Abstract
This article is intended as a guideline to the use of two exploratory data analysis methods, namely STATICO and COSTATIS. Both techniques have already been used in the field of ecological data analysis, and we present a rapid survey of the ecological literature on three-ways analysis methods. Here, we wish to share some advanced computation and graphical display scripts to help ecologists use these methods. We first recall the main principles of these two methods for the analysis of the relationships between the structures of two series of data tables. In the context of ecology, these two series can be for example (1) a series of species data tables and (2) a series of environmental parameters tables. A detailed, real-size example is presented to show how this strategy can be put in place using the ade4 and adegraphics packages for R. This example relates to the ecology of aquatic Heteroptera in the Medjerda watershed (Tunisia). We show how the outputs of the two methods can be used to interpret the relationships between aquatic Heteroptera species distribution and environmental parameters. Several R scripts to conduct the computations and draw suitable graphical displays are reproduced and explained in the text and in five appendices.
Similar content being viewed by others
References
Abdi H, Williams L, Valentin D, Bennani-Dosse M (2012) STATIS and DISTATIS: optimum multitable principal component analysis and three way metric multidimensional scaling. WIREs Comput Stat 4:124–167
Abidi S, Bejaoui M, Boumaiza M (2011) Influence de la pollution sur la qualité des eaux et la méiofaune de l’oued Kasseb (Tunisie septentrionale). Bulletin de la Société Zoologique de France 136:145–157
Abidi S, Bejaoui M, Jemli M, Boumaiza M (2015) Qualité des eaux du cours principal de la Medjerda et trois de ses affluents nord. Hydrol Sci J 60:1607–1619
Amiri A, Chaqui A, Hamdi Nasr I, Inoubli MH, Ben Ayed N, Tlig S (2011) Role of preexisting faults in the geodynamic evolution of Northern Tunisia, insights from gravity data from the Medjerda valley. Tectonophysics 506(1–4):1–10
Andersen N (1971) Infraorder Gerromorpha Popov, 1971. Semiaquatic bugs. In: Aukema B, Rieger C (eds) Catalogue of the heteroptera of the palaearctic region. The Netherlands Entomological Society, Amsterdam, pp 77–114
Aukema B, Rieger C, Rabitsch W (2013) Supplements. In: Catalogue of the Heteroptera of the Palaearctic region, The Netherlands Entomological Society, Amsterdam, p 629
Ben Ayed N (1986) Evolution tectonique de l’avant-pays de la chaîne alpine de Tunisie du début du Mésozoïque à l’actuel. Thèse d’etat, Université De Paris Sud - Centre d’Orsay, Paris
Bertrand F, Maumy-Bertrand M (2010) Using Partial Triadic Analysis for Depicting the Temporal Evolution of Spatial Structures: Assessing Phytoplankton Structure and Succession in a Water Reservoir. Case Studies in Business, Industry and Government Statistics 4(1):23–43, http://www.bentley.edu/csbigs/documents/bertrand2.pdf
Boumaïza M (1984) Contribution à la limnologie de la Tunisie: étude physico-chimique. Arch Inst Pasteur Tunis 61:205–246
Carapezza A (1997) Heteroptera of Tunisia. Naturalista Siciliano 4:1–312
Carassou L, Ponton D (2006) Spatio-temporal structure of pelagic larval and juvenile fish assemblages in coastal areas of New Caledonia, Southwest Pacific. Mar Biol 150:697–711
Carbonell JA, Gutiérrez-Cánovas C, Bruno D, Abellán P, Velasco J, Millán A (2011) Ecological factors determining the distribution and assemblages of the aquatic Hemiptera (Gerromorpha and Nepomorpha) in the Segura river basin (Spain). Limnetica 30:59–70
Certain G, Masse J, Van Canneyt O, Petitgas P, Doremus G, Santos M, Ridoux V (2011) Investigating the coupling between small pelagic fish and marine top predators using data collected from ecosystem-based surveys. Mar Ecol Prog Ser 422:23–39
Chessel D, Hanafi M (1996) Analyses de la co-inertie de K nuages de points. Revue de Statistique Appliquée 44:35–60
Cummins KW, Merritt RW (1996) Ecology and distribution of aquatic insects. In: Merritt RW, Cummins KW (eds) An introduction to the aquatic insects of North America, 2nd edn. Kendall/Hunt Publ. Co., Dubuque, pp 74–86
David V, Ryckaert M, Karpytchev M, Bacher C, Arnaudeau V, Vidal N, Maurer D, Niquil N (2012) Spatial and long-term changes in the functional and structural phytoplankton communities along the French Atlantic coast. Estuar Coast Shelf Sci 108:37–51
Decaëns T, Rossi JP (2001) Spatio-temporal structure of earthworm community and soil heterogeneity in a tropical pasture. Ecography 24:671–682
Decaëns T, Jiménez JJ, Rossi JP (2009) A null-model analysis of the spatio-temporal distribution of earthworm species assemblages in Colombian grasslands. J Trop Ecol 25:415–427
Dolédec S, Chessel D (1994) Co-inertia analysis: an alternative method for studying species-environment relationships. Freshw Biol 31:277–194
Dray S, Dufour AB (2007) The ade4 package: implementing the duality diagram for ecologists. J Stat Softw 22(4):1–20
Dray S, Siberchicot A (2015) adegraphics: An S4 Lattice-based package for the representation of multivariate data. https://github.com/sdray/adegraphics, r package version 1.0-4
Dray S, Chessel D, Thioulouse J (2003) Co-inertia analysis and the linking of ecological data tables. Ecology 84:3078–3089
Dungan JL, Perry JN, Dale MRT, Legendre P, Citron-Pousty S, Fortin MJ, Jakomulska A, Miriti M, Rosenberg MS (2002) A balanced view of scale in spatial statistical analysis. Ecography 25(5):626–640
Erős T, Sály P, Takács P, Specziár A, Bíró P (2012) Temporal variability in the spatial and environmental determinants of functional metacommunity organization - stream fish in a human-modified landscape. Freshw Biol 57(9):1914–1928
Ernoult A, Freiré-Diaz S, Langlois E, Alard D (2006) Are similar landscapes the result of similar histories? Landscape Ecol 21(5):631–639
Escoufier Y (1973) Le traitement des variables vectorielles. Biometrics 29:750–760
Faust D, Zielhofer C, Baena R, del Olmo FD (2004) High-resolution fluvial record of late Holocene geomorphic change in northern Tunisia: climatic or human impact ? Quatern Sci Rev 23(16–17):1757–1775
Garcia-Aviles J, Puig MA, Soler AG (1996) Distribution and association of the aquatic Heteroptera of the Balearic Islands (Spain). Hydrobiologia 324:209–217
Ghanmi M (1980) Etude géologique du Djebel Kebbouch (Tunisie septentrionale). PhD thesis, Université Paul Sabatier, Toulouse
Gonçalves A, Pardal M, Marques S, Mendes S, Fernández-Gómez M, Galindo-Villardón M, Azeiteiro U (2012) Diel vertical behavior of Copepoda community (naupliar, copepodites and adults) at the boundary of a temperate estuary and coastal waters. Estuar Coast Shelf Sci 98:16–30
Gourdol L, Hissler C, Hoffmann L, Pfister L (2013) On the potential for the Partial Triadic Analysis to grasp the spatio-temporal variability of groundwater hydrochemistry. Appl Geochem 39:93–107
Hernández-Fariñas T, Soudant D, Barillé L, Belin C, Lefebvre A, Bacher C (2014) Temporal changes in the phytoplankton community along the French coast of the Eastern English Channel and the Southern Bight of the North Sea. ICES J Mar Sci 71:821–833
Hufnagel L, Bakonyi G, Vásárhelyi T (1999) New approach for habitat characterization based on species lists of aquatic and semiaquatic bugs. Environmental monitoring and assessment. Environ Monit Assess 58(3):305–316
Jansson A (1986) The Corixidae (Heteroptera) of Europa and some adjacent regions. Acta Entomologica Fennica 47:7–94
Jansson A (1995) Family Corixidae Leach, 1815 - water boatmen. In: Aukema B, Rieger C (eds) Catalogue of the Heteroptera of the Palaearctic region. Vol. 1. Enicocephalomorpha, Dipsocoromorpha, Nepomorpha, Gerromorpha and Leptopodomorpha. The Netherlands Entomological Society, Amsterdam, pp 26–56
Jaouadi M, Amdouni N, Duclaux L (2012) Characteristics of natural organic matter extracted from the waters of Medjerda dam (Tunisia). Desalination 305:64–71
Jiménez JJ, Decaëns T, Rossi JP (2006) Stability of the spatio-temporal distribution and niche overlap in neotropical earthworm assemblages. Acta Oecologica 30(3):299–311
Jiménez JJ, Darwiche-Criado N, Sorando R, Comín FA, Sánchez-Pérez JM (2015) A methodological approach for spatiotemporally analyzing water-polluting effluents in agricultural landscapes using Partial Triadic Analysis. J Environ Qual 44:1617–1630
Karaouzas I, Gritzalis KC (2006) Local and regional factors determining aquatic and semi-aquatic bug (Heteroptera) assemblages in rivers and streams of Greece. Hydrobiologia 573(1):199–212
Kidé SO, Manté C, Dubroca L, Demarcq H, Mérigot B (2015) Spatio-temporal dynamics of exploited groundfish species assemblages faced to environmental and fishing forcings: insights from the Mauritanian exclusive economic zone. PLoS ONE 10(e0141):566
Kroonenberg P (1989) The analysis of multiple tables in factorial ecology. III. Three mode principal component analysis: analyse triadique complète. Acta Oecol 10:245–256
Ladhar C, Tastard E, Casse N, Denis F, Ayadi H (2015) Strong and stable environmental structuring of the zooplankton communities in interconnected salt ponds. Hydrobiologia 743:1–13
Lavit C, Escoufier Y, Sabatier R, Traissac P (1994) The ACT (STATIS method). Comput Stat Data Anal 18:97–119
Lebart L, Morineau A, Warwick KM (1984) Multivariate descriptive statistical analysis. Correspondence analysis and related techniques for large matrices. Wiley Series in Probability and Mathematical Statistics: Applied Probability and Statistics. Wiley, New York
Macan TT (1938) Evolution of aquatic habitats with special reference to the distribution of Corixidae. J Anim Ecol 7(1):1
Macan TT (1954) A contribution to the study of the ecology of Corixidae (Hemipt.). J Anim Ecol 23(1):115
Marques SC, Pardal MA, Mendes S, Azeiteiro UM (2011) Using multitable techniques for assessing the temporal variability of species-environment relationship in a copepod community from a temperate estuarine ecosystem. J Exp Mar Biol Ecol 405:59–67
Mendes S, Fernández-Gómez MJ, Resende P, Pereira MJ, Galindo-Villardón MP, Azeiteiro UM (2009) Spatio-temporal structure of diatom assemblages in a temperate estuary. a STATICO analysis. Estuar Coast Shelf Sci 84:637–644
Mendes S, Fernández-Gómez MJ, Pereira MJ, Azeiteiro UM, Galindo-Villardón MP (2010) The efficiency of the partial triadic analysis method: an ecological application. Biometri Lett 47(2):83–106
Napoléon C, Raimbault V, Fiant L, Riou P, Lefebvre S, Lampert L, Claquin P (2012) Spatiotemporal dynamics of physicochemical and photosynthetic parameters in the central English Channel. J Sea Res 69:43–52
Numaan M (2011) Quality assessment of Tigris River by using water quality index for irrigation purpose. Eur J Sci Res 57:15–28
Perthuisot V (1978) Dynamique et pétrogenèse des extrusions triasiques en Tunisie septentrionale. Thèse d’état, École normale supérieure, Paris
Poisson R (1957) Hétéroptères aquatiques. In: Faune de France, Vol. 61, Fédération Française des Sociétés de Sciences Naturelles, Paris, p 263
Polhemus J (1995a) Family Naucoridae Leach, 1815 - creeping water bugs, saucer bugs. In: Aukema B, Rieger C (eds) Catalogue of the Heteroptera of the Palaearctic region. Vol. 1. Enicocephalomorpha, Dipsocoromorpha, Nepomorpha, Gerromorpha and Leptopodomorpha. The Netherlands Entomological Society, Amsterdam, pp 57–60
Polhemus J (1995b) Family Nepidae Latreille, 1802 - water scorpions, water stick insects. In: Aukema B, Rieger C (eds) Catalogue of the Heteroptera of the Palaearctic region. Vol. 1. Enicocephalomorpha, Dipsocoromorpha, Nepomorpha, Gerromorpha and Leptopodomorpha. The Netherlands Entomological Society, Amsterdam, pp 14–18
Polhemus J (1995c) Family Notonectidae Latreille, 1802 - backswimmers. In: Aukema B, Rieger C (eds) Catalogue of the Heteroptera of the Palaearctic region. Vol. 1. Enicocephalomorpha, Dipsocoromorpha, Nepomorpha, Gerromorpha and Leptopodomorpha. The Netherlands Entomological Society, Amsterdam, pp 63–73
Polhemus J (1995d) Family Ochteridae Kirkaldy, 1906 - velvet shore bugs. In: Aukema B, Rieger C (eds) Catalogue of the Heteroptera of the Palaearctic region. Vol. 1. Enicocephalomorpha, Dipsocoromorpha, Nepomorpha, Gerromorpha and Leptopodomorpha. The Netherlands Entomological Society, Amsterdam, pp 25–26
Polhemus J (1995e) Family Pleidae Fieber, 1851 - pygmy backswimmers. In: Aukema B, Rieger C (eds) Catalogue of the Heteroptera of the Palaearctic region. Vol. 1. Enicocephalomorpha, Dipsocoromorpha, Nepomorpha, Gerromorpha and Leptopodomorpha. The Netherlands Entomological Society, Amsterdam, pp 73–75
Rodier J, Colombani J, Claude J, Kallel R (1981) Le bassin de la Medjerda. Monographies Hydrologiques de l’ORSTOM
Rolland A, Bertrand F, Maumy M, Jacquet S (2009) Assessing phytoplankton structure and spatio-temporal dynamics in a freshwater ecosystem using a powerful multiway statistical analysis. Water Res 43(13):3155–3168
Rossi JP (2003) The spatiotemporal pattern of a tropical earthworm species assemblage and its relationship with soil structure. Pedobiologia 47(5–6):497–503
Rouvier H (1977) Géologie de l’extrême nord tunisien. Tectonique et paléogéographie superposées à l’extrême orientale la chaîne nord maghrébine. PhD thesis, Université de Paris VI, Paris
Sabatier R, Vivien M (2008) A new linear method for analyzing four-way multiblock tables: STATIS-4. J Chemom 22:399–407
Savage AA (1982) Use of water boatmen (Corixidae) in the classification of lakes. Biol Conserv 23(1):55–70
Savage AA (1990) The distribution of Corixidae in lakes and the ecological status of the North West Midland Meres. Field Stud 7:516–530
Savage AA (1994) The distribution of Corixidae in relation to the water quality of British lakes: a monitoring model. Freshwater Forum 4:32–61
Simier M, Blanc L, Pellegrin F, Nandris D (1999) Approche simultanee de k couples de tableaux : application à l’étude des relations pathologie végétale - environnement. Revue de Statistique Appliquée 47:31–46
Slimani N, Moulet P, Chen PP, Nieser N, Pluot-Sigwalt D, Boumaïza M, Guilbert E (2015) Checklist, distribution, and a new record of Nepomorphan water bugs (Hemiptera: Heteroptera) in northern Tunisia. Zootaxa 3981(2):151
Slimani N, Chen PP, Nieser N, Moulet P, Ribeiro I, Boumaïza M, Guilbert E (2016) Annotated check-list of semi-aquatic bugs of Tunisia, with detailed faunistic survey of North Tunisia (Hemiptera: Heteroptera: Gerromorpha). Entomologica Americana 122:55–71
Smilde R, Westerhuis M, Boqué R (2000) Multiway multiblock component and covariates regression models. J Chemom 14:301–331
Tamanini R (1979) Guide per il riconoscimento delle specie animali delle acque interne italiane, vol. 6. In: Eterotteri Acquatici (Heteroptera: Gerromorpha, Nepomorpha), Consiglio Nazionale delle Ricerche, Verona, p 106
ter Braak C (1986) Canonical correspondence analysis: a new eigenvector technique for multivariate direct gradient analysis. Ecology 67:1167–1179
Thioulouse J (2011) Simultaneous analysis of a sequence of paired ecological tables: a comparison of several methods. Ann Appl Stat 5:2300–2325
Thioulouse J, Chessel D (1987) Les analyses multitableaux en écologie factorielle. I: De la typologie d’état à la typologie de fonctionnement par l’analyse triadique. Acta Oecol 8:463–480
Thioulouse J, Dray S (2007) Interactive multivariate data analysis in R with the ade4 and ade4TkGUI packages. J Stat Softw 22(5):1–14, http://www.jstatsoft.org/v22/i05
Thioulouse J, Simier M, Chessel D (2004) Simultaneous analysis of a sequence of paired ecological tables. Ecology 85:272–283
Tully O, McCarthy TK, O’Donnell D (1991) The ecology of the Corixidae (Hemiptera: Heteroptera) in the Corrib catchment, Ireland. Hydrobiologia 210(3):161–169
Van Den Wollenberg A (1977) Redundancy analysis, an alternative for canonical analysis. Psychometrika 42:207–219
Vivien M, Sabatier R (2003) Generalized orthogonal multiple co-inertia analysis(-PLS): new multiblock component and regression methods. J Chemom 17:287–301
Vivien M, Sabatier R (2004) A generalization of STATIS-ACT strategy: DO-ACT for two multiblocks tables. Comput Stat Data Anal 46:155–171
Vivien M, Sune F (2009) Two four-way multiblock methods used for comparing two consumer panels of children. Food Qual Prefer 20:472–481
Zahar Y, Ghorbel A, Albergel J (2008) Impacts of large dams on downstream flow conditions of rivers: aggradation and reduction of the Medjerda channel capacity downstream of the Sidi Salem dam (Tunisia). J Hydrol 351:318–330
Acknowledgements
This study was funded by the cooperation program CNRS/DGRST \(\hbox {n}^{\circ }\) 15/R0902 between France and Tunisia. This study was also funded by the Ministry of High Education and Scientific Research of Tunisia. The sampling survey of 2013 was supported by the Laboratory of Hydrobiology of the Faculty of Sciences in Bizerta. We thanks Mr. Abdessalem Ben Hhaj Amara the dean of the Faculty of Sciences in Bizerta, Khalfallah Taoufik, the general secretary, Gharsallah Hafida, director of the financial service, Hamrouni Nizar, Rzeigui Mourad and the members of this service. We also thank Béjaoui Mustapha, Boughdiri Mabrouk for fruitful collaboration. We thank the associate editor and the two reviewers for many useful comments and corrections.
Author information
Authors and Affiliations
Corresponding author
Additional information
Handling Editor: Pierre Dutilleul.
Electronic supplementary material
Below is the link to the electronic supplementary material.
Appendices
Appendices
1.1 General plot of the STATICO method (Fig. 3)
This figure can be drawn with the generic plot function, but the version given here is enhanced to add colors and avoid label superimpositions. Note that this figure should be drawn in a square window to keep an appropriate height/width ratio.
Graph g11 is the correlation circle of the Interstructure (top left). The eigenvalues bar chart g12 of the Interstructure analysis is drawn with the plotEig function and inserted in the correlation circle graph with the insert function to obtain graph g1.
Graph g2 is the factor map of Compromise columns (bottom-left). It is drawn with the s.label function and label color is set to blue. The plabels.optim parameter is set to TRUE, which means that labels are arranged to minimize superimpositions.
Graph g31 is the factor map of Compromise rows (top-right). It is also drawn with the s.label function and label color is set to red. The eigenvalues bar chart g32 of the Compromise analysis is drawn with the plotEig function and inserted in graph 31 with the insert function to obtain graph g3.
Graph g4 is the plot of the “typological value” (squared cosines vs. weights) of the tables. It is drawn with the s.label function.
The four graphs are finally grouped using the ADEgS function to get the final Fig. gtot.
1.2 STATICO Intrastructure for environmental parameters and water bugs (Fig. 4)
This figure uses the facets argument to draw automatically the graphs corresponding to the environmental parameters and species at each date (12 months). The height/width ratio of the window in which this figure is drawn should be set to 1.5 to keep appropriate scales.
Four graph collections are drawn with the s.label and s.arrow function, using the facets argument: slE (labels) and saE (arrows) for environmental parameters (red labels), and slH (labels) and saH (arrows) for water bugs (blue labels).
Each collection is made of the 12 graphs corresponding to the 12 months with the facets argument and the TL or TC elements of the stat1 object. These elements contain factors defining to which month belongs each environmental parameter or each water bug species.
The collections of labels and arrows graphs are superimposed with the superpose function. They are then split in two (months January to June, and months July to December), and the positions of the elementary graphs corresponding to the 6 months are rearranged to place side by side the environmental parameters graph and the water bugs graph of each pair.
This rearrangement of elementary graph positions is done with the layout2position function. It allows an easier comparison of species and environmental parameters graphs month by month.
Both collections of graphs are grouped again using the ADEgS function and plotted side by side.
1.3 STATICO Intrastructure for the sampling sites (Fig. 5)
This figure also uses the facets argument to draw automatically the graphs corresponding to the sampling sites of the environmental parameters table and of the species data table at each date (12 months). The height/width ratio of the window in which this figure is drawn should be set to 1.5 to keep appropriate scales.
Intrastructure plot of the STATICO method for the sampling sites of the environmental parameters (top, red labels) and water bugs (bottom, blue labels).
In this figure, the facets argument of the s.traject and s.label functions is used to draw automatically collections of graphs. In these collections, each elementary graph corresponds to one table (i.e., one month). The selection of the rows that go into each graph is done with the stat1$supTI factor that is built during analysis computations.
The first collection of graphs (st1) is trajectory lines that links the 12 sites of the environmental parameters tables in the upstream-downstream order. The second collection (sla1) draws the site labels (1–12, in red). Both collections are superimposed with the superpose function, resulting in graph s1.
The same procedure is used for the 12 sites of the water bugs tables (with blue labels), resulting in graph s2. Graphs s1 and s2 are placed one under the other and plotted with function ADEgS.
1.4 General plot of the COSTATIS method (Fig. 6)
This figure can be drawn with the generic plot function, but the version given here is enhanced to add colors and avoid label superimpositions. This figure should be drawn in a square window to keep an appropriate height/width ratio.
There are six elementary graphs that correspond to several elements of the COSTATIS analysis numerical outputs.
The two correlation circles on the left of the figure show the projection of unconstrained axes in the Co-inertia factor map. They correspond here to the axes of the two separate PTA. They are drawn with the s.corcircle function and stored in objects g1 and g2. The eigenvalues bar chart is drawn with the plotEig function, giving object g3.
The main graph is graph g4. It is a special graph, drawn with the s.match function. This function takes two sets of coordinates for the same series of points and draws an arrow between each pair of coordinates. Here, the two series of coordinates are cost1$mX, the coordinates of the sites in the environmental parameters tables and cost1$mY, the coordinates of sites in the species tables. The twelve arrows are numbered 1–12 and correspond to the 12 sites (green labels).
The two graphs in the lower part of the figure are the graphs of water bugs and of environmental parameters. Each one is drawn with the s.arrow and s.label function resulting in objects g51 and g52 (water bug species, blue labels) and g61 and g62 (environmental parameters, red labels). The two graphs of each pair are superimposed with the + operator.
The final figure gtot is obtained by joining the six elementary graphs with the ADEgS function and a fixed layout that allocates more space to the main graph g4.
1.5 COSTATIS Intrastructure plot (Fig. 7)
This is a synthetic figure, showing the superimposition of the rows (sampling sites: 1–12) and columns (environmental parameters: red labels and water bugs: blue labels) of both series of tables. The height/width ratio of the window in which this figure is drawn should be set to 0.5 to keep appropriate scales.
This figure is composed of two graphs: the environmental parameters graph (left) and the water bugs graph (right). The limits of the four (scaled) coordinate vectors, cost1$supIX, cost1$c1, cost1$supIY and cost1$l1 are first computed to set the same limits for all the graphs.
The environmental parameters graph is the superimposition of three elementary graphs: sl1 (s.label function, red labels), sa1 (s.arrow function) for parameters, and sc1 (s.class function, green labels grouped by site) for sampling sites. These three graphs are superimposed with the superpose function to get the first part of the Fig. (ss1).
The water bugs graph is also the superimposition of three elementary graphs: sl2 (s.label function, blue labels), sa2 (s.arrow function) for Heteroptera species, and sc2 (s.class function, green labels grouped by site) for sampling sites. These three graphs are superimposed with the superpose function, leading to the second graph ss2.
Graphs ss1 and ss2 are grouped side by side with the ADEgS function to get the complete Fig. st1.
Rights and permissions
About this article
Cite this article
Slimani, N., Guilbert, E., Ayni, F.E. et al. The use of STATICO and COSTATIS, two exploratory three-ways analysis methods: an application to the ecology of aquatic heteroptera in the Medjerda watershed (Tunisia). Environ Ecol Stat 24, 269–295 (2017). https://doi.org/10.1007/s10651-017-0370-6
Received:
Revised:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s10651-017-0370-6