Abstract
Background
Freshwater ecosystems are amongst the most threatened habitats on Earth; nevertheless, they support about 9.5% of the known global biodiversity while covering less than 1% of the globe’s surface. A number of anthropogenic pressures are impacting species diversity in inland waters and, amongst them, the spread of invasive alien species is considered one of the main drivers of biodiversity loss and homogenisation in freshwater habitats.
Crayfish species are widely distributed freshwater invaders and, while alien species introductions occur mostly accidentally, alien crayfish are often released deliberately into new areas for commercial purposes. After their initial introduction, crayfish species can rapidly establish and reach high-density populations as a result of their adaptive functional traits, such as their generalist diet.
The Louisiana crayfish Procambarusclarkii (Girard, 1852) is globally considered one of the worst invaders and its impact on recipient freshwater communities can vary from predation and competition with native species, to modification of food webs and habitat structure and introduction of pathogens. Native to the south United States and north Mexico, P.clarkii has been introduced in Europe, Asia and Africa, determining negative ecological and economic impacts in the majority of invaded habitats where it became dominant within the receiving benthic food webs. Due to its flexible feeding strategy, P.clarkii exerts adverse effects at different trophic levels, ultimately affecting the structure and dynamics of invaded food webs. It is, therefore, paramount to evaluate the ecological consequences of P.clarkii invasion and to quantify its impact in a spatially explicit context.
New information
In the past decades, the analysis of stable isotopes of carbon, nitrogen and other elements has become a popular methodology in food web ecology. Notably, stable isotope analysis has emerged as a primary tool for addressing applied issues in biodiversity conservation and management, such as the assessment of the trophic ecology of non-indigenous species in invaded habitats. Here, we built two geo-referenced datasets, resolved respectively at the population and individual scale, by collating information on δ13C and δ15N values of P.clarkii within invaded inland waters. The population-scale dataset consists of 160 carbon and nitrogen isotopic values of the Louisiana crayfish and its potential prey, including living and non-living primary producers and benthic invertebrates. The dataset resolved at individual scale consists of 1,168 isotopic records of P.clarkii. The isotopic values included within the two datasets were gathered from 10 countries located in Europe, Asia, Africa and North America, for a total of 41 studies published between 2005 and 2021. To the best of the authors’ knowledge, this effort represents the first attempt to collate in standardised datasets the sparse isotopic information of P.clarkii available in literature. The datasets lend themselves to being used for providing a spatially explicit resolution of the trophic ecology of P.clarkii and to address a variety of ecological questions concerning its ecological impact on recipient aquatic food webs.
Keywords: invasive species, Louisiana crayfish, red swamp crayfish, stable isotopes, ecological impact
Introduction
Crayfish species are amongst the most successful and widespread freshwater invaders worldwide (Capinha et al. 2010, Gallardo et al. 2015). The crayfish ability for acting as keystone consumers feeding on a variety of trophic levels is one of the adaptive traits that lead the successful establishment of these crustaceans in non-native habitats (Lodge et al. 1994, Nyström et al. 1996). Invasive crayfish can determine trophic cascades and adverse effects on energy fluxes in invaded habitats and these crustaceans are often the largest and longest-living invertebrates of benthic food webs (Gherardi et al. 2011). The global distribution of crayfish species was once uneven, with 75% of the total number of species native to North and Central America (Gherardi 2007). Nowadays, owing to globalisation and international trade, an increasing number of crayfish species is widely distributed across continents as a consequence of both accidental human-mediated translocations and intentional introductions for commercial purposes (Lodge et al. 2012).
After the initial introduction, crayfish can quickly spread and colonise new habitats thanks to their dispersal ability, including the capacity of some species to travel long distances and even overland at times (Souty-Grosset et al. 2016), such as in the case of the Louisiana crayfish (or red swamp crayfish) Procambarusclarkii (Girard, 1852). Similarly to other crayfish, P.clarkii has a flexible diet and it can also tolerate a broad range of environmental conditions including extreme variations in oxygen level, water salinity and acidity and prolonged droughts (Alcorlo et al. 2004, Loureiro et al. 2015). Despite the relatively small native range, encompassing the southern USA and north-eastern Mexico, P.clarkii has colonised all continents, except Australia and Antarctica and it is globally considered one of the worst invasive species (Loureiro et al. 2015). Due to its economic importance, P.clarkii has been deliberately introduced in different countries for aquaculture and fishing activities and it became invasive for its capacity of rapidly colonising new areas reaching high population densities (Hänfling et al. 2011).
The impact of P.clarkii spans from predation and competition with native species, to disruption of food webs and habitat structure and introduction of pathogens (Souty-Grosset et al. 2016). Introduced populations of the Louisiana crayfish have determined a reduction of freshwater biodiversity with a negative impact on several taxonomic groups such as amphibians (Ficetola et al. 2011, Ficetola et al. 2012), macroinvertebrates (Correia and Anastácio 2008) and macrophytes (Carreira et al. 2014). Furthermore, P.clarkii is one of the vectors of the crayfish plague, which is lethal for freshwater crayfish from regions outside North America and has already determined a number of local extinctions in Europe (Bland 2017, Manenti et al. 2018, Martín-Torrijos et al. 2019). The economic impact associated with the management and control of introduced populations of P.clarkii is also considerable for the agricultural and fishery sectors (de Moor 2002, Anastacio et al. 2005).
As an opportunistic feeder (Alcorlo and Baltanás 2013), but also as an important prey item of freshwater top predators (Soto et al. 2016), P.clarkii is expected to play a crucial role in shaping the structure and dynamics of invaded aquatic food webs (Alcorlo and Baltanás 2013). Traditionally, stomach content analyses have been used to investigate the trophic habits of the species and its adaptation strategy to newly-invaded environments (Hyslop 1980). Over the last three decades, stable isotope analysis of nitrogen and carbon (and more recently of hydrogen; Soto et al. 2011) has been proven as an extremely useful methodology in trophic ecology because it can provide quantitative, standardised and reliable information on the dietary habits of species - including bioinvaders - and, consequently, it can be used to estimate the trophic impact of invasive species on local communities (Vander Zanden et al. 1999, Rush et al. 2012, Mancinelli and Vizzini 2015).
General description
Purpose
The two datasets presented herein collate geo-referenced δ13C and δ15N values of P.clarkii and its potential prey in invaded inland and brackish waters. The dataset resolved at population scale includes mean values and standard deviations of δ13C and δ15N for the Louisiana crayfish populations and their potential animal and vegetal prey. The individual-scale dataset collates isotopic values of single specimens of P.clarkii, similarly to the dataset with stable isotopes of the Atlantic blue crab Callinectessapidus published by Di Muri et al. (2022). In the two datasets, isotopic values are expressed in standard delta notation (permil [‰]), indicating the deviation from atmospheric nitrogen and from Vienna Pee Dee Belemnite (VPDB) limestone, respectively, as scale-defining standards for nitrogen and carbon (Hood-Nowotny and Knols 2007). Specifically, δ15N or δ13C values are calculated as [(RSample/RStandard) – 1] × 1000, where R is the ratio of the heavy vs. the light isotope (i.e. 15N/14N or 13C/12C).
The two datasets can be used for a variety of comparative analyses including the calculation of the trophic position of the Louisiana crayfish (population-scale dataset) and the calculation of metrics and descriptors of its isotopic niche (individual-scale dataset) accounting for isotopic differences in the baseline at each location. Both are examples of input files used for the Crustaceans workflow of the LifeWatch ERIC Internal Joint Initiative. The analytical workflow aims at identifying regional-scale climatic predictors of the trophic position of the two model invasive crustaceans, i.e. P.clarkii and the Atlantic blue crab C.sapidus.
Project description
Title
LifeWatch ERIC Internal Joint Initiative - Functional biogeography of invaders: the case of two widely-distributed omnivorous crustaceans (https://bit.ly/iji-crustaceans)
Personnel
Cristina Di Muri, Giorgio Mancinelli, Ilaria Rosati, Lucia Vaira
Study area description
The geographic coverage of the two datasets includes Europe, Asia, Africa and North America (Fig. 1). In the population-scale dataset, the westernmost site is located in Hawaii, the northernmost in the Netherlands, the easternmost in Japan and the southernmost in Kenya. The majority of the study sites are located in Europe (18 out of a total of 39 locations; Table 1). For the individual-scale dataset, the westernmost site is located in Washington State (USA), the northernmost in France, the easternmost in China and the southernmost in Kenya. As for the population-scale dataset, the majority of the study sites are located in Europe (five out of a total of eight locations; Table 1).
Figure 1.
Distribution map of the locations included in the datasets. The locations represent the study sites where the population- and individual-scale isotopic values of Procambarusclarkii and its potential prey were collated (in red and in blue, respectively).
Table 1.
List of study sites included in the datasets where isotopic data of Procambarusclarkii and its prey were collected. For each study site, information on country, location, habitat, sampling year and associated reference IDs are reported (full reference list in Suppl. material 1). The column "Resolution" indicates whether isotopic data of Procambarusclarkii are available at population- or individual-scale.
Country | Locality (no. of sites) | Habitat | Year sampling | Resolution | Reference ID |
---|---|---|---|---|---|
USA | Nevada, Ash Meadows National Wildlife Refuge (1) | Spring | 1999-2000 | Population | 1 |
Japan | Lake Biwa Basin (1) | River | 2003 | Population | 2 |
USA | Hawaii, Hainako stream (2) | Stream | 2006 | Population | 3 |
France | Garonne River Basin (1) | River | 2007-2008 | Population | 4 |
Japan | Namegawa (1) | Pond | 1999-2000 | Population | 5 |
USA | Hawaii, Opaekaa stream (1) | Stream | 2008-2009 | Population | 6 |
France | Rhone River Basin (1) | Stream | 2009 | Population | 7 |
Japan | Shizuoka Prefecture (1) | Pond | 2009 | Population | 8 |
The Netherlands | Lake Terra Nova (1) | Lake | 2011 | Population | 10 |
Kenya | Lake Navaisha (1) | Lake | 2001-2008 | Individual | 11 |
Japan | Lake Biwa (2) | Lake | 2007 | Population | 12 |
China | Lake Chaohu (1) | Lake | 2003 | Population | 13 |
Spain | Guadalquivir River Basin (3) | River | 2000-2001 | Individual | 14 |
France | Aquitaine (3) | Lake/River | 2009-2010 | Population | 15 |
Japan | Asahi River (1) | River | 2009 | Population | 16 |
USA | Nevada, Ash Meadows National Wildlife Refuge (1) | Spring | 2011-2012 | Population | 17 |
Japan | Lake Teganuma (1) | Lake | 2009 | Population | 18 |
China | Lake Gucheng (1) | Pond | 2013 | Population | 19-20 |
Spain | Ebro River Basin (1) | Reservoir | 2006 | Population | 9-21 |
Japan | Lake Izunuma (1) | Lake | 2006 | Population | 22 |
France | Garonne River Basin (15) | Lake | 2012 | Individual | 23 |
USA | Washington State (5) | Lake | 2009 | Population | 24 |
Spain | Ebro River Basin (1) | Lagoon | 2015-2016 | Population | 25 |
Italy | Lake Trasimeno and Lake Bolsena (2) | Lake | 2014 | Population | 26 |
France | Garonne River Basin (1) | Lake | 2014 | Individual | 27 |
USA | Washington State (5) | Lake | 2014 | Individual | 27 |
Italy | Arno River (1) | River | 2018 | Population | 28 |
Spain | Lake Arreo (1) | Lake | 2017 | Individual | 29-30 |
France | Garonne River Basin (7) | Lake | 2014 | Individual | 31 |
Portugal | Quarteira River Basin (2) | Stream | 2015 | Population | 32 |
China | Huangshui River Basin (1) | Reservoir | 2015-2016 | Population | 33 |
Japan | Lake Izunuma (1) | Pond | 2008 | Population | 34 |
Spain | Albufera de València (1) | Marsh | 2018 | Population | 35 |
Italy | Monterotondo (1) | Pond | 2016 | Population | 36 |
France | Garonne River Basin (3) | Stream | 2019 | Population | 37 |
France | Aquitaine (3) | Lake | 2015 | Population | 38 |
Japan | Tojooka Basin (1) | Pond | 2014-2016 | Population | 39 |
Hungary | Danube River Basin (1) | Stream | 2018 | Population | 40 |
China | Lake Dongting (28) | Lake | 2017 | Individual | 41 |
Design description
Each isotopic record included in the datasets is associated with the corresponding geographical and temporal information of the sampling event including country, location, geographical coordinates (latitude and longitude in decimal degrees), type of habitat and sampling date. In the dataset resolved at population scale, δ13C and δ15N values of putative prey are specified together with other biological features, such as the invasive or native nature of the species for each location. Stable isotope values can be used for downstream analyses as, for example, the calculation of the trophic position (see Di Muri et al. 2022 for details). In the dataset resolved at individual scale, no information on putative prey is included, as they can be obtained from the population-scale dataset. Isotopic values included in the individual-scale dataset can be used, for example, to estimate isotopic spatial niche metrics, including the convex hull area, the nearest-neighbour distance and the distance to centroid (Jackson et al. 2011, Jackson et al. 2012 after Layman et al. 2007).
Funding
LifeWatch ERIC Internal Joint Initiative
Sampling methods
Study extent
The literature search was concluded on 17 January 2022.
Sampling description
The Google Scholar engine was used to search for relevant bibliographic sources using the keywords "Procambarusclarkii" and "stable isotopes" and a total of 651 publications were returned. Peer-reviewed articles and grey literature material were individually inspected in order to identify the bibliographic sources with stable isotope information of the Louisian crayfish and of its potential prey in tabular or graphical format; 41 studies performed in both freshwater and transitional environments and published between 2005 and 2021 were ultimately selected (Table 1; Suppl. material 1). For data extraction, figures were digitised after a five-fold enlargement and converted to numerical form using the WebPlotDigitizer graph capture software. The quality control of stable isotope data extracted from figures was performed by comparing data available in both numerical and graphical form.
Quality control
Only records with specified locations were included in the datasets. The location accuracy was checked using Google Earth and, when geographical coordinates were not explicit, the maps of the study sites included in the publications were used to retrieve them. Geographical coordinates were converted to decimal degrees when not originally specified as such. A taxonomic check was additionally performed using the World Register of Marine Species, the GBIF Backbone Taxonomy and the Integrated Taxonomic Information System to check the current accepted scientific names of all taxa included in the datasets.
Step description
Procambarusclarkii is an omnivore species feeding on vegetal (e.g. algae and leaf detritus) and animal prey including invertebrates (e.g. insect larval stages, oligochaetes, gastropods) and vertebrates (e.g. amphibians and fish) depending on resources availability (Alcorlo et al. 2004, Loureiro et al. 2019).
In general, primary producers, including living (e.g. macrophytes, periphyton etc.) and non-living (i.e. detritus) organisms were preferentially used as reference for the selection of the baseline species included in the population-scale dataset. In few instances, herbivorous gastropods, aquatic larval stages of insects and other invertebrates occurring at the study sites and characterised by a trophic position = 2 were chosen (i.e. Reference ID 12 in Suppl. material 1: Stenopsychemarmorata [Shin et al. 2012]; Reference ID 33 in Suppl. material 1: Macrobrachiumnipponense [Zhang et al. 2020]; Reference ID 35 in Suppl. material 1: maggots of Ephydra sp. [Bradley and Herbst 1994]; Reference ID 3 in Suppl. material 1: larvae of Cheumatopsycheanalis [Zuellig et al. 2004]). Only in two cases, two species of vertebrate predators with a trophic position = 3 were included (i.e. Reference ID 34 in Suppl. material 1: larval stage of the odonate Epophthalmiaelegans [Yamada and Urabe 2021]; Reference ID 39 in Suppl. material 1: larval stage of the hydrophilid beetle Hydrocharaaffinis [Baek et al. 2014]).
The population-scale dataset additionally includes the sample size of each isotopic record as well as the standard deviations of mean δ13C and δ15N values. When the standard deviations were not available (i.e. Reference ID 10 in Suppl. material 1), we have used the modified Range Rule to estimate them, as described in Ramirez and Cox (2012) and as reported below:
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Geographic coverage
Description
The datasets gather isotopic values of P.clarkii and its potential prey in invaded lotic and lentic habitats across 10 countries (Table 1). Overall, the study sites were distributed across 27 locations in France mostly located in the Garonne floodplain, nine locations in the USA, seven in Japan, four in China and in Italy, two in Spain and one in Hungary, Kenya, Portugal and the Netherlands.
Taxonomic coverage
Description
The dataset resolved at individual scale includes only carbon and nitrogen isotopic values of P.clarkii, whereas, the population-scale dataset is a collection of mean isotopic values of P.clarkii and its potential prey, including vegetal and animal prey.
Taxa included
Rank | Scientific Name | |
---|---|---|
class | Gastropoda (Cuvier, 1797) | |
order | Amphipoda | |
order | Ephemeroptera | |
family | Asellidae | |
family | Chironomidae | |
family | Cyrenidae (Gray, 1840) - Corbiculidae in the original publication | |
family | Culicidae (Meigen, 1818) | |
family | Lymnaeidae (Rafinesque, 1815) | |
family | Sialidae | |
genus | Corbicula (Megerle von Mühlfeld, 1811) | |
genus | Dreissena (Beneden, 1835) | |
genus | Echinogammarus (Stebbing, 1899) | |
genus | Ephydra | |
genus | Gammarus (J. C. Fabricius, 1775) | |
genus | Myriophyllum L. | |
genus | Poa L. | |
genus | Potamogeton L. | |
genus | Spirogyra (Link, 1820) | |
species | Alismaplantago-aquatica L. | |
species | Gabbialongicornis (Benson, 1842) - Alocinmalongicornis in the original publication | |
species | Anodontaanatina (Linnaeus, 1758) | |
species | Asellusaquaticus (Linnaeus, 1758) | |
species | Sinotaiaquadrata (Benson, 1842) - Bellamyaaeruginosa in the original publication | |
species | Cipangopaludinachinensis (Gray, 1833) - Bellamyachinensis in the original publication | |
species | Cheumatopsycheanalis (Banks, 1903) | |
species | Corbiculafluminea (O. F. Müller, 1774) | |
species | Dreissenapolymorpha (Pallas, 1771) | |
species | Epophthalmiaelegans (Brauer, 1865) | |
species | Hydrocharaaffinis (Sharp, 1873) | |
species | Macrobrachiumnipponense (De Haan, 1849) | |
species | Menthaaquatica L. | |
species | Phragmitesaustralis (Cav.) Trin. ex Steud. | |
species | Pomaceamaculata (Perry, 1810) | |
species | Potentillaanserina L. | |
species | Ricciafluitans L. | |
species | Semisulcospirareiniana (Brot, 1876) | |
species | Sparganiumerectum L. | |
species | Stenopsychemarmorata (Navas, 1920) | |
species | Radixauricularia (Linnaeus, 1758) - Radixauriculariajaponica in the original publication |
Usage licence
Usage licence
Creative Commons Public Domain Waiver (CC-Zero)
IP rights notes
This work is licensed under a Creative Commons Attribution (CC-BY) 4.0 Licence.
Data resources
Data package title
Individual and population-scale carbon and nitrogen isotopic signatures of Procambarusclarkii in invaded freshwater ecosystems.
Resource link
https://doi.org/10.48372/d25219d3-fe11-4052-879a-eb2e15ca295c
Number of data sets
2
Data set 1.
Data set name
Population-scale carbon and nitrogen isotopic signatures of Procambarusclarkii in invaded freshwater ecosystems.
Data format
csv
Download URL
https://dataportal.lifewatchitaly.eu/view/urn%3Auuid%3A18a8256c-0e31-4800-af5b-958ea88faf34
Description
A description of the dataset is provided below. Wherever possible, the dataset attributes were labelled using standard vocabularies and terms harvested from Darwin Core, LifeWatch ERIC Ecoportal and NERC Vocabulary Server.
Data set 1.
Column label | Column description |
---|---|
catalogNumber | An identifier (preferably unique) for the record within the dataset or collection. |
associatedReferences | A list (concatenated and separated) of identifiers (publication, bibliographic reference, global unique identifier, URI) of literature associated with the Occurrence. |
country | The name of the country or major administrative unit in which the Location occurs. |
locality | The specific description of the place. |
habitat | A category or description of the habitat in which the Event occurred. |
eventDate | The date-time or interval during which an Event occurred. |
decimalLatitude | The geographic latitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic centre of a Location. Positive values are north of the Equator, negative values are south of it. |
decimalLongitude | The geographic longitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic centre of a Location. Positive values are east of the Greenwich Meridian, negative values are west of it. |
taxonName | Name of the biological entity, taxonomic group or lowest level of taxonomic rank that could be determined. |
establishmentMeans | Statement about whether an organism or organisms have been introduced to a given place and time through the direct or indirect activity of modern humans (https://dwc.tdwg.org/em/#dwcem_e). |
trophicRole | Statement specifying whether the species is a predator or a prey. |
d13C_VPDB_biota | The ratio of carbon 13 relative to carbon 12 in a biological organism identified elsewhere in the metadata, expressed in per mille and relative to the international reference Vienna Pee Dee Belemnite standard. |
SD_d13C_VPDB_biota | The square root of the average of the squares of deviations about the mean of a set of values of the specified measurement. |
d15N_biota | The ratio of nitrogen 15 relative to nitrogen 14 in a biological organism identified elsewhere in the metadata, expressed in per mille and relative to atmospheric air. |
SD_d15N_biota | The square root of the average of the squares of deviations about the mean of a set of values of the specified measurement. |
sampleSizeValue_d13C | A numeric value for the measurement of the size (number of samples) in a sampling event for the isotope of the chemical element carbon. |
sampleSizeValue_d15N | A numeric value for the measurement of the size (number of samples) in a sampling event for the isotope of the chemical element nitrogen. |
trophicLevel | Any of the feeding levels through which the passage of energy through an ecosystem proceeds; examples are photosynthetic plants, herbivorous animals and microorganisms of decay. |
Data set 2.
Data set name
Individual-scale carbon and nitrogen isotopic signatures of Procambarusclarkii in invaded freshwater ecosystems.
Data format
csv
Download URL
https://dataportal.lifewatchitaly.eu/view/urn%3Auuid%3A18a8256c-0e31-4800-af5b-958ea88faf34
Description
A description of the dataset is provided below. The dataset attributes were labelled using standard vocabularies and terms harvested from Darwin Core, LifeWatch ERIC Ecoportal and NERC Vocabulary Server.
Data set 2.
Column label | Column description |
---|---|
catalogNumber | An identifier (preferably unique) for the record within the dataset or collection. |
associatedReferences | A list (concatenated and separated) of identifiers (publication, bibliographic reference, global unique identifier, URI) of literature associated with the Occurrence. |
country | The name of the country or major administrative unit in which the Location occurs. |
locality | The specific description of the place. |
habitat | A category or description of the habitat in which the Event occurred. |
eventDate | The date-time or interval during which an Event occurred. |
scientificName | The full scientific name, with authorship and date information, if known. When forming part of an Identification, this should be the name in lowest level taxonomic rank that can be determined. This term should not contain identification qualifications, which should instead be supplied in the IdentificationQualifier term. |
decimalLatitude | The geographic latitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic centre of a Location. Positive values are north of the Equator, negative values are south of it. |
decimalLongitude | The geographic longitude (in decimal degrees, using the spatial reference system given in geodeticDatum) of the geographic centre of a Location. Positive values are east of the Greenwich Meridian, negative values are west of it. |
d13C_VPDB_biota | The ratio of carbon 13 relative to carbon 12 in a biological organism identified elsewhere in the metadata, expressed in per mille and relative to the international reference Vienna Pee Dee Belemnite standard. |
d15N_biota | The ratio of nitrogen 15 relative to nitrogen 14 in a biological organism identified elsewhere in the metadata, expressed in per mille and relative to atmospheric air. |
Supplementary Material
Table S1
Di Muri C, Mancinelli G
Data type
Reference list
Brief description
List of bibliographic references used for isotopic data collection of Procambarusclarkii and potential prey.
File: oo_670329.pdf
Acknowledgements
The authors thank Lucia Vaira (LifeWatch ERIC Service Centre) for her assistance with the data and metadata publication and Iva Johovic for helping with the initial phase of data collection.
Contributor Information
Cristina Di Muri, Email: cristina.dimuri@iret.cnr.it.
Giorgio Mancinelli, Email: giorgio.mancinelli@unisalento.it.
Author contributions
Cristina Di Muri: Data collection, standardisation and publication, data analysis, writing - original draft, final review and editing.
Paloma Alcorlo, Roberta Bardelli, Jordi Catalan, Esperança Gacia, Maria Teresa Guerra, David X. Soto and Salvatrice Vizzini: data providers - final review and editing.
Ilaria Rosati: data standardisation, data and metadata publication and final quality check - final review and editing.
Giorgio Mancinelli: conceptualisation, data collection and analysis, writing - original draft, final review and editing.
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Table S1
Di Muri C, Mancinelli G
Data type
Reference list
Brief description
List of bibliographic references used for isotopic data collection of Procambarusclarkii and potential prey.
File: oo_670329.pdf