Keith B. Gido’s research while affiliated with Kansas State University and other places

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Publications (209)


Model outputs from ANCOVA for emergent midge body size (mm).
Drought‐Induced Decreases in Abundance of Emergent Midge Subsidies Are Offset by Increased Body Size in a Prairie Stream
  • Article
  • Full-text available

February 2025

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36 Reads

Freshwater Biology

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Keith B. Gido

Emerging aquatic insects can be an important resource subsidy for a variety of terrestrial consumers, including spiders, birds, bats and lizards. Emergence flux is influenced by a variety of abiotic and biotic variables, such as temperature, drying, and predators and these variables can also control the body size of emergent insects. Despite their importance, these variables can change rapidly during drought conditions as water temperatures rise, surface area decreases and predator densities increase. During 2018, the Konza Prairie Biological Station experienced a record drought: flow ceased in the lower reaches of Kings Creek for the first time in over 40 years of observation, leaving a series of isolated pools. We studied how the drought affected aquatic insect emergence in 12 of these pools via elevated temperatures, decreased surface area, and concentration of predators (e.g. fishes and crayfish) over a four‐week period. We returned in 2020 and sampled emergence in the same pools over 2 weeks under non‐drought conditions to compare emergence between drought and non‐drought conditions. We found three overall patterns: (1) rates of areal emergence abundance and biomass (number or mg DM m ⁻² d ⁻¹ ) did not differ between drought and non‐drought conditions. In contrast, pool‐scale emergence abundance, but not biomass (number or mg DM pool ⁻¹ d ⁻¹ ), was lower during drought conditions; (2) average midge body size was larger during the drought relative to the non‐drought conditions; (3) environmental variables (e.g. temperature, pool surface area, predator biomass) were not predictive of emergence during drought and non‐drought conditions. Fewer, but larger emergent midges (as seen under drought conditions) may represent a higher quality resource for terrestrial consumers than many smaller midges due to increased per‐capita energy yield. However, due to the overall decrease in water availability throughout the stream network, the overall emergence flux was concentrated in reaches with remaining water during the drought, making pools emergence subsidy hotspots. Overall, these contrasting responses underscore the complex nature of community responses to shifting climatic conditions.

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Conceptual diagram and results summary of mechanisms by which higher gizzard shad relative abundances could lead to increased phytoplankton and decreased zooplankton abundance. Open black arrows represent responses to increased gizzard shad abundances and arrow size indicates predicted relationship strength. First, TN and TP would both be positively associated with gizzard shad relative abundance, but TP would increase at a faster rate due to P excretion by gizzard shad, resulting in a decline in N:P with increasing gizzard shad relative abundance. These effects on nutrient availability should stimulate phytoplankton production, particularly of N-fixing cyanobacteria, because of reduced water column N:P conditions. Second, zooplanktivory by gizzard shad should increase with abundance, resulting in both a shift toward smaller taxa and reduced rates of herbivory by zooplankton, leading to an increase in phytoplankton abundance. Finally, increases in toxic cyanobacteria might further reduce zooplankton abundance and decrease herbivory. Color of horizontal arrows reflects results from this study, as indicated in the legend
Map of 12 study impoundments in Kansas, USA (county borders are shown for reference). SFL = State Fishing Lake. All impoundments are managed for angling recreation by the Kansas Department of Wildlife & Parks (KDWP)
Plot of gizzard shad CPUE versus TN (top), TP (middle), and molar N:P ratios (bottom) by sampling month (left to right: June, August, October). Colors indicate impoundment. Trend lines were included if effects were significant at α = 0.05
Gizzard shad CPUE versus cyanobacteria abundance, green algae abundance, diatom abundance, and total phytoplankton abundance from 12 small Kansas impoundments sampled in June, August, and October 2017–2020. Colors indicate month sampled. Trend lines were included if effects were significant at α = 0.05
Gizzard shad CPUE versus cladoceran density, calanoid copepod density, cyclopoid copepod density, rotifer density, nauplii density, and total zooplankton density from 12 small Kansas impoundments sampled in June, August, and October 2017–2020. Trend lines were included if effects were significant at α = 0.05
Associations between gizzard shad Dorosoma cepedianum (Lesueur, 1818) relative abundances and limnological parameters in small impoundments

December 2024

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65 Reads

Hydrobiologia

Abundant gizzard shad Dorosoma cepedianum (Lesueur, 1818) are thought to contribute to phytoplankton blooms by translocating nutrients from sediments to the water column where they can be readily taken up by phytoplankton and by consuming herbivorous zooplankton that might control phytoplankton. To assess the influence of gizzard shad relative abundance on lentic ecosystems, we sampled 12 small impoundments located in the Great Plains, USA over 4 years. We used linear mixed models to test for associations with limnological characteristics, including total nitrogen (TN) and total phosphorus (TP), zooplankton densities, and phytoplankton abundances. Gizzard shad relative abundance was associated with elevated TN and TP and a general reduction in zooplankton densities. There was substantial within-lake temporal variation in gizzard shad abundance across sampling months, with a negative association between TP and gizzard shad abundance in June but a positive association in August. We did not provide evidence that gizzard shad relative abundance was associated with cyanobacterial abundance or total phytoplankton abundance. The lack of a relationship between these factors might have been obscured by the discontinuous polymictic mixing regimes of the study impoundments, the rapid turnover of phytoplankton, and other drivers, such as variable nutrient runoff across our study impoundments.



Individual return patterns of spawning flannelmouth sucker (Catostomus latipinnis) to a desert river tributary

November 2024

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93 Reads

Tributaries provide temporal and spatial habitat heterogeneity in river networks that can be critical for parts of the life history of a species. Tributary fidelity can benefit individual fish undergoing spawning migrations by reducing time and energy spent exploring new areas and leveraging previous experience, but anthropogenic activities that fragment or degrade these systems can eliminate those benefits. We used multistate models based on passive integrated transponder (PIT) detection data from 2013 to 2023 to estimate the proportion of flannelmouth suckers (Catostomus latipinnis) migrating to a tributary, McElmo Creek, from the mainstem San Juan River for spawning. Survival varied among years and among states. The top model for migration probability included sex, with males slightly more likely to migrate (0.93 vs 0.90), and the next model identified interannual variation in migration probability ranging from 0.875 to 0.999 across years, indicating high site fidelity. Individuals showed consistency in relative arrival timing across years, with the highest correlation generally during years with greater spring discharge and extended tributary residence time. Successful tributary spawning may be important for the maintenance of the mainstem San Juan River flannelmouth sucker population, but site fidelity may be maladaptive where tributaries are vulnerable to human alterations.


Handling effects on dispersal of PIT ‐tagged Flannelmouth Sucker

October 2024

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28 Reads

North American Journal of Fisheries Management

Objective Handling and tagging migrating fish might alter their behavior, limiting inference from mark–recapture studies. Posthandling flight of tributary spawning Flannelmouth Sucker Catostomus latipinnis was previously identified in Coal Creek in the upper Colorado River basin. Our objective was to determine if similar issues were present at McElmo Creek in the San Juan River basin. Methods We compared emigration timing of Flannelmouth Sucker that had been handled and tagged with passive integrated transponder tags during their tributary spawning run to individuals tagged in previous years and detected both entering and exiting the tributary. Linear mixed‐effects models were used to examine intrinsic and extrinsic factors contributing to exit timing. Result Sex and tagging year were associated with emigration timing, but handling did not result in posthandling flight from McElmo Creek. Females exited the tributary ~3 days before males, and larger fish emigrated earlier than smaller adults. Conclusion Differences in capture technique and timing, available spawning habitat, and fish motivation across river systems may contribute to differences in posthandling emigration of tributary spawning Flannelmouth Sucker.



Figure 4. Violin plots of the amount of time (minutes) individual passive integrated transponder (PIT)-tagged Bluntnose Minnows Pimephales notatus released into ponds that contained Largemouth Bass Micropterus salmoides (LMB) and ponds that did not (non-LMB) were redetected on an antenna per day in 2021. Plots distinguish different treatments and panels represent (A) all redetection periods and (B) redetection excluding period one. The large black dot represents the average time the fish was within range of the PIT antenna across all individuals and treatment ponds. The small transparent dots represent the raw data for each individual on each day. Notice the bimodal distribution represented in LMB treatments in both A and B.
Predator Presence Influences Survival and Behavior of Translocated Stream Fish in Ponds

June 2024

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65 Reads

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1 Citation

Journal of Fish and Wildlife Management

Small artificial impoundments such as farm ponds have recently been recognized as potential habitat for threatened native fish species. However, factors influencing translocation or colonization success into these environments, including connectivity to stream networks and interactions with existing fish community, are largely unknown. In this study we conducted a controlled experiment to quantify the influence of piscivorous Largemouth Bass Micropterus salmoides on the survival of a translocated native minnow species that we used as a surrogate for federally endangered Topeka Shiner Notropis topeka. We translocated or released 100 Bluntnose Minnow Pimephales notatus into each replicate treatment ponds with and without Largemouth Bass in the summers of 2020 and 2021. Each minnow was implanted with a passive integrated transponder (PIT) tag. Translocated populations were monitored using stationary and mobile passive integrated transponder antennas and estimates of apparent survival and probability of detection for each pond were derived from open population mark-recapture models. Apparent survival was nearly two times higher in ponds without bass suggesting predation by bass leads to higher mortality. Additionally, probability of detection was nearly 10 times higher in ponds without bass, suggesting reduced movement of translocated minnows when bass were present. While the direct effect of mortality impacts translocated populations, the indirect effect of altered behavior may also be impactful on translocation success. These results confirm that Largemouth Bass can limit the success of translocated minnow species.


Study area map of the San Juan River and major tributaries in the Four Corners region of the southwest United States (inset gray shading). Vertical lines at 0 river kilometers (rkm) and near 307.1 rkm represent either complete or seasonal barriers to fish movement. Arrows depict installed passive integrated transponder (PIT) tag antennas. Other fish detection and capture efforts occurred annually between rkm 0 and 307.1, with effort differing among years. For the multistate model, we considered fishes below the waterfall (rkm 0) as state 1 and above the waterfall as state 3 with an intermediate state for fishes being translocated, state 2. Photo credit: Casey A. Pennock.
Annual counts of unique individuals of four species detected below (1 January to 15 April) and captured and translocated above a waterfall barrier on the San Juan River, USA, from 2016 to 2021. The y‐axis is scaled with a log10‐transformation.
(a) The number of individual fishes detected at different locations in the San Juan River or McElmo Creek upstream of the Piute Farms Waterfall (river kilometers [rkm] 0), Utah, USA, within a year of being translocated. The dashed vertical lines represent the location of the mainstem passive integrated transponder tag antenna near McElmo Creek (186.4 rkm) and the most upstream in‐stream barrier in the San Juan River (307.1 rkm) downstream of Navajo Reservoir. Note the y‐axis in panel (a) is scaled with a log10‐transformation. (b) Modeled mean estimates (and 95% CI) of the most upstream encounter location upstream of the Piute Farms Waterfall within a year of translocation. Estimates are from a linear mixed‐effects model including the fixed effect of species and random effects of translocation year (Table 2).
Multistate model estimates of survival (φ) probabilities by species for translocated (solid circles) and non‐translocated (open circles) fishes above and below the Piute Farms Waterfall on the San Juan River. Error bars indicate 95% CIs, and estimates are scaled to represent annual rates.
Multistate model estimates of transition (ψ) probabilities by species for translocated (solid circles) and non‐translocated (open circles) fishes above and below the Piute Farms Waterfall on the San Juan River. Error bars indicate 95% CIs, and estimates are scaled to represent annual rates.
Translocation in a fragmented river provides demographic benefits for imperiled fishes

May 2024

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148 Reads

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3 Citations

Fragmentation isolates individuals and restricts access to valuable habitat with severe consequences for populations, such as reduced gene flow, disruption of recolonization dynamics, reduced resiliency to disturbance, and changes in aquatic community structure. Translocations to mitigate the effects of fragmentation and habitat loss are common, but few are rigorously evaluated, particularly for fishes. Over six years, we translocated 1215 individuals of four species of imperiled fish isolated below a barrier on the San Juan River, Utah, USA, that restricts access to upstream habitat. We used re‐encounter data (both passive integrated transponder tag and telemetry detections and physical recaptures) collected between 2016 and 2023, to inform a spatially explicit multistate mark–recapture model that estimated survival and transition probabilities of translocated and non‐translocated individuals, both below and above the barrier. Individuals of all four species moved large (>200 km) distances upstream following translocation, with the maximum upstream encounter distance varying by species. Results from the multistate mark–recapture model suggested translocated fish survived at a higher rate compared with non‐translocated fish below the barrier for three of the four species. Above the barrier, translocated individuals survived at similar rates as non‐translocated fish for bluehead sucker (Catostomus discobolus) and flannelmouth sucker (Catostomus latipinnis), while survival rates of translocated endangered Colorado pikeminnow (Ptychocheilus lucius; mean, 95% CI: 0.75, 0.55–0.88) and endangered razorback sucker (Xyrauchen texanus; 0.86, 0.75–0.92) were higher relative to non‐translocated individuals (Colorado pikeminnow: 0.52, 0.51–0.54; razorback sucker: 0.75, 0.74–0.75). Transition probabilities from above the barrier to below the barrier were generally low for three of the four species (all upper 95% CI ≤ 0.23), but they were substantially higher for razorback sucker. Our results suggest translocation to mitigate fragmentation and habitat loss can have demographic benefits for large‐river fish species by allowing movements necessary to complete their life history in heterogeneous riverscapes. Further, given the costs or delays in providing engineered fish passage structures or in achieving dam removal, we suggest translocations may provide an alternative conservation strategy in fragmented river systems.


Capture-translocation restores spawning migration connectivity of Razorback Suckers in the fragmented San Juan River

April 2024

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29 Reads

Transactions of the American Fisheries Society

Objective Barriers to movement negatively affect population vital rates of riverine fishes that rely on connected migratory routes to complete components of their life cycle, such as reproduction and recruitment. In the southwestern United States, decades of water diversion, construction of large impoundments, and loss of floodplain habitats have all contributed to highly fragmented riverscapes. A capture–translocation strategy was implemented for Razorback Suckers Xyrauchen texanus in the San Juan River to mitigate the negative effects of two barriers while precluding the upstream movement of nonnative species. We hypothesized that translocated individuals would remain upstream of barriers during the spawning season and that aggregations of translocated Razorback Suckers would be identified upstream in spawning habitats. Methods We used radiotelemetry to assess movement of Razorback Suckers after translocation above the two barriers. We deployed fixed remote radio receivers to determine residency time above each barrier and conducted mobile telemetry surveys to monitor upstream destinations after translocation. Result Although most Razorback Suckers returned downstream of barriers within 2 months of translocation, we provide evidence that most individuals remained upstream long enough to successfully spawn. After translocation above the Piute Farms Waterfall, 80% of individuals remained upstream for 26 days in 2020 and for 23 days in 2021. Further upstream (307 km), at a weir operated by the Public Service Company of New Mexico, 80% of translocated individuals remained above the barrier for 37 days in 2021 and for 25 days in 2022. After fish translocation above both barriers, we observed upstream movements ranging from 2 to 262 km and we detected distinct aggregations within the expected spawning season. Conclusion Although translocation efforts seasonally reconnect migratory routes for a proportion of the population and may increase spawning potential, other conservation actions are likely still needed to improve recruitment conditions for juvenile fish.


Macroinvertebrate density at the shell (a), patch (b), and mussel bed (c) spatial scale. Species Amblema plicata and Actinonaias ligamentina are abbreviated AP and AL, respectively. All continuous axes are transformed: all axes are log10 transformed except the mussel biomass of mussel beds axis (c), which is loge(1 + x) transformed. Asterisks (*) indicate live treatments had higher macroinvertebrate density than sham treatments (ANOVA F1,28 = 4.51, P < 0.04). For the boxplots, the middle line represents the median macroinvertebrate density, the edges of the box represent the 25% and 75% percentiles, and the lines represent the largest or smallest value. At the patch scale, control patch (CTRL) density mean is indicated at the circle, with the line indicating the 1 standard deviation from the mean
Canonical Correspondence Analysis of macroinvertebrate communities and environmental factors at the shell (a), patch (b), and mussel bed (c) scale. A Partial CCA with a conditional spatial variation was used at the mussel bed scale to control for autocorrelation among samples. Factor constraints are indicated as centroids with underlined, navy text while linear combinations of quantitative measures are indicated with vectors and bold, red text. In the shell CCA (a), discharge is included in the environmental factors at the origin. Points represent species; black, labeled points are discussed within the text. Percent of the total variation accounted for by the CCA axis is displayed. Species Amblema plicata and Actinonaias ligamentina are abbreviated AP and AL, respectively. (For interpretation of the references to color in this figure legend, the reader is referred to the web version of this article.)
Percentage of macroinvertebrate community variation explained by the environmental variables. The pie-charts depict the locational (mussel bed scale only), explained, and unexplained variation within the macroinvertebrate dataset based on the CCA, with the variation partitioned by mussel variables (biomass and treatment), the environment (discharge, chlorophyll a concentration, and substrate), and the interaction of the two indicated by the Venn diagrams. Overlap between groups represents shared variation
Habitat engineering effects of freshwater mussels in rivers vary across spatial scales

Hydrobiologia

Ecosystem engineers alter habitat and resource availability within ecosystems, but the magnitude of these effects depends on abiotic context and spatial scale. We examined how the effects of freshwater mussels, an ecosystem engineer, changed with spatial scale. We combined a field enclosure experiment and comparative field study to evaluate associations among mussels and macroinvertebrate communities across three spatial scales: mussel individuals (~ 0.01 m²), patches of mussels (0.25 m²), and large aggregations of many mussel patches (mussel beds, ~ 1000 m²). We used canonical correspondence analysis and variation partitioning to evaluate how mussel abundance, food availability, substrate heterogeneity, and flow influenced macroinvertebrate communities. We found that mussels’ influence on macroinvertebrate communities differed among spatial scales. At the smallest scale, macroinvertebrate density increased on the shells of live mussels, likely due to mussel influences on food availability to grazers. At the patch scale, we found no mussel effects, likely because they were overridden by a flood event. At the mussel bed scale, macroinvertebrate communities were primarily controlled by flow and secondarily by food availability. As such, the continued loss of freshwater mussels means the loss of habitat creation and food provisioning for other aquatic groups, and alteration of facilitation landscapes within streams.


Citations (74)


... The declining quality and quantity of natural freshwater environments has expedited the search for additional habitats to support threatened small-bodied fish conservation and recovery (Chester & Robson, 2011;Humphries & Baldwin, 2003). One asset to fish conservation currently underutilized globally is the broadly distributed and abundant farm dam network (Downing, 2010;Downing et al., 2006;Pfaff et al., 2022). There are >1.76 million farm dams in Australia (Malerba et al., 2021), with >1 million located in south-eastern Australia, a region encompassing ~80% of Australia's threatened fishes (Lintermans, 2023). ...

Reference:

Farm dams: A valuable interim step in small‐bodied threatened fish conservation
Predator Presence Influences Survival and Behavior of Translocated Stream Fish in Ponds

Journal of Fish and Wildlife Management

... Given that many threatened fishes now only occur in remnant populations of a once much wider distribution, the establishment of additional populations through conservation translocations is a priority management action for many species (Lintermans et al. 2015;Allan et al. 2018Allan et al. , 2022Zukowski et al. 2021;Garnett et al. 2022;Gaywood et al. 2022). Establishment of additional populations means risks of extinction are reduced, and the localised effects of bushfire, predator incursion or stream drying are offset at the population level by increased geographical coverage, while also increasing overall population size of these threatened species (Ellender and Weyl 2015;Gaywood et al. 2022;Pennock et al. 2024). The challenge for management of threatened species is prioritising often-limited funding and resources allocated towards their recovery (Kearney et al. 2023;Lintermans et al. 2024). ...

Translocation in a fragmented river provides demographic benefits for imperiled fishes

... Controlled experiments were conducted in , 2025, Vol. 50, No. 2 • 69 two Kansas impoundments to measure effects of live sonar on catches of crappies and Blue Catfish Ictalurus furcatus by casual anglers and no difference was detected between live sonar users and nonusers for either species (Neely et al., 2023a(Neely et al., , 2023b. ...

Effects of live‐imaging sonar on Blue Catfish angler success, perception, and behavior

North American Journal of Fisheries Management

... A larger fish upstream pattern (LFUP) has been frequently described around the world (e.g. Jellyman & Graynoth, 1994;Hughes, 1999;Mazzoni et al., 2004;Perkin et al., 2023). In such cases, older, reproductively mature individuals often dominate upstream reaches, while juveniles are found at downstream sites (Hughes, 1999;Vitule et al., 2008). ...

Why are larger fish farther upstream? Testing multiple hypotheses using Silver Chub in two Midwestern United States riverscapes
  • Citing Article
  • August 2023

North American Journal of Fisheries Management

... Flannelmouth sucker (Catostomus latipinnis) is a long-lived species that uses tributaries as a part of its reproductive strategy. Some flannelmouth suckers migrate into tributaries for spring spawning 16,17 , exhibiting a partial migration strategy, with probability of tributary use being greatest for fish closer to tributaries 18 . Large spawning aggregations, such as those in tributaries, may increase mate encounter rate and fertilization success, allow for mate selection, or reduce predation rates on adults and offspring 19 . ...

Migration timing and tributary use of spawning flannelmouth sucker (Catostomus latipinnis)

... Early work with aquatic macroinvertebrates suggested movements should be biased in an upstream direction to account for downstream drift of propagules [19], but later work built on simulations suggested any upstream dispersal component may be sufficient for population persistence [63,64]. Observations of downstream movement by hatchery-reared RGSM following release are common [42,44,65], as well as by other hatchery-reared species [66,67]. When we excluded detections within the first week of release to account for this immediate downstream tendency, movement patterns were largely unchanged, and movements were still consistently more common in the downstream direction. ...

Movement, Not Survival, Differs Between Wild and Hatchery‐Reared Imperiled Desert Fishes
  • Citing Article
  • July 2023

North American Journal of Fisheries Management

... Fish released in the morning (9:30-11:30) experience lower water temperatures compared to those released in the afternoon (14:30-16:30). The water temperature has a negative impact on the St value, as higher temperatures may affect energy allocation and behavioral patterns, thereby inhibiting migration speed and migratory capacity [39]. At the same time, higher water levels are often associated with higher water flow velocities, which increase the difficulty for fish to overcome hydraulic resistance. ...

Water temperature predicts razorback sucker Xyrauchen texanus spawning migrations

Environmental Biology of Fishes

... However, accurately modeling spring environmental flows is not possible using StateMod with a monthly timestep. Instead, our analysis focuses on low-flow periods in August, September, and October when streamflow depletions from agricultural diversions can endanger native fish populations (Dibble et al., 2023;US FWS, 1999;US FWS, 2009). For more details on environmental flow requirements, see Section S4 in Supporting Information S1. ...

Assessment of Potential Recovery Viability for Colorado Pikeminnow Ptychocheilus lucius in the Colorado River in Grand Canyon

Journal of Fish and Wildlife Management

... For fish residing within watersheds whose freshwater flows are diverted and otherwise altered to support large human populations, growth rate models have the potential to contribute to the oft contentious debate of just how much water they need to persist. The challenges of native fish conservation in arid areas like the North American west are only expected to grow in light of ongoing climate changes (Gido et al., 2023). ...

Megadroughts Pose Mega‐Risk to Native Fishes of the American Southwest

Fisheries

... They also favor indirect disturbances caused by increased human activities, such as increased sediment, nutrient and pollutants/contamination inputs (White 2014;Turgeon et al. 2019;Linares et al. 2023). Furthermore, anthropogenically altered ecological conditions can facilitate biological invasions and serve as stepping stones for expanding already extant invasive species into new areas (Johnson et al. 2008;Bellard et al. 2013;Pfaff et al. 2023). ...

Community assembly of prairie farm ponds: build it and they will come, stock it and they won't