National Park Shushenskiy Bor, Shushenskoe, Russian Federation
    Anna Barabancova & Andrej Tolmachev

    Voronezhsky Nature Biosphere Reserve, Voronezh, Russian Federation
    Inna Basilskaja & Inna Sapelnikova

    Baikalsky State Nature Biosphere Reserve, Tankhoy, Russian Federation
    Nina Belova, Olga Ermakova, Irina Kozyr, Aleksandra Krasnopevtseva & Nikolay Volodchenkov

    Visimsky Nature Biosphere Reserve, Kirovgrad, Russian Federation
    Natalia Belyaeva & Rustam Sibgatullin

    Kondinskie Lakes National Park named after L. F. Stashkevich, Sovietsky, Russian Federation
    Tatjana Bespalova, Alena Butunina, Aleksandra Esengeldenova, Natalia Korotkikh & Evgeniy Larin

    FSBI United Administration of the Kedrovaya Pad’ State Biosphere Nature Reserve and Leopard’s Land National Park, Vladivostok, Russian Federation
    Evgeniya Bisikalova

    Pechoro-Ilych State Nature Reserve, Yaksha, Russian Federation
    Anatoly Bobretsov, Murad Kurbanbagamaev, Irina Megalinskaja, Viktor Teplov, Valentina Teplova & Tatiana Tertitsa

    A. N. Severtsov Institute of Ecology and Evolution, Moscow, Russian Federation
    Vladimir Bobrov & Igor Pospelov

    Komsomolskiy Department, FGBU Zapovednoye Priamurye, Komsomolsk-on-Amur, Russian Federation
    Vadim Bobrovskyi, Olga Kuberskaya, Polina Van & Vladimir Van

    Tigirek State Nature Reserve, Barnaul, Russian Federation
    Elena Bochkareva & Evgeniy A. Davydov

    Institute of Systematics and Ecology of Animals, Siberian Branch, Russian Academy of Sciences, Novosibirsk, Russian Federation
    Elena Bochkareva

    State Nature Reserve Bolshaya Kokshaga, Yoshkar-Ola, Russian Federation
    Gennady Bogdanov

    Institute of Plant and Animal Ecology, Ural Branch, Russian Academy of Sciences, Ekaterinburg, Russian Federation
    Vladimir Bolshakov

    Sikhote-Alin State Nature Biosphere Reserve named after K. G. Abramov, Terney, Russian Federation
    Svetlana Bondarchuk, Sergey Elsukov, Ludmila Gromyko, Irina Nesterova & Elena Smirnova

    FSBI Prioksko-Terrasniy State Reserve, Danky, Russian Federation
    Yuri Buyvolov & Galina Sokolova

    Lomonosov Moscow State University, Moscow, Russian Federation
    Anna Buyvolova & Ilya Prokhorov

    National Park Meshchera, Gus-Hrustalnyi, Russian Federation
    Yuri Bykov, Zoya Drozdova & Svetlana Mayorova

    South Urals Federal Research Center of Mineralogy and Geoecology, Ilmeny State Reserve, Ural Branch, Russian Academy of Sciences, Miass, Russian Federation
    Olga Chashchina, Nadezhda Kuyantseva & Valery Zakharov

    FGBU National Park Kenozersky, Arkhangelsk, Russian Federation
    Nadezhda Cherenkova, Svetlana Drovnina & Alexander Samoylov

    FGBU GPZ Kologrivskij les im. M.G. Sinicina, Kologriv, Russian Federation
    Sergej Chistjakov

    Altai State University, Barnaul, Russian Federation
    Evgeniy A. Davydov

    Pryazovskyi National Nature Park, Melitopol’, Ukraine
    Viktor Demchenko, Elena Diadicheva & Valeri Sanko

    State Nature Reserve Privolzhskaya Lesostep, Penza, Russian Federation
    Aleksandr Dobrolyubov & Aleksey Kudryavtsev

    Komarov Botanical Institute, Russian Academy of Sciences, Saint Petersburg, Russian Federation
    Ludmila Dostoyevskaya, Violetta Fedotova & Pavel Lebedev

    Sary-Chelek State Nature Reserve, Aksu, Kyrgyzstan
    Akynaly Dubanaev

    Institute for Evolutionary Ecology NAS Ukraine, Kiev, Ukraine
    Yuriy Dubrovsky

    FGBU State Nature Reserve Kuznetsk Alatau, Mezhdurechensk, Russian Federation
    Lidia Epova

    Kerzhenskiy State Nature Biosphere Reserve, Nizhny Novgorod, Russian Federation
    Olga S. Ermakova

    FSBI United Administration of the Mordovia State Nature Reserve and National Park Smolny, Republic of Mordovia, Saransk, Russian Federation
    Elena Ershkova

    Ogarev Mordovia State University, Saransk, Russian Federation
    Elena Ershkova

    Bryansk Forest Nature Reserve, Nerussa, Russian Federation
    Oleg Evstigneev, Evgeniya Kaygorodova, Sergey Kossenko, Sergey Kruglikov & Elena Sitnikova

    Pinezhsky State Nature Reserve, Pinega, Russian Federation
    Irina Fedchenko, Lyudmila Puchnina, Svetlana Rykova & Andrei Sivkov

    The Central Chernozem State Biosphere Nature Reserve named after Professor V.V. Alyokhin, Kurskiy, Russian Federation
    Tatiana Filatova

    Tyumen State University, Tyumen, Russian Federation
    Sergey Gashev

    Reserves of Taimyr, Norilsk, Russian Federation
    Anatoliy Gavrilov, Leonid Kolpashikov, Elena Pospelova & Violetta Strekalovskaya

    Chatkalski National Park, Toshkent, Uzbekistan
    Dmitrij Golovcov

    National Park Ugra, Kaluga, Russian Federation
    Tatyana Gordeeva & Viktorija Teleganova

    Kaniv Nature Reserve, Kaniv, Ukraine
    Vitaly Grishchenko, Yuliia Kulsha, Vasyl Shevchyk & Eugenia Yablonovska-Grishchenko

    Smolenskoe Poozerje National Park, Przhevalskoe, Russian Federation
    Vladimir Hohryakov, Gennadiy Kosenkov & Ksenia Shalaeva

    FSBI Zeya State Nature Reserve, Zeya, Russian Federation
    Elena Ignatenko, Klara Pavlova & Sergei Podolski

    Polistovsky State Nature Reserve, Pskov, Russian Federation
    Svetlana Igosheva & Tatiana Novikova

    Ural State Pedagogical University, Yekaterinburg, Russian Federation
    Uliya Ivanova, Margarita Kupriyanova, Tamara Nezdoliy, Nataliya Skok & Oksana Yantser

    Institute of Mathematical Problems of Biology RAS—the Branch of the Keldysh Institute of Applied Mathematics, Russian Academy of Sciences, Pushchino, Russian Federation
    Natalya Ivanova & Maksim Shashkov

    Kronotsky Federal Nature Biosphere Reserve, Yelizovo, Russian Federation
    Fedor Kazansky & Darya Panicheva

    Zhiguli Nature Reserve, P. Bakhilova Polyana, Russian Federation
    Darya Kiseleva

    Institute for Ecology and Geography, Siberian Federal University, Krasnoyarsk, Russian Federation
    Anastasia Knorre

    Central Forest State Nature Biosphere Reserve, Tver, Russian Federation
    Evgenii Korobov, Elena Shujskaja, Sergei Stepanov & Anatolii Zheltukhin

    National Park Bashkirija, Nurgush, Russian Federation
    Elvira Kotlugalyamova & Lilija Sultangareeva

    State Nature Reserve Kurilsky, Juzhno-Kurilsk, Russian Federation
    Evgeny Kozlovsky

    Vodlozersky National Park, Karelia, Petrozavodsk, Russian Federation
    Elena Kulebyakina & Viktor Mamontov

    State Nature Reserve Kivach, Kondopoga, Russian Federation
    Anatoliy Kutenkov, Nadezhda Kutenkova, Anatoliy Shcherbakov, Svetlana Skorokhodova, Alexander Sukhov & Marina Yakovleva

    South-Ural Federal University, Miass, Russian Federation
    Nadezhda Kuyantseva

    Saint-Petersburg State Forest Technical University, St. Petersburg, Russian Federation
    Pavel Lebedev

    Astrakhan Biosphere Reserve, Astrakhan, Russian Federation
    Kirill Litvinov

    FSBI United Administration of the Lazovsky State Reserve and National Park Zov Tigra, Lazo, Russian Federation
    Lidiya Makovkina, Aleksandr Myslenkov & Inna Voloshina

    State Nature Reserve Tungusskiy, Krasnoyarsk, Russian Federation
    Artur Meydus, Julia Raiskaya & Vladimir Sopin

    Krasnoyarsk State Pedagogical University named after V.P. Astafyev, Krasnoyarsk, Russian Federation
    Artur Meydus

    Institute of Geography, Russian Academy of Sciences, Moscow, Russian Federation
    Aleksandr Minin

    Koltzov Institute of Developmental Biology, Russian Academy of Sciences, Moscow, Russian Federation
    Aleksandr Minin

    Carpathian National Nature Park, Yaremche, Ukraine
    Mykhailo Motruk

    State Environmental Institution National Park Braslav lakes, Braslav, Belarus
    Nina Nasonova

    National Park Synevyr, Synevyr-Ostriki, Ukraine
    Tatyana Niroda, Ivan Putrashyk, Yurij Tyukh & Yurij Yarema

    Pasvik State Nature Reserve, Nikel, Russian Federation
    Natalja Polikarpova

    Mari Chodra National Park, Krasnogorsky, Russian Federation
    Tatiana Polyanskaya

    State Nature Reserve Vishersky, Krasnovishersk, Russian Federation
    Irina Prokosheva

    State Nature Reserve Olekminsky, Olekminsk, Russian Federation
    Yuri Rozhkov, Olga Rozhkova & Dmitry Tirski

    Crimea Nature Reserve, Alushta, Republic of Crimea
    Marina Rudenko

    Forest Research Institute Karelian Research Centre, Russian Academy of Sciences, Petrozavodsk, Russian Federation
    Sergei Sazonov, Lidia Vetchinnikova & Juri Kurhinen

    Black Sea Biosphere Reserve, Hola Prystan’, Ukraine
    Zoya Selyunina

    Institute of Physicochemical and Biological Problems in Soil Sciences, Russian Academy of Sciences, Pushchino, Russian Federation
    Maksim Shashkov

    State Nature Reserve Nurgush, Kirov, Russian Federation
    Sergej Shubin & Ludmila Tselishcheva

    Caucasian State Biosphere Reserve of the Ministry of Natural Resources, Maykop, Russian Federation
    Yurii Spasovski

    National Nature Park Vyzhnytskiy, Berehomet, Ukraine
    Vitalіy Stratiy

    National Park Khvalynsky, Khvalynsk, Russian Federation
    Guzalya Suleymanova

    State Research Center Arctic and Antarctic Research Institute, Saint Petersburg, Russian Federation
    Aleksey Tomilin

    Information-Analytical Centre for Protected Areas, Moscow, Russian Federation
    Aleksey Tomilin

    State Nature Reserve Malaya Sosva, Sovetskiy, Russian Federation
    Aleksander Vasin & Aleksandra Vasina

    Krasnoyarsk State Medical University named after Prof. V.F.Voino-Yasenetsky, Krasnoyarsk, Russian Federation
    Vladislav Vinogradov

    Surhanskiy State Nature Reserve, Sherabad, Uzbekistan
    Tura Xoliqov

    Mordovia State Nature Reserve, Pushta, Russian Federation
    Andrey Zahvatov

    Centre for Biodiversity Dynamics, Department of Biology, Norwegian University of Science and Technology, Trondheim, Norway
    Otso Ovaskainen

    The data were collected by the 195 authors starting from M.A. and ending with T.Z. in the author list. J.K., E.M., C.L., G.T. and E.G. contributed to the establishment and coordination of the collaborative network and to the compilation and curation of the resulting dataset. T.R., O.O., L.A., M.H. and M.d.M.D. conceived the idea behind the current study and wrote the first draft of the paper, with O.O. conducting the analyses. All authors provided useful comments on earlier drafts. More

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    Geometric morphometric investigation of craniofacial morphological change in domesticated silver foxes

    Samples
    We sampled 73 adult fox skulls (Vulpes vulpes) from three separate sample groups: wild (8 F, 12 M), unselected (15 F, 8 M), and domesticated (15 F, 15 M). Domesticated and unselected skulls from the RFF experiment were generously provided by Dr. Trut and transported to Harvard in 2004. Unfortunately, we do not know how these foxes were chosen, but have no reason not to assume that they were selected randomly from both populations. Wild fox skulls in the study were sampled from the collections of the Museum of Comparative Zoology, Harvard University. All but two wild foxes were trapped in Canada east of Quebec between 1894 and 1952, with the majority (70%) between 1894 and 1900 (Table S1). We excluded from the study sample all juvenile skulls, as determined through lower third molar eruption and fusion of the cranial suture between the basioccipital and basisphenoid16, and those skulls that had evidence of damage or disease. After applying these exclusion criteria, we arrived at our final sample of 73 skulls.
    3D landmarks
    To prevent movement during measurement, each skull was embedded in styrofoam and secured to the workspace desk before 3D coordinates of 29 landmarks, listed, defined and displayed in Table S2 and Fig S1, were collected on the left half of each skull by a single analyst (TMK). Of these 29 landmarks, 17% are on the cranial base, 27% are on the neurocranium, and 55% are on the face. 3D landmark coordinates were measured with a Microscribe G2 (Positional Accuracy ± 0.38 mm, Revware, Inc.). This machine consists of a mobile robotic arm tipped with a probe. After calibration, the probe tip is placed on each landmark to record its XYZ coordinates. To avoid having to move the skulls during measuring and to limit the number of variables in our final GM analysis (too high a number may be a problem given our small sample size), we restricted landmark measurements to one half of each skull. We assume that the fluctuating asymmetry between each fox population is negligible and stable as has previously been shown in comparisons across a domestic-wild hybridization zone in mice17. In most cases, landmark positions were lightly marked with pencil to ensure proper probe placement.
    Linear and endocranial volume measurements
    Six linear measurements were taken on each skull using digital calipers (Fowler High Precision, Positional Accuracy ± 0.03 mm): total skull length, snout length, cranial vault height, cranial vault width, bi-zygomatic width and upper jaw width (Fig. 1). Endocranial volume was measured using plastic beads. Each cranium was filled up to the level of the foramen magnum and repeatedly shaken and tamped down until no more beads could be added. The beads were then funneled into a graduated cylinder to obtain a volumetric measurement.
    Figure 1

    Schematic diagram of the six linear measurements taken on the fox skulls. 1: Bi-zygomatic width. 2: Cranial vault width. 3: Upper jaw width. 4: Total skull length. 5: Snout length. 6: Cranial vault height.

    Full size image

    Geometric morphometrics
    Generalized Procrustes analysis was conducted in R v. 4.0.218 using the geomorph v. 3.3.1 package19. Landmark configurations from each specimen were translated to the origin, rescaled to centroid size, and optimally rotated (using a least-squares criterion) until the coordinates of homologous landmarks aligned as closely as possible. These steps place all specimens in the same shape space, centered on the mean shape. An orthogonal projection into a linear tangent space was applied so statistical analyses could be performed on the resulting tangent space coordinates. For Procrustes superimposition, we used the default parameters of the gpagen function in geomorph.
    Repeatability analyses
    Landmark measurement repeatability was evaluated through repeated measurements of three fox skulls (domesticated male ID# TM23, domesticated female ID# TF476, unselected female ID# UF1058) on ten separate occasions. In this case, repeatability encompasses both Microscribe and operator error. Generalized Procrustes Analysis (GPA) was used on these landmark coordinates to ensure that they were in the same 3D location relative to one another. The average Procrustes distance (PD) between all ten iterations of the same specimen was then compared to the average Procrustes distance within the population-sex grouping to which the skull belonged. To do this, we calculated a sensitivity ratio based on the formula: (Mean Inter-specimen PD – Mean Intra-specimen PD)/Mean Intra-specimen PD. This created a sensitivity ratio that reflects how sensitive the Microscribe measurements are with respect to the average difference among foxes of the same population-sex category. Averaging the sensitivity ratios for our three skulls, we find that the difference between replicates is roughly 3.7 times smaller than the differences within population-sex groupings. This indicates that the Microscribe G2 is robust enough to detect subtle individual differences in measured landmark coordinates. Linear and endocranial measurement repeatability was quantified through a similar method where repeat measurements were taken on 3 domesticated female fox skulls on 15 separate occasions. Sensitivity ratios were deteremined for each measurement (i.e. total skull length, snout length etc.) by calculating the standard deviation of each repeated measurement on a single specimen, averaging the three specimens’ standard deviations for that measurement, and then comparing that value to the population (domesticated female) standard deviation for that measurement. With the exception of cranial vault height (see limitations), the replicate standard deviations of each measurement were roughly a third (or less) of the population standard deviations (Table S3).
    Statistical analyses
    All statistical analyses were performed in R18. For all parametric inferences, we report point and interval (95% confidence) estimates of effect sizes, while for permutation-based inferences we report point estimates and p-values. All p-values involving multiple comparisons were adjusted for family-wise error using the sequential Bonferroni method.
    3D shape comparisons
    To test hypotheses about shape differences among the three populations of foxes, we used a permutation-based Procrustes MANOVA to regress tangent space coordinates on population identity and sex in the geomorph v. 3.3.1 package. Because we are unable to detect significant differences in allometry among populations with a permutation-based Procrustes MANOVA of tangent space coordinates on the interaction term of population identity and centroid size, the tangent space coordinates were not corrected for any scaling effects (see Supplemental information and Fig S2). Given this result, we control only for isometric size in geometric morphometric analyses (i.e. no correction for scaling in tangent space coordinates) as well as in our linear measurements. To determine how skull shape differed between fox populations, we performed pairwise comparisons of shape using Procrustes distances. We additionally performed pairwise comparisons between groups of the shape variance within a group (as assessed by the dispersion of residuals around the mean shape for a given population)20. All pairwise comparisons were made using the RRPP v. 0.6.1 package21,22. Permutation-based p-values for the pairwise comparisons were corrected for family-wise error using the sequential Bonferroni method. To visualize changes in skull shape between populations, a principal components analysis (PCA) was performed on the tangent space coordinates. Skull warp changes along the first principal component were graphed to visualize shape changes along this axis. Size differences between populations were assessed via a linear model using a weighted least squares (WLS) estimator, where centroid size was regressed on population identity and sex. The WLS estimator allowed for separate residual variances for each combination of population and sex, so that heteroskedasticity across these groups could be accounted for in the model. Variance in centroid size was assessed with a Levene’s test based on absolute deviations from the median and was performed using the car package v. 3.0-1023.
    Linear and endocranial volume comparisons
    Prior to modeling linear and volumetric data, we created size-adjusted versions of our variables to account for a difference in isometric size between wild and RFF populations. Normalizing to size allows us to parse out the effects of size selection from those of selection for docility as they likely have overlapping effects on craniofacial shape. We adjusted for size by normalizing each linear measurement and the cube root of endocranial volume by centroid size. We used centroid size rather than the geometric mean of the six linear measurements because centroid size was calculated using a larger sample of craniometric landmarks and is therefore the better proxy of overall cranial size. We performed size corrections on the raw measurements instead of including a size variable in the models because it allows the size-correction to be intrinsic to each fox rather than depending on the size of every fox in the model.
    To determine if there were population-level differences in size-corrected linear and volumetric variables, we used a linear model with a generalized least squares (GLS) estimator from the nlme v. 3.1-150 package24 to regress all 7 skull variables simultaneously as correlated responses on population identity and sex (see Supplementary Methods for details of estimation strategy and model specification and Figs. S3, S4). We report estimates of pairwise percent differences between population means for each skull variable. We use this method because the 7 linear and volumetric skull variables were correlated in two ways (see Fig. S3). First, they were measured on the same specimens, and second, they represent non-independent aspects of shape variation. Modeling these response variables in 7 separate general linear models (e.g., ANOVA) would result in biologically unrealistic inferences because these correlations would be artificially fixed at zero. In addition, since skull variables exhibited varying amounts of dispersion, the GLS model allowed for different residual variances for each response variable.
    Sexual dimorphism comparisons
    Sexual dimorphism within a species is often represented as dimorphism in size as well as shape25. Therefore, in contrast to the previous analyses, we assess the degree of sexual dimorphism in both size and shape. We used a similar GLS model to determine the degree of sexual dimorphism of the raw (non-size corrected) variables within each population. To estimate sex-specific effects, we added an additional interaction term between sex and population identity in this model. We report the degree of dimorphism using estimates of mean differences between males and females for a given skull variable, within a population. For both models using linear and volumetric data, we performed model selection for variance components and correlation structures using the Bayesian information criterion, since this has been shown to provide a good balance between parsimony and over-fitting for explanatory models26. Linear model (GLS) assumptions were checked using diagnostic plots of standardized residuals and fitted values (see Fig. S5). More

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