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Native European crayfish Astacus astacus competitive in staged confrontation with the invasive crayfish Faxonius limosus and Procambarus acutus

  • Ivo Roessink ,

    Roles Conceptualization, Investigation, Writing – review & editing

    ivo.roessink@wur.nl

    Affiliation Environmental Risk Assessment, Wageningen Environmental Research, Wageningen, The Netherlands

  • Karina A. E. van der Zon,

    Roles Formal analysis, Writing – original draft

    Affiliations Aquatic Ecology and Water Quality Management, Wageningen University and Research, Wageningen, The Netherlands, Department of Zoology, University of Otago, Dunedin, New Zealand

  • Sophie R. M. M. de Reus,

    Roles Investigation

    Affiliations Aquatic Ecology and Water Quality Management, Wageningen University and Research, Wageningen, The Netherlands, Advisory Group Ecology, Royal HaskoningDHV, Amersfoort, The Netherlands

  • Edwin T. H. M. Peeters

    Roles Conceptualization, Formal analysis, Writing – review & editing

    Affiliation Aquatic Ecology and Water Quality Management, Wageningen University and Research, Wageningen, The Netherlands

Abstract

The European native, noble crayfish (Astacus astacus) has suffered from a serious and long term population decline due to habitat destruction, water pollution and the impact of the invasive North American crayfish that are carriers of the crayfish plague (Aphanomyces astaci). The latter being the major factor currently confining noble crayfish to uninvaded (parts of) waterbodies. However, recently wild populations of apparently healthy noble crayfish carrying the crayfish plague have been found. As crayfish are known for their inter- and intraspecific agonistic behaviour which may be key for their competitive success, this raised the interesting question what would happen if the crayfish plague would not be a dominant factor anymore in the interaction between native and invasive species. Since the outcome of those encounters is still unclear, this study explores whether the noble crayfish can stand its ground towards invasive species in such agonistic interactions. Furthermore, the ability of the noble crayfish and invasive crayfish to acquire shelter through agonistic interaction is also assessed. Through pairwise staged interactions, agonistic behaviour and shelter competition between the native A. astacus and the invasive Faxonius limosus and Procambarus acutus were examined. The results showed that A. astacus triumphs over F. limosus and P. acutus in agonistic encounters and in competition for shelter. In turn, P. acutus dominates F. limosus in staged encounters and shelter. In possible future situations were crayfish plague does no longer eradicate noble crayfish populations, our results show that the native noble crayfish might still have a promising future when confronted with invasive species.

Introduction

Invasive species are one of the most dangerous threats to biodiversity worldwide [1], especially in freshwater ecosystems. Among the most successful freshwater ecosystem invaders are crayfish [2] and through direct competition and as vectors of disease they can displace native crayfish, leading to population declines and local extinctions [3]. From approximately 1860 onwards, outbreaks of the crayfish plague have had a devastating effect on native crayfish populations in Europe [4]. The crayfish plague is caused by the oomycete Aphanomyces astaci (Schikora, 1903) that entered Europe through the introduction of North American crayfish [57]. While North American crayfish can live in a balanced host-parasite relationship with this A. astaci, the parasite is acutely pathogenic to European species [4, 8].

Europe’s most common and economically most valuable indigenous crayfish species, the noble crayfish (Astacus astacus (Linnaeus, 1758)) has suffered from a serious and long term population decline due to habitat destruction and water pollution in combination with the crayfish plague [9]. The recent observations of apparently healthy noble crayfish carrying A. astaci [1012] are therefore very remarkable. Several explanations for these findings have been suggested, including the possibilities that the As-genotype of the pathogen is becoming less virulent [10, 12], that less virulent strains of the pathogen are becoming more common [10] and that the resistance of A. astacus against the pathogen, or at least against the As-genotype of the pathogen, is increasing [11].

Whatever the reason, these findings trigger the interesting question: what would happen in the event that the crayfish plague presence or absence would not be the determining factor for native crayfish occurrence anymore? Would in that case, agonistic interactions and competition for shelter become more important determinants of competitiveness of A. astacus against invasive species? Agonistic, fighting related, behaviours are stereotyped [13] and largely conserved among crayfish species [14]. However, levels of aggression and outcomes of interspecific agonistic interactions differ among species [15], which can influence the outcome of interspecific competition [2]. This is partly because agonistic interactions influence a species ability to hold key resources such as shelters [16], which are critical for crayfish survival, providing protection against predators and refuge during vulnerable life stages and times of environmental stress [17].

At present, there are at least 10 non-indigenous crayfish species that A. astacus could encounter in Europe [3, 18]. One of the most successful invasive crayfish species in Europe is the North American signal crayfish Pacifastacus leniusculus (Dana, 1991; [16]). Although at the time of experimenting the species was difficult to obtain in the Netherlands, previous research by Söderbäck [16] has shown already that it dominates over A. astacus in agonistic interaction. As a result, there was no need to include it in our experiments. In contrast, agonistic interactions between A. astacus and the other 9 non-indigenous crayfish species have not been studied yet, nor has competition for shelter between A. astacus and non-indigenous crayfish. In order to fill part of this knowledge-gap we tested agonistic encounters and shelter occupancy using the native noble crayfish (A. astacus) and the invasive spiny-cheek crayfish (Faxonius limosus (Rafinesque, 1817), formerly Orconectes limosus) and white river crayfish (Procambarus acutus (Girard, 1852)), two invasive crayfish species readily available in The Netherlands [18].

Faxonius limosus was the first non-indigenous crayfish species to be introduced in Europe in 1890 [3] and has since established itself in 22 European countries [18]. Faxonius limosus is a well-studied vector of the crayfish plague [19]. A recent addition to the European crayfish fauna is the North American white river crayfish (Procambarus acutus (Girard, 1852)). In 2005, the first established population of P. acutus was recorded in the Netherlands and in 2012 an established population was also documented in the United Kingdom [18].

In the laboratory, paired species experiments were performed to compare outcomes of interspecific agonistic encounters [1618, 2025] and the ability of competing species to obtain shelter [16, 19, 20, 22]. We hypothesise that F. limosus will be less successful than the other two species in agonistic interactions and competition for shelter because F. limosus is known to be low in aggression [26, 27]. Aggressive behaviour is common in both A. astacus [16] and P. acutus [20] but there is no literature available on dominance in agonistic behaviour and competition for shelter between the two species. Therefore, we hypothesise that both species have equal changes in aggressive encounters and competition for shelter.

Materials and methods

Astacus astacus were obtained from a breeder in Germany (Harald Groβ, location Bad Münstereifel-Schönau; batch FZ2015/10) while F. limosus and P. acutus were wild-caught by a Dutch commercial fisherman (Blokland B.V., location Hardinxveld-Giessendam; batch 2015.0609.1&2015.1209.1). Crayfish were kept under controlled conditions (water temperature 21 ± 1°C, 8:16 h L:D regime, fluorescent light, pH 7.8–8.1) and were fed 2 to 4 Trouvit™ fish food pellets twice a week. Each individual stayed in a (10 L x 38 W x 38 H cm) section of an aquarium that was separated by perforated plastic dividers. The health status of the crayfish was daily checked. All crayfish used in the experiment were in intermoult stage, had fully intact appendages and showed no abnormal behaviour.

General set-up experiment

In September and October 2015 experiments were performed in (50 L x 30 W x 30 H cm) glass aquaria with 1 cm of gravel and 15 cm of water that stood in a water bath. Interaction pairs of crayfish of the same gender and similar body size were selected in three species combinations:

  1. A. astacus and F. limosus, 5 male and 5 female pairs
  2. A. astacus and P. acutus, 9 male and 6 female pairs
  3. F. limosus and P. acutus, 12 male and 6 female pairs

Differences in carapace length between the interaction pairs (Fig 1 and S1 Table) were mostly small except for pairs of A. astacus and P. acutus. Five out of nine A. astacus and P. acutus males had similar carapace lengths (< 3 mm difference) but carapaces of the A. astacus females were always > 9 mm longer than those of their P. acutus opponents. The difference in carapace length between female F. limosus and their P. acutus opponents was significant according to the two sided Wilcoxon signed rank test but always < 1.2 mm (Fig 1).

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Fig 1. The difference in carapace length between the two interacting crayfish.

The difference is positive when the specimen of the species named first in the legend is larger than the specimen of the species named second and negative when it is the other way around. Each data point indicates one interacting pair and the symbols are vertically aligned according to gender and species combination. Outcomes of two-sided Wilcoxon signed rank tests are indicated below the corresponding gender and species combination and the average carapace lengths of the trialled animals are indicated above the data points.

https://doi.org/10.1371/journal.pone.0263133.g001

To minimize the chance of crayfish plague infection, experiments with F. limosus and P. acutus were performed first and thereafter those with A. astacus. Astacus astacus were kept separate from the other crayfish in a different isolated tank with a separate water circulation system. Different sets of equipment were used for A. astacus and for the other species and experimental aquaria were disinfected with Virkon S™ between trials. Also to avoid infection, individuals of A. astacus were only used once and were not returned to the holding tanks after the trial. Some F. limosus and P. acutus individuals, however, were used in a second trial that took place two or three weeks after the first. This period is long enough to not affect the behaviour of the crayfish in a second trial [25].

The interactions were examined in a two-staged experiment. In the first stage, agonistic behaviour between the two interacting individuals was observed for one hour. Over the following night, shelter occupancy was examined with the same two individuals in the same aquarium.

Before an experiment started, a plastic divider was placed in the middle of the aquarium and the two individuals of each pair were placed on opposite sides of the divider to acclimatise for 10 minutes. The divider was removed after the acclimatisation period and agonistic interactions between the two crayfish were observed by a single observer for 60 minutes. The following events were recorded:

  1. First attacks: the number of fights started per individual with a fight defined as a crayfish using claws trying to touch or grab the opponent [28, 29].
  2. Wins: number of times a crayfish stands its ground and forces the opponent to stop moving or retreat.
  3. Retreats: number of times a crayfish moves away from the opponent for a distance equal to or larger than its body length [28]

After the 60 minute observation period, the crayfish were separated by replacing the divider between them in the middle of the aquarium. At around 5 pm, the divider was removed again and a (15 L x 10 W x 5 H cm) PVC tube was placed in the middle of the aquarium as a shelter. The next morning it was observed which of the two crayfish had occupied the shelter.

As a control, the shelter occupancy test was performed with single crayfish in the aquarium to ascertain that the crayfish desired to occupy the shelter [14]. This control was performed with 7 F. limosus males, 6 F. limosus females, 5 P. acutus males and 5 P. acutus females. Due to risk of contamination with the crayfish plague this control was not performed with A. astacus.

Data analysis

Generalized Linear Model (GLM) analysis was performed to test whether gender was a significant variable explaining the number of agonistic interactions per pair. Gender, species identity and the interaction between gender and species were used as independent variables and an intercept was calculated for each gender. Furthermore, a quasipoisson model with a logarithmic link function was chosen because the count data was overdispersed.

Each species’ average number of first attacks, wins and retreats per trial was calculated for males and females separately based on the data in S1 Table. Because no obvious differences in behavioural patterns between the genders of the same species were observed, statistical analyses of interspecific outcomes were performed for combined male and female data. Two-tailed Wilcoxon signed rank tests were used to test for significant differences in the number of first attacks, wins and retreats between the interacting species. Pearson chi-square tests were performed to evaluate whether differences between expected and observed frequencies of shelter occupancy were significant. Expected frequencies were calculated based on the assumption that both species would occupy the shelter equally often. Statistical analyses were performed in R 3.6.3 using RStudio version 1.2.5042 [30].

Results

Agonistic interactions

In general, fewer agonistic interactions took place in female pairs than in male pairs (Fig 2) and patterns in agonistic behaviour between paired species did not seem to differ for male and female pairs. For the total number of agonistic interactions gender was significant (GLM p ≤ 0.002, S3 Table). In male A. astacus and P. acutus pairs, there was a higher number of first attacks than in male A. astacus and F. limosus pairs, mostly due to a higher number of first attacks by A. astacus in the presence of P. acutus than in the presence of F. limosus. Female A. astacus also started more fights than F. limosus and P. acutus but there were not more first attacks by female A. astacus in presence of P. acutus than in presence of F. limosus.

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Fig 2.

Average number of first attacks, wins and retreats per trial with a) A. astacus vs. F. limosus, b) A. astacus vs. P. acutus and c) F. limosus vs. P. acutus by males and females.

https://doi.org/10.1371/journal.pone.0263133.g002

For the A. astacus vs. F. limosus pairs, there were more first attacks (two-tailed Wilcoxon signed rank test, W = 44, n = 9, p = 0.01), more wins (W = 28, n = 7, p = 0.02) and less retreats (W = 1.5, n = 9, p = 0.02) by A. astacus than by F. limosus. In the A. astacus vs. P. acutus pairs, A. astacus performed more first attacks (W = 108, n = 15, p = 0.007), won more fights (W = 91, n = 13, p = 0.002) and retreated less (W = 7, n = 13, p = 0.003) than P. acutus. Lastly, in the F. limosus vs. P. acutus pairs there were more fist attacks (W = 13.5, n = 16, p = 0.005) and wins (W = 21, n = 14, p = 0.05) by P. acutus than by F. limosus, but the difference in retreats was not significant (W = 123, n = 18, p = 0.1).

Shelter competition

In the single animal shelter occupancy controls F. limosus males and females were found in the shelter in all trials. Also P. acutus females occupied the shelter in all trials. Only the P. acutus males were found outside of the shelter in 4 of the 7 trials (S2 Table).

The shelter in the competition experiment was always occupied in the trials with A. astacus and F. limosus pairs but was sometimes found empty in the trials where P. acutus participated (Fig 3). Astacus astacus occupied the shelter more often (Chi-square test, χ2 = 12.8, df = 1, p < 0.001) than F. limosus and more often than P. acutus2 = 5, df = 1, p = 0.03). There was no significant difference in shelter occupancy between F. limosus and P. acutus2 = 1.9, df = 1, p = 0.2).

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Fig 3. Shelter occupancy by the interacting species in percentages for males and females.

Numbers of trialled male and female pairs of each species combination are indicated above the bars.

https://doi.org/10.1371/journal.pone.0263133.g003

Discussion

Outcomes of the paired species experiments

The results show that of the three species A. astacus was the most aggressive and most successful in fight and shelter acquisition. Procambarus acutus was the next most aggressive and successful in agonistic interactions and F. limosus the least. There was a larger number of agonistic interactions between male pairs than between female pairs, which is in accordance with the general notion that male crayfish are more aggressive than female crayfish [31].

Body size has a major influence on crayfish dominance [32] and the difference in carapace length between A. astacus and their P. acutus opponents could have influenced the outcome of the experiment. However, when inspecting only the five A. astacus vs. P. acutus pairs that had a difference in carapace length that is <10% of the average carapace length of the two opponents, the same pattern arose as when considering all A. astacus vs. P. acutus pairs with A. astacus starting and winning more fights and retreating less than P. acutus. Interestingly, there was one A. astacus that was shorter than its opponent but still dominated the encounters.

The shelter occupancy control experiment showed that F. limosus males and females and P. acutus females preferred to be in the shelter and although the control was not performed with A. astacus, it is clear from the outcomes of the paired species shelter occupancy experiment that A. astacus males and females stayed in the shelter as well. It is interesting to notice that the shelter in the trials with P. acutus was sometimes not occupied by either of the competitors. This might be because the animals were still fighting over the shelter at the time the occupancy was assessed. Unfortunately no video recordings of the experiment were made, so an additional check couldn’t be made. An alternative explanation for the unoccupied shelters could be that the dominant crayfish prevented the subordinate one from using it as was also observed by Gherardi and Daniels [20] in a shelter occupancy experiment where the dominant Procambarus clarkii did not use the shelter after evicting subordinate P. acutus acutus from it.

Relevance for crayfish populations in Europe

Remarkable changes in the host-parasite relationship between A. astaci and the native European crayfish species Astacus leptodactylus [31], Austropotamobius torrentium [32] and Austropotamobius pallipes [33] have recently been reported. A. astaci used to have a devastating effect on these species, but lately populations of these three species carrying A. astaci as a subclinical infection and showing melanized spots have been found. It is not inconceivable that in the long-term similar changes may occur in the host-parasite relationship between A. astacus and A. astaci.

Outside of the laboratory, differences in body sizes between species probably do matter for the outcome of interspecific agonistic encounters because A. astacus males, for example, can grow to a length of 180 mm and females can reach 150 mm while F. limosus, on the other hand, has a maximum length of 61 mm. Furthermore, specimens of P. acutus rarely grow longer than 140 mm [34]. However, the maximum length that a species can achieve is not the sole determinant of the size structure of a crayfish population. Juveniles of F. limosus grow much faster than juvenile A. astacus [30] giving them a competitive advantage at young age. Such an advantage is even bigger for P. acutus because this species has an even higher growth rate than F. limosus [35]. How these differences in juvenile development affect agonistic interactions between A. astacus and invasive crayfish remains unclear and can be studied in experiments in which juveniles are reared together [30].

Furthermore, other traits besides agonistic dominance could contribute to the competitive success of a crayfish species over another. For example, the higher growth rate, higher egg production per capita, the lower age and smaller size at which P. leniusculus reaches sexual maturity were all important for the displacement of A. astacus by the more aggressive P. leniusculus in Swedish [36] and Finnish [37] lakes. Bearing this in mind, it is highly recommended to include P. clarkii (Girard, 1852) in further research on interspecific agonistic interactions between A. astacus and invasive species because P. clarkii is known to be aggressive [26], and is widespread in Europe and increasing its numbers [3]. Van Kuijk et al. [35] compared traits of successful and unsuccessful invasive crayfish in the Netherlands and found that temperature tolerances, egg counts, and numbers of clutches per year contributed to invasion successes. However, these researchers stressed that there are different routes to success [35]. For example, although F. limosus scores low on agonistic behaviour it is a highly successful invader [3] due toits parthenogenetic reproduction [3], fast population growth [30], and indifference to land use change [38].

In conclusion, several traits and combinations of mechanisms may explain the success of invasive crayfish and interspecific agonistic interaction and competition for shelter are relevant. While invasive crayfish continue to threaten European waterways [3] and the crayfish plague still has disastrous effects on A. astacus [12], recent observations [3133] indicate the possibility that as other native crayfish are doing, in time the noble crayfish might also coexist with A. astaci. As a result, this justifies research on behavioural interactions between the noble crayfish and sympatric invasive crayfish species. In the wild, a lot of different factors determine the success of crayfish populations [35]. Of course, it remains to be seen whether the investigated endpoints in this study, e.g., winning direct interactions or the competition for shelter, are indeed key drivers. Once crayfish plague is no longer a decisive factor, long-term research on populations of invasive and native crayfish kept under controlled outdoor conditions could provide explanations to those specific questions. Nevertheless, the present study has clearly shown that in absence of the crayfish plague, the noble crayfish can at least behaviourally resist aggressive advances of two invasive species, F. limosus and P. acutus.

Supporting information

S1 Table. Agonistic interactions.

Number of "First Attacks", "Wins" and "Retreats" observed for each trialed crayfish.

https://doi.org/10.1371/journal.pone.0263133.s001

(PDF)

S2 Table. Shelter occupancy.

Frequencies of shelter occupancy for male and female species pairs.

https://doi.org/10.1371/journal.pone.0263133.s002

(PDF)

S3 Table. Summary GLM agonistic interactions.

Coefficients, standard errors, t-statistics and p-values of three quasipoisson distributed log linked Generalized Linear Models (GLMs) without intercept based on 43 observations for the dependent variables "First Attacks", "Wins" and "Retreats".

https://doi.org/10.1371/journal.pone.0263133.s003

(PDF)

Acknowledgments

The authors thank Lars Bakermans and Marie-Claire Boerwinkel for their assistance with conducting the experiments and Marc Schallenberg for proofreading. Also, the feedback from 3 reviewers is highly appreciated.

References

  1. 1. Clout MN, Williams PA, editors. Invasive Species Management: A Handbook of Principles and Techniques. Oxford: Oxford University Press; 2009.
  2. 2. Hudina S, Hock K, Radović A, Klobučar G, Petković J, Jelić M, et al. Species-specific differences in dynamics of agonistic interactions may contribute to the competitive advantage of the invasive signal crayfish (Pacifastacus leniusculus) over the native narrow-clawed crayfish (Astacus leptodactylus). Mar Freshw Behav Physiol. 2016;49(3):147–57.
  3. 3. Holdich DM, Reynolds JD, Souty-Grosset C, Sibley PJ. A review of the ever increasing threat to European crayfish from non-indigenous crayfish species. Knowl Manag Aquat Ecosyst. 2009;11:394–5.
  4. 4. Söderhäll K, Cerenius L. The crayfish plague fungus: history and recent advances. Freshw. Crayfish. 1999;12:11–35.
  5. 5. Unestam T. Resistance to the crayfish plague in some American, Japanese and European crayfishes. Rep. Inst. Freshw. Res., Drottningholm 1969;49:202–9.
  6. 6. Unestam T. On the host range and origin of the crayfish plague fungus. Rep. Inst. Freshw. Res., Drottningholm. 1972;52:192–8.
  7. 7. Martín-Torrijos L, Martínez-Ríos M, Casabella-Herrero G, Adams SB, Jackson CR, Diéguez-Uribeondo J. Tracing the origin of the crayfish plague pathogen, Aphanomyces astaci, to the Southeastern United States. Sci Rep. 2021;11(9332).
  8. 8. Cerenius L, Andersson MG, Söderhäll K. Aphanomyces astaci and crustaceans. In: Lamour K, Kamoun D, editors. Oomycete Genetics and Genomics: Diversity, Interactions and Research Tools. New Jersey: John Wiley & Sons Inc. 2009;425–33.
  9. 9. Gross R, Palm S, Kõiv K, Prestegaard T, Jussila J, Paaver T, et al. Microsatellite markers reveal clear geographic structuring among threatened noble crayfish (Astacus astacus) populations in Northern and Central Europe. Conserv Genet. 2013;14(4):809–21.
  10. 10. Jussila J, Makkonen J, Vainikka A, Kortet R, Kokko H. Latent crayfish plague (Aphanomyces astaci) infection in a robust wild noble crayfish (Astacus astacus) population. Aquaculture. 2011;321(1–2):17–20.
  11. 11. Makkonen J, Kokko H, Vainikka A, Kortet R, Jussila J. Dose-dependent mortality of the noble crayfish (Astacus astacus) to different strains of the crayfish plague (Aphanomyces astaci). J Invertebr Pathol. 2014;115(1):86–91.
  12. 12. Makkonen J, Jussila J, Kortet R, Vainikka A, Kokko H. Differing virulence of Aphanomyces astaci isolates and elevated resistance of noble crayfish Astacus astacus against crayfish plague. Dis Aquat Organ. 2012;102(2):129–36. pmid:23269387
  13. 13. Bruski CA, Dunham DW. The Importance of Vision in Agonistic Communication of the Crayfish Orconectes rusticus. I: An Analysis of Bout Dynamics Stable URL: Behaviour. 1987;1(3):83–107.
  14. 14. Hudina S, Galić N, Roessink I, Hock K. Competitive interactions between co-occurring invaders: Identifying asymmetries between two invasive crayfish species. Biol Invasions. 2011;13(8):1791–803.
  15. 15. Tierney AJ, Godleski MS, Massanari JR. Comparative analysis of agonistic behavior in four crayfish species. J Crustac Biol. 2000;20(1):54–66.
  16. 16. Söderbäck B. Interspecific dominance relationship and aggressive interactions in the freshwater crayfishes Astacus astacus (L.) and Pacifastacus leniusculus (Dana). Can J Zool. 1991;69(5):1321–5.
  17. 17. Lele SF, Pârvulescu L. Experimental evidence of the successful invader Orconectes limosus outcompeting the native Astacus leptodactylus in acquiring shelter and food. Biol. 2017;72(8):877–85.
  18. 18. Kouba A, Petrusek A, Kozák P. Continental-wide distribution of crayfish species in Europe: Update and maps. Knowl Manag Aquat Ecosyst. 2014;(413).
  19. 19. Vey A, Söderhäll K, Ajaxon A. Susceptibility of the Orconectes limosus Raff. to the crayfish plague, Aphanomyces astaci Schikora. Freshw. Crayfish. 1983;5:284–91.
  20. 20. Gherardi F, Daniels WH. Agonism and shelter competition between invasive and indigenous crayfish species. Can J Zool. 2004;82(12):1923–32.
  21. 21. Bovbjerg Richard V. Ecological Isolation and Competitive Exclusion in Two Crayfish (Orconectes Virilis and Orconectes Immunis). Ecology. 1970;51(2):225–36.
  22. 22. Blank GS, Figler MH. Interspecific Shelter Competition between the Sympatric Crayfish Species Procambarus clarkii (Girard) and Procambarus zonangulus (Hobbs and Hobbs). J Crusta. 1996;16(2):300–9.
  23. 23. Guiasu RC, Dunham DW. Initiation and outcome of agonistic contests in male form I Cambarus robustus Girard, 1852 crayfish (Decapoda, cambaridae). Curstaceana. 1997;70(4):480–96.
  24. 24. Guiasu RC, Dunham DW. Aggressive Interactions between the Crayfishes Cambarus bartonii bartonii and C. robustus (Decapoda: Cambaridae): Interspecific and Intraspecific Contests. J Crustac Biol. 1999;19(1):131–46.
  25. 25. Bergman DA, Kozlowski CP, McIntyre JC, Huber R, Daws AG, Moore PA. Temporal dynamics and communication of winner-effects in the crayfish, Orconectes rusticus. Behaviour. 2003;140(6):805–25.
  26. 26. Savvides P, Louca V, Sfenthourakis S. Competition for shelter occupancy between a native freshwater crab and an invasive crayfish. Aquat Ecol. 2015;49(3):273–8.
  27. 27. Vannini M, Sardini A. Aggressivity and dominance in river crab Potamon fluviatile (herbst). Monit Zool Ital—Ital J Zool. 1971;5(3):173–213.
  28. 28. Team RC. R: A Language and Environment for Statistical Computing. Vienna; 2020.
  29. 29. Team Rs. RStudio: Integrated Development Environment for R. Boston; 2020.
  30. 30. Kozák P, Buřič M, Policar T, Hamáčková J, Lepičová A. The effect of inter- and intra-specific competition on survival and growth rate of native juvenile noble crayfish Astacus astacus and alien spiny-cheek crayfish Orconectes limosus. Hydrobiologia. 2007;590(1):85–94.
  31. 31. Kokko H, Koistinen L, Harlioǧlu MM, Makkonen J, Aydin H, Jussila J. Recovering Turkish narrow clawed crayfish (Astacus leptodactylus) populations carry Aphanomyces astaci. Knowl Manag Aquat Ecosyst. 2012;(404):1–7.
  32. 32. Kušar D, Vrezec A, Ocepek M, Jenčič V. Aphanomyces astaci in wild crayfish populations in Slovenia: First report of persistent infection in a stone crayfish Austropotamobius torrentium population. Dis Aquat Organ. 2013;103(2):157–69. pmid:23548366
  33. 33. Martín-Torrijos L, Campos Llach M, Pou-Rovira Q, Diéguez-Uribeondo J. Resistance to the crayfish plague, Aphanomyces astaci (Oomycota) in the endangered freshwater crayfish species, Austropotamobius pallipes. PLoS One. 2017;12(7):1–14.
  34. 34. Holdich DM, editor. Biology of Freshwater Crayfish. Oxford: Blackwell Science; 2002. 702 p.
  35. 35. van Kuijk T, Biesmeijer JC, van der Hoorn BB, Verdonschot PFM. Functional traits explain crayfish invasive success in the Netherlands. Sci Rep. 2021;11(1). pmid:33531568
  36. 36. Söderbäck B. Replacement of the native crayfish Astacus astacus by the introduced species Pacifastacus leniusculus in a Swedish lake: possible causes ad mechanisms. Freshw Biol. 1995;(33):291–304.
  37. 37. Westman K, Savolainen R, Julkunen M. Replacement of the native crayfish Astacus astacus by the introduced species Pacifastacus leniusculus in a small, enclosed Finnish lake: A 30-year study. Ecography (Cop). 2002;25(1):53–73.
  38. 38. Schulz HK, Smietana P, Schulz R. Crayfish occurence in relation to land-use properties: implementation of a Geographic Information System (GIS). Bull français la pêche la Piscic. 2002;(367):861–72.