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Figure 1 from: Lavesque N, Daffe G, Grall J, Zanol J, Gouillieux B, Hutchings P (2019) Guess who? On the importance of using appropriate name: case study of Marphysa sanguinea (Montagu, 1813). ZooKeys 859: 1-15. https://doi.org/10.3897/zookeys.859.34117

Figure 1 Marphysasanguinea: A anterior part, dorsolateral view (MNHN-IA-TYPE 1856) B anterior part, ventral view (MNHN-IA-TYPE 1856) C anterior part, lateral view (MNRJP002048) D Maxillae, dorsal view (MNHN-IA-TYPE 1856). Key: white arrow showing eye; MI to MV, maxillae I to V, Mc, maxillary carriers. Scale bars: 2 mm (A–C), 1mm (D).

Figure 4 from: Lavesque N, Daffe G, Grall J, Zanol J, Gouillieux B, Hutchings P (2019) Guess who? On the importance of using appropriate name: case study of Marphysa sanguinea (Montagu, 1813). ZooKeys 859: 1-15. https://doi.org/10.3897/zookeys.859.34117

Figure 4 Maximum Likelihood tree of valid species of Marphysa and different Marphysasanguinea available in GenBank, based on cytochrome oxidase I (COI) sequences and Kimura-2-parameters model. Bootstrap values on nodes if >50. Sequence accession numbers refer to Table 1.

Figure 3 from: Lavesque N, Daffe G, Grall J, Zanol J, Gouillieux B, Hutchings P (2019) Guess who? On the importance of using appropriate name: case study of Marphysa sanguinea (Montagu, 1813). ZooKeys 859: 1-15. https://doi.org/10.3897/zookeys.859.34117

Figure 3 SEM images of Marphysasanguinea: A isodont, symmetrical pectinate chaetae from anterior chaetiger (AM W.49086, 3rd chaetiger) B isodont, symmetrical pectinate chaetae from mid-body chaetiger (AM W.49086, chaetiger 108) C the two types of pectinate chaetae (AM W.49086, far posterior chaetiger) D subacicular bifid hook (AM W.49086, chaetiger 142). Numbers in white circles indicate the type of pectinate chaetae.

Assessing the Impacts of Super Storm Flooding in the Transportation Infrastructure – Case Study: San Antonio, Texas

<p>Corresponding data set for Tran-SET Project No. 18HSTSA02. Abstract of the final report is stated below for reference:</p> <p>"Flooding are likely to increase worldwide due to climate change. Large storms, referred here as superstorms, defined as events with return period equal or larger than 100 years, can lead to an increase of property damages and loss of life. The ability to predict and plan for the impacts of superstorms on transportation infrastructure is key to mitigate future damages and losses. This study analyzed 51 combinations of future projections for representative concentration pathways (RCP) 4.5 and 8.5 scenarios, which were used to calculate future 1st and 3rd quartiles, median, minimum and maximum intensity-duration-frequency curves (IDF). A HEC-HMS and GSSHA models were built for Leon Creek and Upper San Antonio watersheds. HEC-RAS 1D and 2D were used to evaluate flooding in 20 bridges and the extent of flooded area and roads in both watersheds and to test flood control scenarios. Land use modification with 5, 10 and 15% of LID areas in the watersheds were simulated. The use of levees and altering channels were evaluated. In addition, we evaluated how an increasing the storage capacity of the Olmos Dam would contribute to reduce flood impacts downstream. Results show that the 3rd quartile of projected IDF is closest to the one originated with observed precipitation, which is likely to increase in the future. The near future (2025-2049) under RCP 4.5 scenario presented the greatest increase in intensity. HEC-HMS models showed that discharge peak will increase for all future periods under both scenarios, for the 100- and 500-years storms. Flood projections generated by GSSHA for 100- and 500-years and future precipitation showed that flooded area can increase significantly. For instance, the increase in flooded roads can be more than 80% in near future for 500-year storm in Leon Creek watershed. HEC-RAS analysis showed that all 20 analyzed bridges can be flooded with 500-years storm with climate change and 15 with the 100-year storm. Simulation showed that LID implementation and the elevation of the Olmos Dam’s crest were ineffective to protect transportation infrastructure. Enhancing cross-sections of the main channels and the use of levees can mitigate the impact in some bridges. This study illustrates the need for updates in the design criteria of current and future transportation infrastructure."</p>

Fig 3 from: Kenyeres Z, Takács G, Bauer N (2019) Response of orthopterans to macroclimate changes: A 15-year case study in Central European humid grasslands. Journal of Orthoptera Research 28(2): 187-193. https://doi.org/10.3897/jor.28.34102

Fig 3 Significant decreasing and increasing trends in the relative abundance of some characteristic Orthoptera species in the studied grasslands (2002–2017). Temporal trends were evaluated by the Mann-Kendall trend test.

Fig 2 from: Kenyeres Z, Takács G, Bauer N (2019) Response of orthopterans to macroclimate changes: A 15-year case study in Central European humid grasslands. Journal of Orthoptera Research 28(2): 187-193. https://doi.org/10.3897/jor.28.34102

Fig 2 Decreasing and increasing trends in the relative abundance of some orthopteran parameters (2002–2017). Temporal trends were evaluated by the Mann-Kendall trend test.

Fig 5 from: Kenyeres Z, Takács G, Bauer N (2019) Response of orthopterans to macroclimate changes: A 15-year case study in Central European humid grasslands. Journal of Orthoptera Research 28(2): 187-193. https://doi.org/10.3897/jor.28.34102

Fig 5 CCA ordination based on Orthoptera parameters and environmental parameters (Confus: Conocephalus fuscus; Eucdec: Euchorthippus declivus; gra: graminicole species; mo-ata: mean of the monthly active thermic amount (10°C); mo-eta: mean of the monthly effective thermic amount (10°C); m-ther&ther: moderately-thermophilic and thermophilic species; pra: pratinicole species; rain-spr: rainfall in spring; Roeroe: Roeseliana roeselii; s-r: species richness; tem-m: annual mean temperature; tem-min: annual minimum temperature; tem-sum: mean temperature in summer; the: thermophilic species).

Fig 4 from: Kenyeres Z, Takács G, Bauer N (2019) Response of orthopterans to macroclimate changes: A 15-year case study in Central European humid grasslands. Journal of Orthoptera Research 28(2): 187-193. https://doi.org/10.3897/jor.28.34102

Fig 4 Trends in macroclimate parameters on the studied area (2002–2017). Temporal trends were evaluated by the Mann-Kendall trend test.

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РИС. 6. Пригодность местообитанийдля Brephulopsis cylindrica согласно протестированным моделям четырех типов. Имя колонки обоЗначает номер выборки. in Land snails Brephulopsis cylindrica and Xeropicta derbentina (Gastropoda: Stylommatophora): case study of invasive species distribution modelling

РИС. 6. Пригодность местообитанийдля Brephulopsis cylindrica согласно протестированным моделям четырех типов. Имя колонки обоЗначает номер выборки.

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РИС. 5. Пригодность местообитаний для Xeropicta derbentina согласно протестированным моделям четырех типов. Имя колонки обоЗначает номер выборки. in Land snails Brephulopsis cylindrica and Xeropicta derbentina (Gastropoda: Stylommatophora): case study of invasive species distribution modelling

РИС. 5. Пригодность местообитаний для Xeropicta derbentina согласно протестированным моделям четырех типов. Имя колонки обоЗначает номер выборки.

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РИС. 2. РеЗультаты кластерного аналиЗа по методу Уорда: дендрограмма и кластеры на карте. Цветами выделены кластеры с 1 по 6. in Land snails Brephulopsis cylindrica and Xeropicta derbentina (Gastropoda: Stylommatophora): case study of invasive species distribution modelling

РИС. 2. РеЗультаты кластерного аналиЗа по методу Уорда: дендрограмма и кластеры на карте. Цветами выделены кластеры с 1 по 6.

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Figure 1 in Can the type and placement of traps influence the capturability of marsupials according to their body weight? A case study with Didelphis albiventris and Gracilinanus agilis in central Brazil

Figure 1. Mean and standard deviation of bodied weight (g) for (A) Didelphis albiventris and (B) Gracilinanus agilis captured in semi-deciduous forest fragments in central Brazil. Silhouette according PhyloPic – free silhouette images of organisms, version 2.0 (https://www.phylopic.org/).

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Figure 2 in Abrupt boundaries between mountain meadows and forests separate ground-dwelling invertebrate communities: a case study from South Tyrol, Italy

Figure 2. Unconstrained Detrended Canonical Analyses (DCA) of log-transformed abundances of ground-dwelling macroinvertebrates from montane meadows and mixed forests in South Tyrol, Italy. Data for the highest available taxonomic resolution was used (i.e. Araneae and Formicidae at species level, all other on family level, where possible). Each data point represents a pitfall trap along a linear transect starting from extensively managed hay meadows ('MM' and 'M', squares) across an abrupt ecotone ('E', diamonds) towards mixed forest stands ('F' and 'FF', circles). The size of the data points represents the number of taxa from min. 15 to max. 41.

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Figure 1 in Abrupt boundaries between mountain meadows and forests separate ground-dwelling invertebrate communities: a case study from South Tyrol, Italy

Figure 1. Overview map of the study area of Barbian/Barbiano, South Tyrol (Italy), showing the three extensively managed meadows and the linear transects towards the forests. (A) Overview of the three meadows that are embedded in montane mixed forests. (B) Detailed view of a site showing the sampling design ('MM' – meadow, 'E' – ecotone, 'FF' – forest). (C) Photo of the plot EH3 (Photo credit: Michael Steinwandter). (D) Position of the study site of Barbian/Barbiano within the European Alps (red border). Aerial photographs by Google Earth.

Fig. 2 in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 2. Top: The sampling site on Astley bog in 1998 when the samples described in Davis and Wilkinson (2004) were taken. Bottom: Danes Moss in 1999 when the samples described in Davis and Wilkinson (2004) were taken.

Fig. 7 in Benthic Foraminiferal Assemblages and Biotopes in a Coastal Lake: The Case Study of Lake Varano (Southern Italy)

Fig. 7. PCA ordination diagram by projecting variables on the factor-planes (a: 1 × 2 and b: 3 × 4). The secondary variables are marked with a black square.

Fig. 6 in Benthic Foraminiferal Assemblages and Biotopes in a Coastal Lake: The Case Study of Lake Varano (Southern Italy)

Fig. 6. Dendrogram classification of the stations produced by a Q-mode cluster analysis using the Linkage Distance.

Fig. 6. A in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 6. A: Surface testate samples from a raised 'hummock' site on Holcroft Moss. B: Surface testate samples from bare peat on a path at Holcroft Moss. Note that in the older literature (including all the more accessible identification guides) Archerella flavum is refered to as Amphitrema flavum.

Fig. 1 in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 1. Left: map of UK and Ireland showing locations of sites mentioned in text. Right Top: NW England, showing 1. Chat Moss (Astley Moss as cut-out), 2. Holcroft Moss and 3. Danes Moss. Right Bottom: Location of Ardagullion Bog, Co. Longford.

Fig. 3 in The Use of Testate Amoebae in Monitoring Peatland Restoration Management: Case Studies from North West England and Ireland

Fig. 3. Top: A general view across the current (in 2012) surface of Holcroft Moss from close to our core site. Bottom: The edge of Holcroft Moss (in 2011) showing both the fence designed to keep the sheep used for conservation grazing on the bog and – between the fence and the taller vegetation – the plastic piling sunk into the peat to try and maintain a wetter bog surface.