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30 September 2021 Predicting successful reproduction and establishment of non-native freshwater fish in peninsular Florida using life history traits
Katelyn M. Lawson, Jeffrey E. Hill
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Identification of factors that facilitate successful completion of invasion process stages by nonnative species is a major priority among invasion biologists. Stage-based analyses of non-native fish species traits have been conducted for several regions, but not for a subtropical non-native species hotspot like peninsular Florida. Typically, establishment is the first stage of analysis but Florida is home to many nonnative fish species that have successfully reproduced, yet failed to establish. Therefore, we used life history traits and three model types (categorical and regression trees, logistic regression, and discriminant analysis) to predict successful reproduction and establishment by non-native fishes in peninsular Florida. Statistical models for predicting both successful reproduction and establishment suggested parental care was the most important variable, but other traits included in the best models differ between the two stages. The high level of parental care in successful non-native fishes of Florida is unique among non-native freshwater fish faunas across the United States. Other studies also found that suites of traits used to predict various stages of the invasion process differ, suggesting that stage-based analyses provide a good foundation for better understanding invasion processes. Our results may be applied to stage-based risk screening tools for nonnative fishes in Florida.


The identification of factors contributing to successful establishment and invasion by nonnative species is an important objective for invasion biologists (Leung et al. 2012). In support of this objective, numerous studies examining the life history traits of introduced non-native species have been conducted for a variety of taxonomic groups. The results of these studies, even within one taxonomic group such as fishes, are highly variable and dependent on numerous factors such as regional characteristics, phylogenetic constraints, and stage of the invasion process examined (Garcia-Berthou 2007). The most heavily investigated stage of the invasion process is establishment (Garcia-Berthou 2007, Hayes & Barry 2008), however there are several steps that non-native organisms must complete prior to successfully establishing a stable population (Kolar & Lodge 2001, 2002, Hill 2008). Many different stages and definitions of the invasion process have been published (Kolar & Lodge 2001, Lockwood et al. 2005, Blackburn et al. 2011, Leung et al. 2012) therefore explicitly defining terminology is important (Richardson et al. 2000, Catford et al. 2009). One common aspect of invasion process models is that they are based on conditional probabilities; a species must successfully complete one stage before it can progress to the next (Hill 2008, Leung et al. 2012). We developed a linear, stage-based invasion model based on the literature to inform an investigation into the importance of life history traits in invasion science (Fig. 1). The stages that are included in this model are 1) transport/introduction into novel environment and survival, 2) successful reproduction and recruitment, 3) establishment of a self-sustaining population, 4) spatial spread of the population beyond the initial point of establishment, and 5) ecological and/or socio-economic impacts to the region where it is established (Fig. 1).

Fig. 1.

The five stages of the invasion process described in the present study. The two stages examined in the present study, reproduction and establishment, are shaded.


Survival following initial introduction is difficult to document because existing data underestimate failed introductions due to insufficient spatial and temporal coverage of sampling, low detectability of some species, and under-reporting of captures (Kolar & Lodge 2001, Garcia-Berthou 2007, Lawson et al. 2017). In Florida, there are likely hundreds of non-native fish species that have been introduced and gone undetected (Tuckett et al. 2016). Still, many non-native fish species have been collected multiple times in Florida yet failed to reproduce and recruit (United States Geological Survey 2021). The availability of this information makes it feasible to model successful reproduction among a select group of non-native fishes within the study region of peninsular Florida. Further, there are many non-native fish species in Florida for which reproduction has been documented, but not establishment of self-sustaining populations. An introduced species' ability to successfully reproduce is dependent on many factors such as high enough propagule pressure for availability of mates (Lockwood et al. 2005, Colautti et al. 2006, Simberloff et al. 2009) and cues for reproduction. Other requirements include suitable habitat for egg deposition and survival (Ortega et al. 2007), availability of food, and protection from predators to ensure juvenile survivorship and recruitment to the population (Baltz & Moyle 1993, Moyle & Light 1996).

When an introduced species is able to recruit offspring, the population can then grow in size which leads to establishment of a self-sustaining population. In contrast, population declines can also occur if reproduction requirements are not consistently met; this has been observed for several non-native fish species in Florida (Shafland et al. 2008, Hill 2016). In the literature, the reproduction stage is often considered to be a barrier or filter to establishment that must be overcome (Copp et al. 2005, Colautti et al. 2006, Blackburn et al. 2011) rather than a distinct stage of the invasion process. There are likely many reasons for this such as lower propagule pressure, harsher receiving environment, climate mismatch and other filters that prohibit the detection of introduced species that fail to reproduce and reproducing species that fail to establish. Consequently, this stage has not received much attention in previous studies predicting invasion success. Florida's warm climate, diverse water bodies, large human population, and ornamental aquaculture industry have facilitated the introduction of many species that are able to survive and reproduce yet fail to establish. This unique combination of factors allows us to study the reproduction stage of the invasion process, a novel first step for examining non-native fish success in Florida.

A quantitative approach was taken to identify traits associated with successful reproduction and those associated with establishment success given that reproduction occurs in non-native freshwater fishes in peninsular Florida (USA). Florida, with its large human population, strong introduction pathways, and favourable climate (Hill 2002) has more reported sightings of foreign non-native freshwater fish species than any other US state (Shafland et al. 2008). Since this number is continuing to increase (Shafland et al. 2008), developing methods to profile non-native fishes that are likely to become invasive in Florida is critical to improving management. A variety of quantitative techniques have been used to examine successful completion of invasion process stages across a range of taxa (Hayes & Barry 2008). The most common are classification and regression trees, discriminant analysis (DA), and logistic or multiple linear regression (Garcia-Berthou 2007, Hayes & Barry 2008), particularly for fishes (Kolar & Lodge 2002, Marchetti et al. 2004a, b, Ruesink et al. 2005, Ribeiro et al. 2008, Allen et al. 2013, Howeth et al. 2016). These statistical techniques are all suitable for our dataset, because classification trees are well-suited for the analysis of complex ecological datasets (Howeth et al. 2016), and logistic regression is useful for datasets where the number of subjects is small with respect to the number of variables (Ribeiro et al. 2008). All have been used in similar studies for other regions and most studies have used two or more techniques, however no consensus has been reached on the best approaches. Therefore, we used classification trees, DA, and logistic regression to identify traits that likely facilitate successful reproduction and establishment of non-native freshwater fishes in Florida and compared the results. Our objectives for this study were to 1) determine which traits were most important in predicting whether introduced species would successfully reproduce, 2) identify traits that may facilitate reproducing non-native fish species to establish self-sustaining populations, and 3) compare the effectiveness of logistic regression, classification trees, and DA for predicting each of the two stages of the invasion process (Fig. 1).

Material and Methods

Data collection

A list of non-native taxa (hereafter, “species”) that have been detected in peninsular Florida was first compiled and any species with fewer than three collection records was removed to ensure that species included have been introduced several times. Sources used to create this list and determine status were the US geological survey's nonindigenous aquatic species database (United States Geological Survey 2021), and Shafland et al. (2008). Species for which there was little published information were also removed. The list of remaining species was then divided into those that have reproduced successfully at any point in time somewhere in peninsular Florida, and those that have never been observed reproducing in the environment for inclusion in reproduction models. Species that have successfully reproduced were then split into two groups: those that have successfully established and those that have failed to establish populations for inclusion in establishment models. A literature review was conducted to collect data for 21 life history variables for potential use as predictors in the analyses (Table 1). Multiple searches for each species using both common name and scientific name, both with and without “life history” included in the search bar, were conducted using Google Scholar and the Web of Science. Primary literature was used whenever possible, but databases, including Fishbase (Froese & Pauly 2021), FishTraits (Frimpong & Angermeier 2009), and grey literature were used to fill in any data gaps. For some species, data for specific traits were not available, in which case congener data were used following the methods of Olden et al. (2006). Categorical variables were numerically coded, and all continuous variables were left in their original state, except for fecundity which was log10 transformed.

Table 1.

Traits that were used in the analyses for the present study based on six references with descriptions for measurement of each trait. Traits with an asterisk (*) were included in the analyses.


Statistical analyses

Mann-Whitney rank sum tests were used to determine significant trait differences between species that have succeeded or failed to pass through the reproduction and establishment invasion filters (Lester 2005). Life history variables were compared using Spearman rank correlations to detect significant correlations among variables; data for both groups of fishes were used in this analysis. Variables with a correlation of 0.60 or greater were identified and one variable was retained as a surrogate for both correlated variables to avoid unnecessary complexity (Marchetti et al. 2004a). When two variables were highly correlated, the trait with the highest significance according to the Mann-Whitney rank sum test for reproduction was retained. Variables that were removed from the dataset include length at maturation, fecundity, migratory, time to hatch, and reproductive guild, reducing the number of variables considered in the models to 16. These non-parametric tests were used because the traits' data were not normally distributed.

Table 2.

Observed status vs. predicted status for all three reproduction models: Log Reg = logistic regression model chosen from bootstrap analysis, Class Tree = classification tree, and DA = discriminant analysis. The values are: 1 = successful reproduction, and 0 = fail to reproduce.




The remaining variables were then used to develop logistic regression models to predict successful reproduction, and to predict successful establishment of non-native fishes that have reproduced in Florida. All categorical variables were characterized as factors prior to running models. A full model with all 16 remaining variables was produced for each stage, and a backward selection procedure was used to reduce the models. A bootstrap analysis was then applied to the full models with 50 model iterations, to identify the best model for each stage and to assess predictor importance. The best model was then applied to the dataset to identify any misclassified species. In order to better assess model classification accuracy, a leave-one out cross-validation procedure was applied to each model. These analyses were completed using the R packages “stats”, “MASS”, “bootstepAIC”, and “boot” in R version 4.0.3 (R Core Team 2020) and RStudio 1.3.1093 (RStudio Team 2020).

A second method, classification tree analysis was used to predict successful reproduction, and successful establishment. Classification trees are models developed through partitioning independent variables to predict a categorical outcome. Classification trees were used instead of regression trees because the response variable was binary (success = 1, failure = 0) rather than continuous. Due to a small sample size, we used the ten-fold cross-validation procedure to choose the best classification trees. We followed the methods of Howeth et al. (2016) and selected the smallest tree within one standard error of the misclassification rate. The R package “rpart” was used to complete these analyses in R version 4.0.3 (R Core Team 2020) and RStudio 1.3.1093 (RStudio Team 2020).

Table 3.

Observed status vs. predicted status for all three establishment models: Log Reg = logistic regression model chosen from bootstrap analysis, Class Tree = classification tree, and DA = discriminant analysis. The values are: 1 = successful establishment, and 0 = fail to establish.


Canonical discriminant analysis, a multivariate method that determines the relationship between a categorical variable and independent variables of mixed data types, was also used. Canonical scores and structure coefficients for the discriminant function were plotted. These analyses were completed using the R package “candisc” in RStudio R version 4.0.3 (R Core Team 2020) and RStudio 1.3.1093 (RStudio Team 2020). For each of the two stages predicted, the best logistic regression model identified in the bootstrap procedure was used to classify each species from the original dataset, and the classification results were compared with the results from the classification tree and discriminant function.


Of the 67 non-native fish species selected, 24 species have never been observed reproducing in peninsular Florida (Table 2). Of the 43 species that have successfully reproduced, three were unable to establish potentially due to human intervention; however, it is unknown whether they would have established had they not been eradicated. Those three species, convict cichlid Archocentrus nigrofasciatus Gunther, 1867 (Hill & Cichra 2005), three spot cichlid Cichlasoma trimaculatum Gunther, 1867 (Courtenay & Stauffer 1990), and redbelly tilapia Tilapia zillii Gervais, 1848 (Hogg 1976, Courtenay et al. 1984, 1986, Taylor et al. 1986) were not included in the dataset used to create models predicting successful establishment. The variable platyfish Xiphophorus variatus Meek, 1904 was also removed due to fluctuating populations and unknown status in many areas where it has previously been observed (United States Geological Survey 2021). Although four species of Pterygoplichthys were combined in the analyses for reproduction (Pterygoplichthys sp.), the two species most commonly found in Florida, the vermiculated sailfin catfish Pterygoplichthys disjunctivus Weber, 1991 and the Orinoco sailfin catfish Pterygoplichthys multiradiatus Hancock, 1828 were included in the analyses for successful establishment resulting in 40 species for analysis. Of those 40 species, 31 successfully established and nine failed to establish (Table 3).

Fig. 2.

Classification tree predicting successful reproduction and establishment of non-native fish in peninsular Florida. A) Successful reproduction of non-native fish. B) Successful establishment of non-native fish that have reproduced in peninsular Florida. These classification trees could be used as a rapid screen or hazard identification of non-native fishes with potential for introduction in Florida.



The statistical models supported parental care as the most important variable, with larger egg diameter strongly supported in two of the three methods. The final model identified in the logistic regression bootstrap analysis included the following predictors: maximum body length, swim factor, substrate preference, fluvial dependence, trophic guild, diet breadth, egg diameter, spawning temperature, parental care, salinity tolerance, and spawning season. The predictors selected most frequently for models in the bootstrap analysis, indicating a higher level of importance, include egg diameter and parental care (Table 4). As the model was developed using all the data, classification was completed with 100% accuracy, however leave-one-out cross-validation resulted in a 78% classification accuracy.

The classification tree that was selected (Fig. 2) used parental care and swim factor to classify successful and failed species with 90% accuracy (87% upon ten-fold cross-validation). The resultant tree shows that species likely to reproduce successfully have parental care greater than 2.5 and those likely to fail have parental care less than 2.5 and a swim factor less than 0.545 (relative cost = 0.29, AUROC = 0.91). The discriminant function that best predicted successful reproduction indicates that high parental care, larger egg diameter, and spawning substrate are correlated with successful reproduction (Fig. 3). The misclassification rate for the model was 0.134 (0.223 in jackknife validation) and the discriminant function classified species with 87% accuracy (78% in jackknife validation). Table 2 contains the prediction results for all species by model. Among the models predicting successful reproduction, the classification tree model performed the best, and misidentified only one species with successful reproduction, the silver dollar Metynnis sp., as failed. Of the species that failed to reproduce, the classification tree predicted six would successfully reproduce, which was less than the nine misclassifications by canonical discriminant analysis.

Fig. 3.

Canonical discriminant analysis results for predicting successful reproduction among fishes introduced into peninsular Florida (A) and successful establishment by fishes that reproduced (B). The boxplots summarize canonical scores by displaying the median, first and third quartiles, minimum, maximum and outliers for each group. Variable contribution to the models is displayed as vectors with longer arrows indicating greater contribution.



For establishment, given that reproduction occurs, parental care was a consistent variable across models. The models also suggested that reproducing species that established were not fluvial dependent and were relatively benthic in vertical position in the water column. The final model identified in the logistic regression bootstrap analysis included the following predictors: swim factor, fluvial dependence, diet breadth, egg diameter, care, salinity tolerance, and air breathing. The predictors selected most frequently for models in the bootstrap analysis, indicating a higher level of importance, also include egg diameter and parental care (Table 4). As the model was developed using all the data, classification was completed with 100% accuracy, however leave-one-out cross-validation resulted in a 80% classification accuracy.

Table 4.

The percentage of logistic regression models each predictor variable was included in during bootstrap analysis for each of the invasion stages.


The classification tree that was selected (Fig. 2) used only parental care to classify successful and failed species with 90% accuracy (79% upon tenfold cross-validation). Species with parental care greater than 3.5 were more likely to successfully establish than those with parental care lower than 3.5 (relative cost = 0.44, AUROC = 0.86). The discriminant function that best predicted successful establishment among species that have reproduced indicates species that have established have high levels of parental care, no fluvial dependence, larger maximum length, and greater salinity tolerance (Fig. 3). The misclassification rate for the model was 0.125 (0.175 in jackknife validation) and the discriminant function classified species with 88% accuracy (83% in jackknife validation). For predicting successful establishment, both the classification tree and discriminant analysis misclassified the croaking gourami Trichopsis vittata Cuvier, 1831 as failed. Although it has established a self-sustaining population, its range in Florida is extremely small when compared to most other established species (Schofield & Schulte 2016, United States Geological Survey 2021). The classification tree only misclassified the established oriental weatherfish Misgurnus anguillicaudatus Cantor, 1842 as failed. Overall, we found that all three modelling techniques performed similarly (87-78% after cross-validation).


Parental care is the most important variable for predicting both reproduction and establishment, and is the only trait included in every model reported in the present study. Other variables, particularly reproductive traits, were important predictors of reproduction and establishment but to a lesser degree. All models developed in the present study were comparable with similar predictions and accuracies for each stage. The models performed well, with percent accuracies ranging from 78-87% for predicting reproduction, and 79-83% for predicting establishment. These accuracies are consistent with similar analyses for other regions (e.g. Kolar & Lodge 2002).

Table 5.

Summary of non-native fishes and corresponding parental care strategies by family for the present study and three previous studies in different parts of the United States. The number of species represents the number of species in each family present in the study area. Parental care ranges indicated the strategies employed by the species in that family. Parental care values range from 0 to 6, with higher numbers equating to greater levels of parental care (Olden et al. 2006). References are as follows: (1) Olden et al. (2006), (2) Marchetti et al. (2004b), and (3) Kolar & Lodge (2002).


Parental care was the most important predictor for reproduction, and for establishment because most of the species for which there is evidence of reproduction went on to establish self-sustaining populations. Of the 31 species included in this analysis that have successfully established, only the oriental weatherfish lacks parental care and the croaking gourami has relatively low levels of parental care (Lawson 2018). Each of the 29 remaining established species have higher levels of parental care with strategies including livebearing (Poeciliidae), mouthbrooding (Cichlidae), and paternal or biparental nest guarding (Lawson 2018). The high level of parental care displayed by many of the successfully established non-native fishes in Florida is unique among non-native freshwater fish faunas across the United States (Table 5; Kolar & Lodge 2002, Marchetti et al. 2004b, Olden et al. 2006).

The cichlid family in particular is a diverse group with high levels of parental care (Turner 2007) that is well-represented among successfully established non-native species in Florida. Many cichlids that are successfully established in Florida exhibit biparental care, which is a unique strategy among teleost fishes (Teresa & Goncalves-de-Freitas 2011). All Neotropical cichlid species established in Florida exhibit this biparental care strategy. Gross & Sargent (1985) theorized that biparental care resulted from the coevolution of paternal care increasing with larger egg sizes, necessitating a longer guarding period and teamwork to successfully guard mobile fry. This biparental care strategy has not evolved in native North American fish families, being present in North America only in the members of the family Cichlidae that spread north from South America into Mexico and the Rio Grande River basin of Texas. The family Centrachidae which possesses life history strategies similar to the family Cichlidae only exhibits nest guarding by males (Blumer 1982, Gross & Sargent 1985). Of the many African cichlid species that have likely been introduced to Florida, the tilapiine species have been the most successful (United States Geological Survey 2021). These species also have a high degree of parental care; members of the genus Oreochromis are maternal mouthbrooders, Tilapia spp. are nest guarders, and blackchin tilapia Sarotherodon melanotheron Ruppell, 1852 is a paternal (occasionally biparental) mouthbrooder (Trewavas 1983).

Although parental care is the best predictor of both successful reproduction and establishment, other traits included in the best models differ between the two stages. Egg diameter and swim factor seem to be important predictors of successful reproduction, whereas fluvial dependence and vertical position in the water column are more important predictors of establishment. Other studies have found that suites of traits used to predict various stages of the invasion process differ, which suggests that stage-based analyses provide a good foundation for a better understanding of invasion processes (Kolar & Lodge 2002, Marchetti et al. 2004b, Howeth et al. 2016). Parental care, along with physiological tolerance, were the two strongest predictors of establishment for non-native fishes in California according to Marchetti et al. (2004b). The reason behind its importance, that parental care increases juvenile survival and minimizes their dispersal into poor environments (Marchetti et al. 2004b), is likely the same for Florida. Similar to the present study, they also found parental care to be an important predictor of the other stages they examined with otherwise different suites of traits as predictors for each stage.

In addition to parental care, traits that appear to be important for predicting successful reproduction of non-native fishes in Florida include egg diameter, air breathing, swim factor, and to a lesser degree diet breadth, maximum length, fluvial dependence, and spawning season. Larger egg diameters among species that have successfully reproduced indicate a higher level of parental investment in offspring, consistent with the equilibrium life history strategy (Winemiller & Rose 1992, Winemiller 1995, Lawson 2018). Egg diameter has also been shown to positively correlate with the duration of parental care in ectothermic animals (Sargent et al. 1987, Kolm et al. 2006). Of the introduced fishes examined, many that have successfully reproduced in Florida are facultative air breathers and have larger swim factors which indicates less frequent or slower swimming, and no fluvial dependency (Olden et al. 2006). Fishes possessing all four major traits (parental care, air-breathing, larger swim factors, no fluvial dependency) indicating successful reproduction include clown knifefish Chitala ornata Gray, 1831, brown hoplo Hoplosternum littorale Hancock, 1828, suckermouth catfish Hypostomus sp., armoured sailfin catfish Pterygoplichthys spp., walking catfish Clarias batrachus Linnaeus, 1758, spotfin spiny eel Macrognathus siamensis Gunther, 1861, Asian swamp eel Monopterus albus Zuiew, 1793, and bullseye snakehead Channa marulius Hamilton, 1822.

The suite of traits that best predict successful establishment differs from those predicting reproduction. Parental care is still the single best predictor, however fluvial dependence, maximum length, and vertical position in the water column are of secondary importance. It should be noted that there are no successfully established nonnative fishes in Florida with fluvial dependence. Many of the introduced benthic species have also successfully established, and this strategy seems particularly successful when combined with parental care, air breathing, and lack of fluvial dependence, as demonstrated by brown hoplo, suckermouth catfish, armoured sailfin catfish, walking catfish, spotfin spiny eel, and Asian swamp eel. These species are especially suited to the soft substrate and generally low to no flow aquatic habitats in Florida. The brown hoplo, armoured sailfin catfishes, and walking catfish have done especially well and can be found in a variety of habitats across much of peninsular Florida (Lawson 2018, United States Geological Survey 2021). Many other species that have successfully established in Florida are not benthic or air breathing, but pelagic species with similarly high levels of parental care and lack of fluvial dependence such as those in the family Cichlidae. Successfully established species also have a larger maximum body length.

Despite numerous opportunities presented by the introduction of fishes of varying geographic origin and body size, observations of reproduction in peninsular Florida by opportunistic or periodic strategists (Winemiller & Rose 1992) are almost completely lacking (Table 2). The lack of reproduction in opportunistic non-native fishes is especially surprising given the large proportion of native fishes that fall within or near this category (Lawson 2018). The inability to reproduce or establish could be due to unsuitable environmental conditions or biotic resistance, however specific causes of failure remain unknown. Abiotic and biotic factors have been shown to influence the failure of small-bodied fish invaders (Hill & Tuckett 2018) which are often opportunistic strategists. Aggression (Thompson et al. 2012), predation (Hill 2016), and asymmetric intraguild predation (Tuckett et al. 2021) from native species are known mechanisms of biotic resistance in the region. Periodic strategists may have more difficulty reproducing in Florida habitats due to their often exacting requirements for flowing waters or other habitat features that may not be present or conditions that may be temporally mismatched for reproduction. Research into the specific mechanisms of failure in reproduction and recruitment, whether abiotically or biotically driven, is warranted.

Peninsular Florida possesses a variety of unique attributes that make it particularly susceptible to non-native fish introductions. These attributes include a subtropical climate, large human population, numerous importation locations, and a robust ornamental aquaculture industry (Hill & Yanong 2002). The pet trade and ornamental aquaculture industries have facilitated the importation and culture of hundreds of non-native fish species into Florida (Chapman et al. 1997, Hill & Yanong 2002). The diversity and number of donor regions of these non-native fishes are unparalleled when compared to other regions of the United States. Fishes that have successfully established in Florida come from tropical regions of Central America, South America, Africa, and Asia, whereas most established non-natives in California, the Great Lakes, and the River Colorado are native transplants, or temperate species from Eurasia. This leads to relatively little overlap in Florida's introduced fauna and that of other studied regions of the US (Table 5). These differences in nonnative fauna are largely a product of the types of introduction pathways that are most common for each region, and the receiving environments. The fact that peninsular Florida imports so many nonnative tropical fish species which have a strong climate match to the state presents a need for the development of a region-specific risk screening tool for fishes.

In terms of accurately predicting the success of species included in the training dataset, there is some variation among the models. Logistic regression provides the best understanding of variable importance, but the models are not as user-friendly for predicting success of a large number of species. Classification trees combine a high degree of accuracy with a simple model that can be applied easily, allowing the user to quickly screen a large number of species. In a study comparing the performance of three model types applied to mixed ecological data, Olden & Jackson (2002) found that of the three, classification trees outperformed multiple linear regression and discriminant analysis. We similarly found that the classification trees misidentified fewer species than both the best logistic regression model, and the best discriminant function.

The results of the present study may be applied toward the creation of stage-based risk screening tools for non-native fishes for Florida. Region-specific analyses using traits to predict success are growing in popularity and are useful for regions with elevated risk (e.g. Kolar & Lodge 2002). The results of the classification tree analysis in particular can be used for hazard identification or as a simple, coarse screen for Florida (Fig. 2). Species with parental care scores > 2.5 are likely to reproduce (92%) and those with score < 2.5 still have a 67% chance of reproduction if their swim factor is > 0.545. Given successful reproduction, 94% of species with parental care scores > 3.5 have successfully established. This simple tool can augment more detailed and complex risk screening tools such as the fish invasiveness screening kit (FISK: Copp et al. 2009, Lawson et al. 2013, Vilizzi et al. 2019) and aquatic species invasiveness screening kit (AS-ISK: Copp et al. 2016, Vilizzi et al. 2021). The development of more regional risk screening tools can assist managers by improving accuracy and saving time. Future research will address characteristics that can be used to predict spread and determine the magnitude and probability of impacts by non-native fishes in Florida. The spread of non-native fishes in Florida has not been specifically investigated and new methods for measuring spread may be needed for this region. Similarly, few analyses address the impacts of nonnative fishes in Florida (Schofield & Loftus 2015), a critical need for additional research to improve risk assessment.


We thank the University of Florida, College of Agricultural and Life Sciences for Graduate Student Fellowship funding, the School of Forest Resources and Conservation, and the faculty, staff and students of the Tropical Aquaculture Laboratory (Craig Watson, Director) for their assistance. We also thank Drs. Michael Allen, Charles Cichra, Daryl Parkyn, and Steven Johnson (University of Florida) for their valuable suggestions for the improvement of this manuscript and Kelly Gestring (Florida Fish and Wildlife Conservation Commission) for helpful discussions about the lists of successful and failed non-native species. Author contributions: K. Lawson and J. Hill designed the study and K. Lawson collected the data, conducted analyses, and drafted the manuscript. Both authors contributed to the final version of the manuscript.



Alcaraz C., Vila-Gispert A. & Garcia-Berthou E. 2005: Profiling invasive fish species: the importance of phylogeny and human use. Divers. Distrib. 11: 289–298. Google Scholar


Allen C.R., Nemec K.T., Wardwell D.A. et al. 2013: Predictors of regional establishment success and spread of introduced non-indigenous vertebrates. Glob. Ecol. Biogeogr. 22: 889–899. Google Scholar


Baltz D.M. & Moyle P.B. 1993: Invasion resistance to introduced species by a native assemblage of stream fishes. Ecol. Appl. 3: 246–255. Google Scholar


Blackburn T.M., Pyšek P., Bacher S. et al. 2011: A proposed unified framework for biological invasions. Trends Ecol. Evol. 26: 333–339. Google Scholar


Blumer L. S. 1982: A bibliography and categorization of bony fishes exhibiting parental care. Zool. J. Linn. Soc. 76: 1–22. Google Scholar


Catford C.A., Jansson R. & Nilsson C. 2009: Reducing redundancy in invasion ecology by integration hypotheses into a single theoretical framework. Divers. Distrib. 15: 22–40. Google Scholar


Chapman F.A., Fitz-Coy S.A., Thunberg E.M. & Adams C.M. 1997: United States of America trade in ornamental fish. J. World Aquacult. Soc. 28: 1–10. Google Scholar


Colautti R.I., Grigorovich I.A. & MacIsaac H.J. 2006: Propagule pressure: a null model for biological invasions. Biol. Invasions 8: 1023–1037. Google Scholar


Copp G.H., Bianco P.G., Bogutskaya N.G. et al. 2005: To be, or not to be, a non-native freshwater fish? J. Appl. Ichthyol. 21: 242–262. Google Scholar


Copp G.H., Vilizzi L., Mumford J. et al. 2009: Calibration of FISK, an invasiveness screening tool for nonnative freshwater fishes. Risk Anal . 29: 457–467. Google Scholar


Copp G.H., Vilizzi L., Tilbury H. & Stebbing P. 2016: Development of a generic decision-support tool for identifying potentially invasive aquatic taxa: AS-ISK. Manag. Biol. Invasions 7: 343–350. Google Scholar


Courtenay W.R., Jr., Hensley D.A., Taylor J.N. & McCann J.A. 1984: Distribution of exotic fishes in the continental United States. In: Courtenay W.R., Jr. & Stauffer J.R., Jr (eds.), Distribution, biology and management of exotic fishes. John Hopkins University Press , Baltimore, USA : 41–77. Google Scholar


Courtenay W.R., Jr., Hensley D.A., Taylor J.N. & McCann J.A. 1986: Distribution of exotic fishes in North America. In: Hocutt C.H. & Wiley E.O. (eds.), The zoogeography of North American freshwater fishes. John Wiley and Sons , New York, USA : 675–698. Google Scholar


Courtenay W.R., Jr. & Stauffer J.R., Jr. 1990: The introduced fish problem and the aquarium fish industry. J. World Aquacult. Soc. 21: 145–159. Google Scholar


Frimpong E.A. & Angermeier P.L. 2009: FishTraits: a database of ecological and life-history traits of freshwater fishes of the United States. Fisheries 34: 487–495. Google Scholar


Froese R. & Pauly D. 2019: FishBase. Downloaded on May 2021. Google Scholar


Garcia-Berthou E. 2007: The characteristics of invasive fishes: what has been learned so far? J. Fish Biol. 71: 33–55. Google Scholar


Gross M.R. & Sargent R.C. 1985: The evolution of male and female parental care in fishes. Am. Zool. 25: 807–822. Google Scholar


Hayes K.R. & Barry S.C. 2008: Are there any consistent predictors of invasion success? Biol. Invasions 10: 483–506. Google Scholar


Hill J.E. 2002: Exotic fishes in Florida. LakeLines 22: 39–43. Google Scholar


Hill J.E. 2008: Non-native species in aquaculture: terminology, potential impacts, and the invasion process. Southern Regional Aquaculture Center , Stoneville, USA . Google Scholar


Hill J.E. 2016: Collapse of a reproducing population of non-native African jewelfish (Hemichromis letourneuxi) in a Florida lake. NeoBiota 29: 35–52. Google Scholar


Hill J.E. & Cichra C.E. 2005: Eradication of a reproducing population of convict cichlids, Cichlasoma nigrofasciatum (Cichlidae), in north-central Florida. Fla. Sci. 68: 65–74. Google Scholar


Hill J.E. & Tuckett Q.M. 2018: Abiotic and biotic contributions to invasion resistance for ornamental fish in west-central Florida, USA. Hydrobiologia 817: 363–377. Google Scholar


Hill J.E. & Yanong R.P. 2002: Fresh water ornamental fish commonly cultured in Florida. EDIS Circular 54 , University of Florida , Gainesville, USA . Google Scholar


Hogg R.G. 1976: Established exotic cichlid fishes in Dade County, Florida. Fla. Sci. 39: 97–103. Google Scholar


Howeth J.G., Gantz C.A., Angermeier P.L. et al. 2016: Predicting invasiveness of species in trade: climate match, trophic guild and fecundity influence establishment and impact of non-native freshwater fishes. Divers. Distrib. 22: 148–160. Google Scholar


Kolar C.S. & Lodge D.M. 2001: Progress in invasion biology: predicting invaders. Trends Ecol. Evol. 16: 199–204. Google Scholar


Kolar C.S. & Lodge D.M. 2002: Ecological predictions and risk assessment for alien fishes in North America. Science 298: 1233–1236. Google Scholar


Kolm N., Goodwin N.B., Balshine S. & Reynolds J.D. 2006: Life history evolution in cichlids 1: revisiting the evolution of life histories in relation to parental care. J. Evol. Biol. 19: 66–75. Google Scholar


Lawson K.M. 2018: Use of life history traits to predict invasion success of non-native fishes in Peninsular Florida. PhD thesis, University of Florida , Gainesville, USA . Google Scholar


Lawson K.M., Tuckett Q.M., Ritch J.L. et al. 2017: Distribution and status of five non-native fish species in the Tampa Bay drainage (USA), a hot spot for fish introductions. BioInvasions Rec . 6: 393–406. Google Scholar


Lawson L.L., Vilizzi L., Hill J.E. et al. 2013: Revisions of the fish invasiveness screening kit (FISK) for its application in warmer climatic zones, with particular reference to peninsular Florida. Risk Anal. 33: 1414–1431. Google Scholar


Lester P.J. 2005: Determinants for the successful establishment of exotic ants in New Zealand. Divers. Distrib. 11: 279–288. Google Scholar


Leung B., Roura-Pascual N., Bacher S. et al. 2012: TEASIng apart alien species risk assessments: a framework for best practices. Ecol. Lett. 15: 1475–1493. Google Scholar


Lockwood J.L., Cassey P. & Blackburn T. 2005: The role of propagule pressure in explaining species invasions. Trends Ecol. Evol. 20: 223–228. Google Scholar


Marchetti M.P., Moyle P.B. & Levine R. 2004a: Alien fishes in California watersheds: characteristics of successful invaders. Ecol. Appl. 14: 587–596. Google Scholar


Marchetti M.P., Moyle P.B. & Levine R. 2004b: Invasive species profiling? Exploring the characteristics of non-native fishes across invasion stages in California. Freshw. Biol. 49: 646–661. Google Scholar


Moyle P.B. & Light T. 1996: Biological invasions of fresh water: empirical rules and assembly theory. Biol. Conserv. 78: 149–161. Google Scholar


Olden J.D. & Jackson D.A. 2002: A comparison of statistical approaches for modelling fish species distributions. Freshwater Biol . 47: 1976–1995. Google Scholar


Olden J.D., Poff N.L. & Bestgen K.R. 2006: Life-history strategies predict fish invasions and extirpations in the Colorado River Basin. Ecol. Monogr. 76: 25–40. Google Scholar


Ortega H., Guerra H. & Ramirez R. 2007: The introduction of nonnative fishes into freshwater systems of Peru. In: Bert T.M. (ed.), Ecological and genetic implications of aquaculture activities. Springer , Dordrecht, Netherlands : 247–278. Google Scholar


R Core Team 2020: R: a language and environment for statistical computing. R Foundation for Statistical Computing , Vienna, Austria . Google Scholar


Ribeiro F., Elvira B., Collares-Pereira M.J. & Moyle P.B. 2008: Life-history traits of non-native fishes in Iberian watersheds across several invasion stages: a first approach. Biol. Invasions 10: 89–102. Google Scholar


Richardson D.M., Pysek P., Rejmanek M. et al. 2000: Naturalization and invasion of alien plants: concepts and definitions. Divers. Distrib. 6: 93–107. Google Scholar


RStudio Team 2020: RStudio: integrated development for R. RStudio, Inc ., Boston, USA . Google Scholar


Ruesink J. 2005: Global analysis of factors affecting the outcome of freshwater fish introductions. Conserv. Biol. 19: 1883–1893. Google Scholar


Sargent R.C., Taylor P.D. & Gross M.R. 1987: Parental care and the evolution of egg size in fishes. Am. Nat. 129: 32–46. Google Scholar


Schofield P.J. & Loftus W.F. 2015: Non-native fishes in Florida waters: a literature review and synthesis. Rev. Fish Biol. Fish. 25: 117–145. Google Scholar


Schofield P.J. & Schulte J.M. 2016: Small but tough: what can ecophysiology of croaking gourami Trichopsis vittata (Cuvier, 1831) tell us about invasiveness of non-native fishes in Florida? NeoBiota 28: 51–65. Google Scholar


Shafland P.L., Gestring K.B. & Stanford M.S. 2008: Florida's exotic freshwater fishes. Fla. Sci. 7: 220–245. Google Scholar


Simberloff D. 2009: The role of propagule pressure in biological invasions. Annu. Rev. Ecol. Evol. Syst. 40: 81–102. Google Scholar


Taylor J.N., Snyder D.B. & Courtenay W.R., Jr. 1986: Hybridization between two introduced, substrate-spawning tilapias (Pisces: Cichlidae) in Florida. Copeia 1986: 903–909. Google Scholar


Teresa F.B. & Goncalves-de-Freitas E. 2011: Reproductive behavior and parental roles of the cichlid fish Laetacara araguaiae. Neotrop. Ichthyol. 9: 355–362. Google Scholar


Thompson K.A., Hill J.E. & Nico L.G. 2012: Eastern mosquitofish resists invasion by nonindigenous poeciliids through agonistic behaviors. Biol. Invasions 14: 1515–1529. Google Scholar


Trewavas E. 1983: Tilapiine fishes of the genera Sarotherodon, Oreochromis, and Danakilia. British Museum of Natural History , London, UK . Google Scholar


Tuckett Q.M., Deacon A.E., Fraser D. et al. 2021: Unstable intraguild predation causes establishment failure of a globally invasive species. Ecology 102: e03411. Google Scholar


Tuckett Q.M., Ritch J.L., Lawson K.M. & Hill J.E. 2016: Implementation and enforcement of best management practices for Florida ornamental aquaculture with an emphasis on nonnative species. N. Am. J. Aquacult. 78: 113–124. Google Scholar


Turner G.F. 2007: Adaptive radiation of cichlid fish. Curr. Biol. 17: R827–R831. Google Scholar


United States Geological Survey 2021: Nonindigenous aquatic species database. Downloaded on May 2021. Google Scholar


Vila-Gispert A., Alcaraz C. & Garcia-Berthou E. 2005: Life-history traits of invasive fish in small Mediterranean streams. Biol. Invasions 7: 107–116. Google Scholar


Vilizzi L., Copp G.H., Adamovich B. et al. 2019: A global review and meta-analysis of applications of the freshwater fish invasiveness screening kit. Rev. Fish Biol. Fish. 29: 529–568. Google Scholar


Vilizzi L., Copp G.H., Hill J.E. et al. 2021: A global-scale screening of non-native aquatic organisms to identify potentially invasive species under current and future climate conditions. Sci. Total Environ. 788: 147868. Google Scholar


Winemiller K.O. 1989: Patterns of variation in life-history among South American fishes in periodic environments. Oecologia 81: 225–241. Google Scholar


Winemiller K.O. 1995: Fish ecology. In: Nierenberg W.A. (ed.), Encyclopedia of environmental biology, vol. 2. Academic Press , San Diego, USA : 49–66. Google Scholar


Winemiller K.O. & Rose K.A. 1992: Patterns of life-history diversification in North American Fishes: implications for population regulation. Can. J. Fish. Aquat. Sci. 49: 2196–2218. Google Scholar
Katelyn M. Lawson and Jeffrey E. Hill "Predicting successful reproduction and establishment of non-native freshwater fish in peninsular Florida using life history traits," Journal of Vertebrate Biology 70(4), 21041.1-17, (30 September 2021).
Received: 1 June 2020; Accepted: 10 August 2021; Published: 30 September 2021

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