Next Article in Journal
Sonoplasma Frequency Tuning of Electric Pulses to Modulate and Maximise Reactive Oxygen Species Generation
Previous Article in Journal
Data Analysis to Evaluate the Influence of Drought on Water Quality in the Colorado River Basin
Previous Article in Special Issue
Evaluating the Effect of Common Carp Control on Restoration of a Coastal Wetland in the Laurentian Great Lakes
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

The Diatom Genus Navicula in Spring Ecosystems with the Description of Navicula aquaesuavis sp. nov.

by
María Cid-Rodríguez
1,
Marco Cantonati
2,*,
Nicola Angeli
3,
Olena Bilous
4,5,
Maha Al-Harbi
6,
Horst Lange-Bertalot
7,
Zlatko Levkov
8,
Lucia Piana
2,
Daniel Spitale
9 and
Abdullah A. Saber
10
1
Department of Ecology and Animal Biology, University of Vigo, 36310 Vigo, Spain
2
Department of Biological, Geological and Environmental Sciences, Alma Mater Studiorum—University of Bologna, 40126 Bologna, Italy
3
Research & Collections Department (Limnology & Phycology), MUSE—Museo delle Scienze, 38123 Trento, Italy
4
Institute of Hydrobiology and Aquatic Ecosystem Management (IHG), University of Natural Resources and Life Sciences, 1180 Vienna, Austria
5
Institute of Hydrobiology of NAS of Ukraine, Volodymyra Ivasiuka Ave, 12, 04210 Kyiv, Ukraine
6
Department of Biology, College of Science, Princess Nourah bint Abdulrahman University, Riyadh 11671, Saudi Arabia
7
Biologicum, Goethe Universität Frankfurt, 60438 Frankfurt, Germany
8
Institute of Biology, Faculty of Natural Sciences and Mathematics, Ss. Cyril and Methodius University, 1000 Skopje, North Macedonia
9
BMT BioMonitoring Team, 38095 Trento, Italy
10
Botany Department, Faculty of Science, Ain Shams University, Cairo 11566, Egypt
*
Author to whom correspondence should be addressed.
Water 2024, 16(19), 2751; https://doi.org/10.3390/w16192751
Submission received: 10 August 2024 / Revised: 31 August 2024 / Accepted: 23 September 2024 / Published: 27 September 2024
(This article belongs to the Special Issue Biodiversity of Freshwater Ecosystems: Monitoring and Conservation)

Abstract

:
Given the limited understanding of species diversity and ecological preferences of diatoms of the genus Navicula in spring ecosystems, herein we present and describe as species new to science, Navicula aquaesuavis Lange-Bert., Levkov, Cid-Rodríguez, A.A.Saber and Cantonati sp. nov. This species was collected from a mountain spring located above the tree line at 1613 m a.s.l. in the Northern Apennines. The Fontana del Vescovo (Bishop’s spring), which is the locus classicus of the new species, has a low conductivity (60–70 µS cm−1), temperature of ca. 5 °C, circumneutral pH (7.3–7.5), relatively low nitrate (ca. 1 mg L−1), and also suffered from a discharge reduction from 1 to 0.1 L s−1 from 2011 to 2023. The putative new species was confirmed by a second finding in Northern Macedonia, and we thoroughly document this second population as well. We seized the opportunity to describe this new Navicula and review the global literature on the diatom genus Navicula in spring ecosystems. Using the results of this review and our own databases on springs and wells in central Europe and Egypt, we discuss the main Navicula species and their environmental preferences in spring habitats.

1. Introduction

Spring ecosystems are unique habitats that are increasingly at risk because of the exploitation of strategic water resources, the availability of which is reduced in many geographic areas due to climate change [1]. Diatoms in springs have been investigated more than other components of the biota, but still, new species (sometimes even new genera) are described from springs in the frame of in-depth research on diatom communities (e.g., [2]).
The genus Navicula Bory is usually well-represented in springs; however, it is typically not prominent from a quantitative standpoint, likely because of environmental features of such ecosystems, such as, for instance, low trophic levels (e.g., Navicula dealpina Lange-Bert.) [2].
Representatives of the genus occur more commonly and abundantly in springs at low elevations, in urban areas, with higher nitrates, and with sandy, muddy substrata (e.g., [3]). For instance, in the karstic Su Gologone spring (central-eastern Sardinia, Italy), the Navicula-Nitzschia-Surirella Index indicated low physical disturbance [4].
Fazlutdinova et al. [5] studied diatom communities in soils near thermal springs and found that they included both aquatic and terrestrial species. Navicula was one of the most common diatom genera. Kamberović et al. [6] investigated twenty springs of Mt. Konjuh (Bosnia and Herzegovina) from contrasting bedrocks (limestones and different ophiolitic lithologies, respectively) and noted that the most common alkaliphilic, circumneutral, and eutraphentic diatoms were represented by the genera Gomphonema, Nitzschia and Navicula. Finally, Navicula, Fragilaria, Nitzschia, Cymbella and Gomphonema were the most species-rich genera in the limnocrenic spring Zelenci in Slovenia [7].
At low altitudes, in urban springs, even a Navicula species-flock, morphotypes in the vicinity of N. cincta (Ehrenb.) Ralfs) appear to have developed, including Navicula domiciliensis E.Reichardt [8], N. veronensis Lange-Bert. and Cantonati [2], and Navicula fontana Żelazna-Wieczorek, Lange-Bert., Olszynski and Witkowski [9].
Considering the pivotal importance of the correct knowledge of the taxonomy and ecological preferences of the species occurring in mountain (low conductivity) freshwater ecosystems to use diatoms as reliable indicators of environmental and climate change (e.g., ref. [10]), in this paper, we contribute to fill the gap of the limited understanding of species diversity and ecological preferences of diatoms of the genus Navicula in spring ecosystems. Our objectives were to describe a putative new Navicula species from a spring in the Northern Apennines, review the global literature on Navicula in springs, including arid and semi-arid regions, and use our own selected databases to calculate ecological preferences for the main Navicula species in the mountains of southern central Europe.

2. Materials and Methods

2.1. Study Area, Sampling

Fontana del Vescovo (Bishop’s spring), Northern Apennines, Italy, is a small flowing (rheocrenic) spring shaded only by tall grasses [1]. It has a low conductivity (60–70 µS cm−1), temperature of ca. 5 °C, circumneutral pH (7.3–7.5), relatively low nitrate (ca. 1 mg L−1), and suffered from a discharge reduction from 1 to 0.1 L s−1 from 2011 to 2023 (MC, unpublished data). Fontana del Vescovo is depicted on a map in [1]. All details, including the co-occurring photoautotrophs from cyanobacteria to angiosperms, are available in Cantonati et al. [11]. In general, the photoautotrophic communities are typical of small, mountain, oligotrophic, low-conductivity but well-buffered, flowing springs.
Lake Bogovinsko is the largest permanent glacial lake in North Macedonia, located on Shara Mountain between Bresovec and Mala Smreka at an altitude of 1936 m (shown on a map in [12]). It is located in a rocky area with siliceous geology. The lake is 471 m long and 195 m wide with a shoreline of 1246 m. It is relatively shallow, with a maximum depth of 2.2 m. In the past, Lake Bogovinsko was larger, but due to the anthropogenic regulation (widening) of the river Bogovinska, its size significantly decreased. Several small springs, streams, and snowmelt feed the lake. The water loss is caused by evaporation and surface runoff from the River Bogovinska.
Epilithic diatoms were collected by brushing seven to ten cobbles or small boulders. For the epibryon, entire plantlets of the dominant bryophyte species (submerged or closest to the water) were collected.

2.2. Diatom Preparation, Identification and Counting

The diatom samples were treated with hydrogen peroxide and hydrochloric acid to remove organic material. The cleaned valves were then mounted with Naphrax® (Brunel Microscopes Ltd., Chippenham, Wiltshire, UK). For each sample, three coverslips were prepared and mounted on glass slides, with a total of 400 valves counted to determine relative abundances. The identification and nomenclature primarily followed Lange-Bertalot [13].
Observations were conducted using a Zeiss Axioskop 2 optical microscope (Carl Zeiss Microscopy GmbH, Jena, Germany) equipped with phase contrast and a digital Axiocam camera (Carl Zeiss JSC, Milan, Italy). SEM observations on gold-coated prepared material were primarily carried out at the University of Frankfurt using a Hitachi S-4500 (Hitachi Ltd., Tokyo, Japan). Additional SEM observations were performed at the Museo delle Scienze—MUSE in Trento with an LEO XVP (Carl Zeiss SMT Ltd., Cambridge, UK) under a high vacuum. All observations and micrography mentioned in this note were based on epibryon samples.
Materials, including slides, prepared samples, and aliquots of the original specimens, along with the holotypes of the two new species and the epitype, were stored at the Diatom Collection of MUSE—Museo delle Scienze (TR) in Trento, Northern Italy.
Isotype slides and aliquots of prepared material from the same locality and substratum were deposited at the Diatom Collection of the Natural History Museum, London (BM), and the Diatom Collection of the Botanical Garden and Botanical Museum of the Freie University of Berlin (B), Germany. Measurements from 55 different specimens representing the size-diminution series were taken to obtain ranges and averages of the morphological and ultrastructural features.

2.3. Data Processing and Statistical Analysis

The eight primarly databases that were used to find out the main Navicula species, and their ecological preferences that occur in mountain springs of southern central Europe were as follows: CRENODAT (110 springs): ‘Biodiversity assessment and integrity evaluation of springs of Trentino—Italian Alps—and long-term ecological research (2004–2008) and 16 springs in the adjacent Dolomiti Bellunesi National Park (2004) [14,15]; EBERs; diatoms (sampled in 2022) from 15 springs selected in the Berchtesgaden National Park (Bavaria, Germany) to be sentinel environments of climate change (the paper [16] provides a description of the same dataset but based on samples taken in 2018); diatoms (sampled in 2022) from 14 springs selected in the Bavarian Forest (Bayerischer Wald) National Park (Bavaria, Germany) to be sentinel environments of climate change (twin project to the previous one, M.C. unpublished data); application of the standard methodology developed in the previous project to other protected areas of southern Germany: Rhön UNESCO Biosphere Reserve (nine springs) and Steigerwald Nature Park (six springs) [17], Fichtelgebirge Nature Park (six springs) and Spessart Nature Park (six springs) (M.C. unpublished data).
To study the environmental preferences of all the Navicula taxa, we computed the weighted averages using the WA function in the vegan package in R. The technique calculates the average value of an environmental variable weighted by the relative abundance of the species. By leveraging the species’ abundance data, the weighted average approach allows us to infer the optimal conditions for species based on their distribution across different sites.

3. Results

Division: Bacillariophyta.
Class: Bacillariophyceae Haeckel, 1878 (emend. D.G. Mann, in Round et al., 1990 [18]).
Subclass: Bacillariophycidae D.G. Mann, in Round et al. [18].
Order: Bacillariales D.G. Mann, in Round et al., 1990 [18].
Family: Bacillariaceae Kütz. 1844.
Genus: Navicula Bory de Saint-Vincent, 1822.
  • Navicula aquaesuavis Lange-Bert., Levkov, Cid-Rodríguez, A.A. Saber and Cantonati sp. nov.
Description: LM (Figure 1): Valves lanceolate, ends shortly protracted, subrostrate. Length 14–26 µm, breadth 5.0–6.5 µm. The average length is 18.7 µm with a standard deviation of 2.2 µm, and the average width is 6.0 µm with a standard deviation of 0.3 µm. Raphe filiform with distinct central pores appearing indistinctly or not deflected. The axial area is narrowly linear but somewhat expanded proximally. The central area is moderately large, variable in shape, and mostly of an approximately rhombical shape. Striae radial and slightly arcuate up to the strongly developed Voigt discontinuity, becoming straight and less radial, then parallel, and finally convergent near the apices, 13 in 10 µm. Striae at the central area do not regularly alternate shorter/longer, but one or two shorter ones may be intercalated irregularly. Areolae discernible at least with oblique lighting, 30–40 in 10 µm.
SEM external view, see Figure 2A,B. The raphe sternum with extended central nodule relief-like elevated above the smooth valve face, just even in slightly oblique view (black arrow). The asymmetry of the central area and nodule, respectively, is scarcely developed. Raphe branches are gently curved. The drop-shaped central pores are slightly deflected to the primary side of the valve, opposite to the distal endings and Voigt fault. This feature occurs in most specimens but is sometimes not clearly marked. Terminal raphe fissures commonly form a complicated double curve, never being simply fish-hook-shaped (white arrow). Voigt discordances are commonly marked by a gap in the stria pattern or by a reduced series of less and shortened lineolae.
SEM internal view, see Figure 2C. The fine structure pattern conforms to the large majority of comparable Navicula s. str. Species, and therefore does not provide exclusive characters that might be useful for identification. The raphe slits are twisted in the narrow internal raphe sternum, with free central ends lying in a distinct apically elongated nodule (white arrow), and distal ends in small helictoglossae (black arrow) that are more or less circular to shortly elliptical areolae, which are occluded by hymens lying in troughs between rather equally broad virgae.
Holotype: 31 July 2011, M. Cantonati s.n. (holo-: TR, slide cLIM007 DIAT 1984, partly shown here in Figure 1 and Figure 2A–C (holotype specimen: Figure 1P).
Isotypes: B, slide B 40 0045802, cleaned material B 40 0045803, raw material B 40 0045804; BM; slide BM 92453.
Type locality: Rheocrenic mountain spring Fontana del Vescovo, Italy, Northern Apennines, Province of Parma, Municipality of Corniglio in the Upper Parma Valley, lithology: Siliciclastic sandstones (44°22′44.767″ N, 10°2′26.790″ E, 1613 m a.s.l.).
Etymology: The Latin epithet aquae suavis is the genitive of “soft water” in free translation and refers to the water quality of the habitat.
Synonymy: To exclude from synonymy: Navicula reichardtiana var. crassa Lange-Bert. and Hofmann [19].
Distribution: Navicula aquaesuavis sp. nov. was found only in two sites: the type locality of Fontana del Vescovo in northern Italy and Lake Bogovinsko (the population found at this site is illustrated in Figure 3 and Figure 4) in Northern Macedonia (see Section 2.1 Study area for their environmental characteristics). At the type locality, the new species was found, though with very low numbers of specimens (<0.25% = not counted), both in the epilithon and in the epibryon, but was more abundant in the latter.
  • Co-occurring diatom species and ecology
Fontana del Vescovo: Associated diatom species were Achnanthidium minutissimum (Kütz.) Czarn., A. lineare W.Smith, Planothidium lanceolatum (Bréb. ex Kütz.) Lange-Bert., Amphora indistincta Levkov, A. inariensis Krammer, Navicula exilis Kütz., and Odontidium mesodon (Kütz.) Kütz.
Lake Bogovinsko: Cymbella neocistula Krammer, Cymbopleura macedonica Levkov & Krstic, Diploneis mollenhaueri Lange-Bert. and Fuhrmann, Navicula oligotraphenta Lange-Bert. & G.Hofm., Placoneis opportuna (Hustedt) Chudaev and Gololobova, Platessa ziegleri (Lange-Bert.) Lange-Bert., Pseudostaurosira pseudoconstruens (Marciniak) D.M. Williams and Round, Sellaphora utermoehlii (Hustedt) C.E.Wetzel and D.G.Mann, Planothidium joursacense (Héribaud-Joseph) Lange-Bert., Staurosira construens (Ehrenb.) D.M.Williams and Round, Staurosira neoproducta (Lange-Bert.) Chudaev and Gololobova, Staurosira sviridae Kulikovskiy, Genkal smf Mikheyeva and several unidentified fragilaroid species.
From the environmental assessments at the two verified sites where the new species occurs, from physical and chemical measurements and analyses at the type locality, and from the autecological preferences of the co-occurring diatom species, the new species appears to be typical of oligotrophic, mountain inland waters, with good light conditions and relatively low-conductivity but well-buffered waters.

3.1. The Ecological Preferences of the Main Navicula Species in Mountain Springs of Southern Central Europe as Represented in Own Selected Databases

Nine species were found to be relevant in the epibryon with the set criteria (Table 1), whilst six were important in the epilithon (Table 2). Of these, six were in common, and three were relevant in the epibryon only: Navicula dealpina, N. lundii, and N. moenofranconica.
Considering all records, i.e., both epibryon and epilithon, the two species with the highest numbers of occurrences were Navicula exilis and N. cryptotenella, with 33 and 32 records, respectively, and the two with the highest relative abundances were N. cryptocephala (64%) and N. cryptotenella (16%).

3.2. The Genus Navicula in Spring Ecosystems as Represented in the Global Literature

The global literature on the diatom genus Navicula in spring ecosystems is still scarce. Papers from our review related to springs as habitats (global literature) were integrated with 2–3 books on the topic and by specifically searching the Web of Science for Navicula in springs. These efforts, combined with the articles on arid land springs cited below, hardly yielded twenty papers relevant to the topic.
In typically oligotrophic and often fast-flowing mountain springs, Navicula is not a prominent diatom genus. The only indicator species found by Cantonati et al. [15] working on spring types of the Alps was Navicula exilis for ‘well-buffered siliceous rheocrenes’.
Many of the mountain springs in North Macedonia are under hydromorphological pressures since the water is used for human consumption [20]. Several Navicula appear frequently and abundantly in alkaline springs: N. hintzii Lange-Bert., N. exilis Kütz., and N. moenofranconica Lange-Bert. In circumneutral springs, N. radiosa Kütz. and N. metareichardtiana Lange-Bert. and Kusber are most commonly found, while the diversity of Navicula species is the lowest in slightly acidic springs (N. angusta and N. heimansioides Lange-Bert.). In a few cases, rare species, such as N. umida Bock and N. odiosa Wallace, have been recorded from mountain springs. All species observed in mountain springs are typically oligotrophentic and sensitive to pollution, except N. cryptotenella, which might tolerate moderate pollution levels and eutrophication. A few Navicula species might be found in temporary springs or subaerial habitats (N. lundii Reichardt). The highest species diversity has been noticed in helocrenic springs where various microhabitats are present (humic substrate, sand and silt, and bryophytes), enabling varied diatom communities where different ecological traits can find their place. In general, Navicula species, being motile, prefer springs with low and permanent currents, while they are extremely rare in rheocrenes with fast flow or temporary springs. Such ecological preferences of Navicula species make them quite vulnerable to climate change. A decrease in precipitation (15–20% annually), especially in the quantity of snow during the winter and draughts during the summer, might change the water regime of springs, thus strongly influencing species distribution.
Navicula is one of the most numerous genera of diatoms present in the areas with low-elevation springs in Central [3] and Southern [21] Poland. N. cincta inhabit waters with a broad range of nitrate concentrations and high levels of calcium, magnesium, potassium, sodium, and moderate dissolved oxygen [21]. N. striolata, listed as endangered in the Polish Red List of Algae [3,22], has the narrowest range of environmental variables. It is primarily found in sandy-bottomed springs with limestone bases and moderate magnesium and sodium concentrations while also tolerating a broad range of nitrate levels and showing tolerance to some increased content of nitrate [3]. This species, classified as alkalibiontic taxon by Van Dam et al. [23], also occurs in calcareous springs in the Brenta Dolomites [24]. Werum [25]. Navicula angusta Grunow was found in less polluted springs with low conductivity, nitrate content, alkalinity, calcium concentration, and high dissolved oxygen. Navicula reinhardtii, common in rheocrenes with higher discharge, is found in slightly alkaline waters and is positively influenced by sodium, chloride, and pH levels. The occurrence of species like N. cryptocephala Kütz., N. cryptotenella Lange-Bert., N. radiosa Kütz., N. reichardtiana Lange-Bert. (currently Navicula metareichardtiana) is promoted by human impacts. These species were all recorded in calcium-rich springs with moderate–high specific conductivity. N. metareichardtiana was observed in the Krakowsko-Częstochowska Upland in lightly alkaline, highly alkaline and moderate–very high chlorides and high–very high nitrate concentrations [3].
Navicula gregaria Donkin, a very high-nutrient taxon, is observed in calcium-rich waters with moderate–high specific conductivity and is positively influenced by sodium and chloride ion concentrations. N. antonii is common in alkaline waters with a broad range of specific conductivity, calcium, and nitrate concentrations, which are most prevalent in waters with high nitrate levels. This species is affected positively by potassium and nitrate ion concentrations and redox potential but negatively by silica concentration. These last two species are indicators of increased trophic status in springs of Southern Poland [3]. Navicula aquaedurae, N. catalanogermanica Lange-Bert. and G.Hofm., N. cataracta-rheni Lange-Bert., and N. moenofranconica Lange-Bert. are all vulnerable/rare diatom taxa in Poland. The occurrence of N. moenofranconica was negatively influenced by sodium, nitrate, and phosphate ion concentrations and redox potential. N. veneta Kütz., and N. wiesneri Pant. are rare taxa found in sulphide springs with slightly alkaline waters [3].
The genus Navicula can also occur and even be prevalent in some special kinds of springs, such as naturally radioactive mineral springs, where Baker et al. [26] found Navicula sanctamargaritae to be one of the dominant amplicon sequence variants (ASV). Beauger et al. [27] found Navicula sanctamargaritae to be also associated with the highest potassium concentration in mineral saline springs in the French Massif Central.
Our knowledge of the diversity of species of the genus Navicula in arid and semi-arid springs is still limited. In South America, Angel et al. [28] studied the diatom inventory in the high-altitude arid and semi-arid thermal springs in the El Tatio geothermal field (Altiplano, Chile), one of the least known major geothermal systems in the southern hemisphere, and pinpointed that the water conductivity of these springs varied from 4860 to 12,150 µS·cm−1, except for the freshwater fumarole spring where conductivity showed the lowest range from 440 to 810 µS·cm−1. Navicula cincta, N. cryptocephala, N. cryptotenella, N. lauca U.Rumrich and Lange-Bert., N. microdigitoradiata Lange-Bert., N. parinacota U.Rumrich and Lange-Bert., N. pseudogracilis Hust., N. salinicola Hust., N. tripunctata (O.F.Müller) Bory, N. veneta, and N. viridula (Kütz.) Ehrenb. were recorded. N. salinicola was the most common diatom species in these springs, reflecting its tolerance to the water chemistry of these saline groundwater-dependent systems.
Very little is known about diatoms from the arid and semiarid springs in the Middle East countries. Springs in this hot and dry region of the world are common and the main water supply for local populations. In Saudi Arabia, Abdelwahab and Amin [29], for instance, studied the diatom diversity of the arid mineral-rich hot springs (temp.: up to 60 °C and T.D.S.: up to 4000 mg L–1) in the southwest region and identified 23 different diatom taxa. Both N. cincta and N. radiosa were among the dominant diatom taxa in these springs. In northern Israel, Barinova and Romanov [30] also only recorded N. recens and N. rhynchocephala in the ambient freshwater spring ‘Ein El Balad’ located on the northern slope of the Mount Carmel, confirming the rare occurrence of species of the genus Navicula in the arid and semiarid springs of this region. Similarly, Gerloff et al. [31], on their preliminary list of diatoms from Jordan, only reported N. veneta, N. rhynchocephala var. amphiceros (currently regarded as N. rhynchotella), and N. radiosa var. tenella in the nutrient-rich freshwater springs studied. In Iran, very little attention has also been given to the diatom assemblages in the spring ecosystems. In their study on the hydrochemistry and diatom diversity in three arid springs in NE Iran, Mirzahasanlou et al. [32] stressed that the springs’ diatom assemblages are mainly shaped by the size and morphology of the springs. Navicula broetzii Lange-Bert., E.Reichardt, N. capitatoradiata, N. cryptotenella, N. rostellata Kütz, N. trivialis Lange-Bert. and N. tripunctata. These Navicula species are widely distributed, have a wide range of tolerance to pollution, and usually prefer eutrophic waters. Both N. cryptotenella and N. rostellata were among the most abundant diatom species in the springs studied.
In Africa, Coste et al. [33], for instance, studied the diatom assemblages from three thermal springs in the semi-arid Merguellil Wadi located in Central Tunisia and found a few taxa of the genus Navicula, mostly with low relative abundances, including N. recens (Lange-Bert.) Lange-Bert., N. radiosa, N. rostellata, and N. veneta. Ecologically, the latter diatom species was classified as N-heterotrophic, with a low water quality signature.
Our understanding of the diversity and distribution of the genus Navicula in the arid springs of the largest oasis in the world, Egypt, is still limited. All the previous studies on the Egyptian Navicula species mostly depended on light microscopical observations, using complex taxonomic and nomenclatural history in species identification. In this sense, the real picture of the diversity and distribution of the genus Navicula in Egypt, especially in the spring habitats, is still unconfirmed, and thus, more in-depth taxonomic studies are still needed using modern diatom taxonomy standards. Shaaban [34], Hamed [35], and Saleh [36] are among the reliable taxonomic literature available as an aid for the identification of the Egyptian diatoms, including the Navicula species, but the nomenclatural system applied is nowadays obsolete, overlooking the interesting and small-sized species. For instance, Shaaban and Hamed [37] studied the diatom diversity of the euthermal mineral-rich spring ‘Ain El-Sokhna’, located on the western side of the Suez Gulf, and identified thirty-six different diatom species, out of them N. disjuncta Hust. (currently known as Myriactula pulvinata (Kütz.) Kuntze), N. erifuga Lange-Bert., N. leptostriata E.G.Jørg., N. stankovicii Hust., and N. tenelloides Hust. In the Egyptian desert springs, the occurrence of Navicula species has rarely been observed. For example, N. erifuga was only reported in the inventory of diatoms of Ain Kidies and Ain El-Godyrate at El-Arish Valley in North Sinai, Egypt [38]. The same observations were documented by Shaaban [39] in an investigation of the desert thermal mineral springs of the Siwa Oasis (the Western Desert of Egypt), where he only recorded N. menisculus Schum. and N. radiosa. The same findings were recently confirmed by Saber (unpublished data). Similarly, N. cryptocephala and N. heufleri var. leptocephala (Bréb. ex Grunow) H.Perag. and Perag. (currently known as N. erifuga) were only documented in three thermal and hot springs of the El-Bahariya Oasis. Hamed [35] summarized the geographical distribution of the Egyptian diatoms in different aquatic habitats, including thermal and hot arid springs, and reported eight taxonomically accepted Navicula species in all the springs, including N. cincta, N. cryptocephala, N. erifuga, N. halophila var. leptocephala (currently considered a synonym of N. erifuga Lange-Bert.), N. leptostriata, N. stankovicii, N. tenelloides, and N. veneta. In our recent taxonomic and ecological investigation on diatoms of El-Farafra Oasis springs and drilled wells, the most common Navicula species identified were N. cf. arctotenelloides, N. cryptocephala, N. cryptotenelloides, N. rhynchocephala, N. tenelloides, and N. veneta (Saber and Cantonati, unpublished data) (Figure 5). In general, the most common and distributed Navicula species in the Egyptian arid springs and their counterpart artificial habitats, ‘drilled wells’, are N. cryptocephala and N. veneta ([34,35,36,40]; A.A. Saber, unpublished data). These Navicula species usually colonize the freshwater mineral springs and could tolerate increased nutrient (N and P) concentrations (meso- to eutraphentic species), reflecting different human impacts on the springs they colonize.

4. Discussion

The newly described species superficially resembles the allied Navicula species listed in the following, in particular N. metareichardtiana, but still can be separated by combinations of morphological (and ecological) characters.
Navicula metareichardtiana is commonly recorded from eutrophic, beta-meso-saprobic, alkaline waters. As the most resembling species, it differs mainly by the following morphological characteristics: Valves moderately narrower on average, 5.0–5.5, rarely up to 6.0 (vs. 5.5–6.5) µm; stria density higher on average, 14–16 (vs. 13–15) in 10 µm; areola density higher on average, 35–40 in 10 µm, difficult to discern in LM (vs. 30–35) in 10 µm. The central area is not extended and is approximately rhombical but is smaller. Under the SEM external views, the central nodule and other proximal parts of the sternum do not appear relief-like elevated at any angle of view (by tilting). The slits (areolae, foramina, and lineolae) are apically longer and the alternating virgae and, therefore, narrower than in N. acquaesuavis.
Navicula caterva Hohn and Hellerman exists in alkaline, euthrophic waters with medium–high electrolyte content, differing by valve breadth commonly lower than 5 µm and a higher stria and areola density, 18–21 and ca. 40 in 10 µm, respectively. The central area is conspicuously smaller.
Navicula associata Lange-Bert. is distinguished by almost elliptical valves and longer rostrate protracted ends. In SEM, proximal raphe ends clearly deflected to the secondary valve side; striae more radiated proximally; the lineolae were therefore arranged notably concentrically around the central area; central pores were elongated apically. This species is ecologically adapted to eutrophic alkaline lakes and lake outflows with medium to higher conductivity.
Navicula reichardtiana var. crassa Lange-Bert. and Hofmann is clearly different and separated from the newly described species both morphologically and ecologically. Navicula reichardtiana var. crassa, as the variety epithet suggests, is broader than Navicula metareichardtiana, whilst Navicula aquaesuavis sp. nov. is narrower (see above). Navicula reichardtiana var. crassa, was described from a eutrophic lake (Waginger See) with much higher nitrate contents as compared to the sites from which the newly described species is known [19].
Overall, the statistical analysis of the ecological optima of the main Navicula species in springs of southern central Europe confirms that the epilithon is more suitable for discussing relationships between diatom species and water-quality variables because the epibryon represents a particular, partly buffered, microenvironment. In this way, in our data, nitrates confirm Navicula antonii and N. tripunctata as classical eutraphentic species in the epilithon only. Contrastingly, our analyses focused on Navicula in spring ecosystems confirm the epibryon to be the substratum hosting the most diverse associations, also including rare and Red List species. Out of the three species that were relevant in the epibryon only in our databases, two are in high-threat categories of the Red List [41]: Navicula dealpina (threat category “2”) and N. moenofranconica (t.c. “3”). All of the three Navicula species (N. cryptocephala, N. cryptotenella, N. exilis) most frequent and abundant in our spring databases are included in the list of terrestrial species of Foets et al. [42], highlighting once more that many springs with small discharge are deeply influenced by the effects of discharge fluctuations and desiccation episodes (e.g., ref. [17]).
The results of the study of the ecological preferences of Navicula species in the mountain springs of southern central Europe are also in good agreement with the picture emerging from our synthesis of the global literature on the diatom genus Navicula in spring habitats. The focus on the poorly known diatom assemblages of arid land springs appears to suggest that common species that are typical eutraphentic elements in central Europe (e.g., N. cryptotenelloides, N. erifuga, and N. veneta) might be widespread representatives of diatom assemblages of not necessarily polluted desert springs and wells. However, due to important human impacts on almost all oasis springs in North Africa, more in-depth and focused studies are needed to clarify this point.
Springs are unique but fragile habitats that need to be known as natural biota refugia and sites where the potential of diatoms as indicators particularly unfolds and to be protected because they increasingly face the insults of exploitation and climate change globally [1]. Our study of the species diversity and ecological preferences of diatoms of the genus Navicula in spring ecosystems, also including the description of a new species, is a small but significant contribution to filling the gap of knowledge on this genus in springs, which is important to achieve a correct knowledge of the taxonomy and ecological preferences of the species occurring in near-natural mountain (low conductivity) freshwater ecosystems to use diatoms as reliable indicators of environmental and climate change (e.g., ref. [10]).

Author Contributions

Conceptualization, M.C., Z.L. and H.L.-B.; methodology, M.C., N.A., M.C.-R., L.P. and M.A.-H.; validation, M.C. and H.L.-B.; formal analysis, D.S., M.C., A.A.S. and N.A.; resources, M.C. and A.A.S.; data curation, M.C., M.C.-R., L.P. and N.A.; writing—original draft preparation, M.C., M.C.-R., A.A.S., Z.L., L.P., M.A.-H. and O.B.; writing—review and editing, M.C., O.B., M.C.-R., Z.L., H.L.-B. and D.S.; visualization, N.A., M.C.-R. and M.C.; supervision, M.C. and H.L.-B.; project administration, M.C.; funding acquisition, M.C. All authors have read and agreed to the published version of the manuscript.

Funding

The EBERs Project, which was funded by the Geological Survey of the Emilia-Romagna Region (Italy), generated the data on which the description of the new species is based.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The data presented in this study are available on request from the corresponding author.

Acknowledgments

We are grateful to the Geological Survey of the Emilia-Romagna Region (in particular, Stefano Segadelli) for fostering the EBERs (Exploring the Biodiversity of Emilia-Romagna springs; 2011–2013) Project, in the framework of which the samples used to describe the new species were collected. A.A.S. is also very grateful to M.C. for giving him the opportunity to participate in this project during his post-doctoral position in Italy and after returning to Egypt. A.A.S. is thankful to Adel F. Hamed, Professor of Phycology at the Botany Department, Faculty of Science, Ain Shams University, Egypt, for providing us with some LM images of the Egyptian Navicula species. We also thank the Princess Nourah bint Abdulrahman University Researchers Supporting Project number (PNURSP2024R182), Princess Nourah bint Abdulrahman University, Riyadh, Saudi Arabia.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Cantonati, M.; Segadelli, S.; Spitale, S.; Gabrieli, J.; Gerecke, G.; Angeli, N.; De Nardo, M.T.; Ogata, K.; Wehr, J.D. Geological and hydrochemical prerequisites of unexpectedly high biodiversity in spring ecosystems at the landscape level. Sci. Total Environ. 2020, 740, 140157. [Google Scholar] [CrossRef] [PubMed]
  2. Cantonati, M.; Angeli, N.; Spitale, D.; Lange-Bertalot, H. A new Navicula (Bacillariophyta) species from low-elevation carbonate springs affected by anthropogenic disturbance. Fottea 2016, 16, 255–265. [Google Scholar] [CrossRef]
  3. Żelazna-Wieczorek, J. Diatom Flora in Springs of Łódź Hills (Central Poland); Witkowski, A., Ed.; Diatom Monographs; R.G. Gantner Verlag K.G.: Ruggell, Liechtenstein, 2011; Volume 13, 420p. [Google Scholar]
  4. Lai, G.G.; Padedda, B.M.; Wetzel, C.E.; Lugliè, A.; Sechi, N.; Ector, L. Epilithic diatom assemblages and environmental quality of the Su Gologone karst spring (centraleastern Sardinia, Italy). Acta Bot. Croat. 2016, 75, 129–143. [Google Scholar] [CrossRef]
  5. Fazlutdinova, A.I.; Allaguvatova, R.Z.; Gaysina, L.A. Ecotonic Communities of Diatoms in the Southeastern Part of the Kamchatka Peninsula. Earth 2023, 4, 209–222. [Google Scholar] [CrossRef]
  6. Kamberović, J.; Plenković-Moraj, A.; Borojević, K.K.; Udovič, M.G.; Žutinić, P.; Hafner, D.; Cantonati, M. Algal assemblages in springs of different lithologies (ophiolithes vs. limestone) of the Konjuh Mountain (Bosnia and Herzegovina). Acta Bot. Croat. 2019, 78, 66–81. [Google Scholar] [CrossRef]
  7. Zelnik, I.; Balanč, T.; Toman, M.J. Diversity and Structure of the Tychoplankton Diatom Community in the Limnocrene Spring Zelenci (Slovenia) in Relation to Environmental Factors. Water 2018, 10, 361. [Google Scholar] [CrossRef]
  8. Reichardt, E. Neue Diatomeen (Bacillariophyceae) aus dem Gebiet der Stadt Treuchtlingen. Berichte Der Bayer. Bot. Ges. 2012, 82, 19–32. [Google Scholar]
  9. Żelazna-Wieczorek, J.; Lange-Bertalot, H.; Olszynski, R.M.; Witkowski, A. Navicula fontana sp. nov., a new freshwater diatom from a limnocrenic spring in central Poland. Phytotaxa 2020, 452, 155–164. [Google Scholar] [CrossRef]
  10. Bahls, L.; Pierce, J.; Apfelbeck, R.; Olsen, L. Encyonema droseraphilum sp. nov. (Bacillariophyta) and other rare diatoms from undisturbed floating-mat fens in the northern Rocky Mountains, USA. Phytotaxa 2013, 127, 32–48. [Google Scholar] [CrossRef]
  11. Cantonati, M.; Angeli, N.; Lange-Bertalot, H.; Levkov, Z. New Amphora and Halamphora (Bacillariophyta) species from springs in the northern Apennines (Emilia-Romagna, Italy). Plant Ecol. Evol. 2019, 152, 285–292. [Google Scholar] [CrossRef]
  12. Angus, R.B. Further karyosystematic investigation of the Stictotarsus griseostriatus (De Geer) group of sibling species (Coleoptera: Dytiscidae). Comp. Cytogenet. 2008, 2, 151–156. [Google Scholar]
  13. Lange-Bertalot, H. Navicula sensu stricto, 10 genera seperated from Navicula sensu lato, Frustulia. In Diatoms of Europe, Diatoms of the European Inland Waters and Comparable Habitats; Lange-Bertalot, H., Ed.; A.R.G. Gantner Verlag K.G.: Ruggell, Liechtenstein, 2001; Volume 2, pp. 1–526. [Google Scholar]
  14. Cantonati, M.; Spitale, D. The role of environmental variables in structuring epiphytic and epilithic diatom assemblages in springs and streams of the Dolomiti Bellunesi National Park (south-eastern Alps). Fundam. Appl. Limnol.-Arch. Hydrobiol. 2009, 174, 117–133. [Google Scholar] [CrossRef]
  15. Cantonati, M.; Angeli, N.; Bertuzzi, E.; Spitale, D.; Lange-Bertalot, H. Diatoms in springs of the Alps: Spring types, environmental determinants, and substratum. Freshw. Sci. 2012, 31, 499–524. [Google Scholar] [CrossRef]
  16. Cantonati, M.; Bilous, O.; Spitale, D.; Angeli, N.; Segadelli, S.; Bernabè, D.; Lichtenwöhrer, K.; Gerecke, R.; Saber, A.A. Diatoms from the spring ecosystems selected for the long-term monitoring of climate-change effects in the Berchtesgaden National Park (Germany). Water 2022, 14, 381. [Google Scholar] [CrossRef]
  17. Cantonati, M.; Casoria, C.; Gerecke, R.; Bilous, O.; Maisto, G.; Segadelli, S.; Spitale, D.; Steinbauer, A.; Vogel, S.; Saber, A.A. Diatom Indicators of Fluctuating/Intermittent Discharge from Springs in Two German Nature Conservation Areas. Diversity 2023, 15, 915. [Google Scholar] [CrossRef]
  18. Round, F.E.; Crawford, R.M.; Mann, D.G. The Diatoms: Biology and Morphology of the Genera; Cambridge University Press: Cambridge, UK, 1990; p. 747. [Google Scholar]
  19. Lange-Bertalot, H. 85 neue Taxa und über 100 weitere neu definierte Taxa ergänzend zur Süsswasserflora von Mitteleuropa/85 New Taxa and much more than 100 taxonomic clarifications supplementary to Süsswasserflora von Mitteleuropa. Bibl. Diatomol. 1993, 27, 164. [Google Scholar]
  20. Levkov. Diatom Atlas of Macedonia. manuscript in preparation.
  21. Wojtal, A.Z. Species composition and distribution of diatom assemblages in spring waters from various geological formations in southern Poland. In Bibliotheca Diatomologica; J. Cramer Verlag: Stuttgart, Germany, 2013; Volume 59, 436p. [Google Scholar]
  22. Siemińska, J.; Bąk, M.; Dziedzic, J.; Gąbka, M.; Gregorowicz, P.; Mrozińska, T.; Pełechaty, M.; Owsianny, P.M.; Pliński, M.; Witkowski, A. Red list of algae in Poland. In Red List of Plants and Fungi in Poland; W. Szafer Institute of Botany, Polish Academy of Sciences: Kraków, Poland, 2006; pp. 35–52. [Google Scholar]
  23. Van Dam, H.; Mertens, A.; Sinkeldam, J. A coded checklist and ecological indicator values of freshwater diatoms from the Netherlands. J. Aquat. Ecol. 1994, 28, 117–133. [Google Scholar]
  24. Cantonati, M. Diatom communities of springs in the Southern Alps. Diatom Res. 1998, 13, 201–220. [Google Scholar] [CrossRef]
  25. Werum, M. Die Kieselalgengesellschaften in Quellen: Abhängigkeit von Geologie und anthropogener Beeinflussung in Hessen (Bundesrepublik Deutschland). In Umwelt und Geologie; Hessische Landesamt für Umwelt und Geologie: Wiesbaden, Germany, 2001; 273p. [Google Scholar]
  26. Baker, L.A.; Beauger, A.; Kolovi, S.; Voldoire, O.; Allain, E.; Breton, V.; Chardon, P.; Miallier, D.; Bailly, C.; Montavon, G.; et al. Diatom DNA metabarcoding to assess the effect of natural radioactivity in mineral springs on ASV of benthic diatom communities. Sci. Total Environ. 2023, 15, 162270. [Google Scholar] [CrossRef] [PubMed]
  27. Beauger, A.; Voldoire, O.; Allain, E.; Gosseaume, P.; Blavignac, C.; Baker, L.-A.; Wetzel, C.E. Biodiversity and Environmental Factors Structuring Diatom Assemblages of Mineral Saline Springs in the French Massif Central. Diversity 2023, 15, 283. [Google Scholar] [CrossRef]
  28. Angel, A.; Vila, I.; Diaz, C.; Molina, X.; Sepulveda, P. Geothermal diatoms: Seasonal variability in the El Tatio geothermal field (Altiplano, Chile). Adv. Microbiol. 2018, 8, 211–234. [Google Scholar] [CrossRef]
  29. Abdelwahab, H.E.M.; Amin, A.S. Diatoms diversity of thermal springs in the southwest region, Saudi Arabia. Egypt. Acad. J. Biolog. Sci. 2017, 8, 59–74. [Google Scholar] [CrossRef]
  30. Barinova, S.; Romanov, R. The Ein El Balad charophyte locality in the Mount Carmel Biosphere Reserve, Israel. Int. J. Adv. Res. Bot. 2015, 1, 1–12. [Google Scholar]
  31. Gerloff, J.; Natour, R.M.; Ivera, P. Diatoms from Jordan. Willdenowia 1978, 8, 261–316. [Google Scholar]
  32. Mirzahasanlou, J.P.; Musaabad, L.A.; Mahmoodlu, M.G.; Bahalkeh, A. An ecological and hydrochemical study of three springs in NE Iran with the emphasis on diatom diversity. Limnologica 2021, 90, 125908. [Google Scholar] [CrossRef]
  33. Coste, M.; Riaux-Gobin, C.; Riaux, J.; Saenz-Ag udelo, P.; Massuel, S.; Ector, L.; Calvez, R.; Ben Aïssa, N. Aïn Bou Rkhiss and Aïn Kibrbrit, two springs from the Merguellil basin (Kairouan, Central Tunisia): Diatom assemblages, biological polluosensitivity indices, hydrogeology and societal aspects. Vie Et Milieu-Life Environ. 2019, 69, 1–17. [Google Scholar]
  34. Shaaban, A.S. Freshwater Algae of Egypt. In Biological Diversity of Egypt; The United Nations Environmental Programme, The Egyptian Environmental Affairs Agency: Cairo, Egypt, 1994; 150p. [Google Scholar]
  35. Hamed, A.F. Biodiversity and distribution of blue-green algae/cyanobacteria and diatoms in some of the Egyptian water habitats in relation to conductivity. Aust. J. Basic Appl. Sci. 2008, 2, 1–21. [Google Scholar]
  36. Saleh, A.I. Biodiversity of Order Naviculales (Bacillariophycophyta) in Egypt. Ph.D. Thesis, Faculty of Science, Ain Shams University, Cairo, Egypt, 2009. [Google Scholar]
  37. Shaaban, A.S.; Hamed, A.F. The algal flora of the euthermal spring: Ain El-Sokhna. In Proceedings of the 9th Conference of Microbiology, Cairo, Egypt, 25–27 March 1997. [Google Scholar]
  38. Shaaban, A.S.; Hamed, A.F. Fresh-water algae of El-Arish valley and its vicinity (North Sinai), Egypt. Desert Inst. Bull. 1997, 47, 101–118. [Google Scholar]
  39. Shaaban, A.S. The algal flora of Egyptian oases. II-On the algae of Siwa oasis. In Proceedings of the Egyptian Botanical Society, Ismaileyah, Egypt, 16–19 April 1985; Volume 4, pp. 1–10. [Google Scholar]
  40. Shaaban, A.S.; Hamed, A.F.; Fumanti, B. The algal flora of Egyptian Oases. III-The algal flora of the thermal springs of Bahariya oasis. Egypt. J. Aquat. Biol. Fish. 1997, 1, 85–98. [Google Scholar] [CrossRef]
  41. Hofmann, G.; Lange-Bertalot, H.; Werum, M.; Klee, R. Rote Liste der limnischen Kieselalgen. Naturschutz Und Biol. Vielfalt 2018, 70, 601–708. [Google Scholar]
  42. Foets, J.; Stanek-Tarkowska, J.; Teuling, A.J.; Van de Vijver, B.; Wetzel, C.E.; Pfister, L. Autecology of terrestrial diatoms under anthropic disturbance and across climate zones. Ecol. Indic. 2021, 122, 107248. [Google Scholar] [CrossRef]
Figure 1. (AR) Type material of Navicula aquaesuavis sp. nov. from a spring in the Apennines, Italy. LM micrographs of valves showing the size diminution series. Scale bar = 10 µm.
Figure 1. (AR) Type material of Navicula aquaesuavis sp. nov. from a spring in the Apennines, Italy. LM micrographs of valves showing the size diminution series. Scale bar = 10 µm.
Water 16 02751 g001
Figure 2. (AC) SEM micrographs of Navicula aquaesuavis sp. nov.; (DF) SEM micrographs of Navicula metareichardtiana shown for comparison. (A,B,D,E) outside view. Black arrow: central nodule. White arrow: distal raphe endings; (C,F) inside view. Black arrow: distal raphe endings terminate in a helictoglossa. White arrow: central ends lying in an elongated nodule. Scale bars = 4 µm.
Figure 2. (AC) SEM micrographs of Navicula aquaesuavis sp. nov.; (DF) SEM micrographs of Navicula metareichardtiana shown for comparison. (A,B,D,E) outside view. Black arrow: central nodule. White arrow: distal raphe endings; (C,F) inside view. Black arrow: distal raphe endings terminate in a helictoglossa. White arrow: central ends lying in an elongated nodule. Scale bars = 4 µm.
Water 16 02751 g002
Figure 3. LM micrographs of Navicula aquaesuavis from Lake Bogovinsko on Shara Mountain, North Macedonia. Scale bar = 10 µm.
Figure 3. LM micrographs of Navicula aquaesuavis from Lake Bogovinsko on Shara Mountain, North Macedonia. Scale bar = 10 µm.
Water 16 02751 g003
Figure 4. (AF) SEM micrographs of Navicula aquaesuavis from Lake Bogovinsko on Shara Mountain, North Macedonia. Scale bars = 2 µm.
Figure 4. (AF) SEM micrographs of Navicula aquaesuavis from Lake Bogovinsko on Shara Mountain, North Macedonia. Scale bars = 2 µm.
Water 16 02751 g004
Figure 5. Light and SEM micrographs of the most common Navicula species inhabiting the Egyptian springs and drilled wells. (A) Navicula cf. arctotenelloides from a thermal freshwater drilled well known as ‘Bir Sitta’ in El-Farafra Oasis. (B) N. cryptotenelloides from a slightly hot freshwater drilled well known as ‘Bir 1B’ at Abu Minqar village in El-Farafra Oasis. (C) N. cryptocephala from a freshwater spring in the Bahariya Oasis. (D) N. erifuga from the thermal mineral-rich spring ‘Hammam Musa’. (E) N. rhynchocephala from the rheocrenic, slightly hot freshwater spring ‘Ain El-Balad’ in the El-Farafra Oasis. (F) N. tenelloides from a slightly hot freshwater drilled well known as ‘Bir 3A’ at Esha Abd El-Rahman village in the El-Farafra Oasis. (G) N. veneta from the rheocrenic thermal mineral-rich spring ‘Ain Helwan’, south of Cairo, Egypt. (H,I) External and internal valve views of N. cryptocephala at ‘Bir Sitta’ in El-Farafra Oasis. (J) External valve of an entire valve of N. veneta at ‘Bir Sitta’ in El-Farafra Oasis. All the micrographs were taken from diatom specimens collected in 2015 from the El-Farafra Oasis (the Western Desert of Egypt), except Figures (C,D,G), which were obtained after Hamed [35]. Scale bars: LM = 10 µm; SEM = 5 µm.
Figure 5. Light and SEM micrographs of the most common Navicula species inhabiting the Egyptian springs and drilled wells. (A) Navicula cf. arctotenelloides from a thermal freshwater drilled well known as ‘Bir Sitta’ in El-Farafra Oasis. (B) N. cryptotenelloides from a slightly hot freshwater drilled well known as ‘Bir 1B’ at Abu Minqar village in El-Farafra Oasis. (C) N. cryptocephala from a freshwater spring in the Bahariya Oasis. (D) N. erifuga from the thermal mineral-rich spring ‘Hammam Musa’. (E) N. rhynchocephala from the rheocrenic, slightly hot freshwater spring ‘Ain El-Balad’ in the El-Farafra Oasis. (F) N. tenelloides from a slightly hot freshwater drilled well known as ‘Bir 3A’ at Esha Abd El-Rahman village in the El-Farafra Oasis. (G) N. veneta from the rheocrenic thermal mineral-rich spring ‘Ain Helwan’, south of Cairo, Egypt. (H,I) External and internal valve views of N. cryptocephala at ‘Bir Sitta’ in El-Farafra Oasis. (J) External valve of an entire valve of N. veneta at ‘Bir Sitta’ in El-Farafra Oasis. All the micrographs were taken from diatom specimens collected in 2015 from the El-Farafra Oasis (the Western Desert of Egypt), except Figures (C,D,G), which were obtained after Hamed [35]. Scale bars: LM = 10 µm; SEM = 5 µm.
Water 16 02751 g005
Table 1. List of Navicula species selected with >three records and >1.2% max abundance with their weighted averages in the epibryon. In bold are species that were relevant only in the epibryon.
Table 1. List of Navicula species selected with >three records and >1.2% max abundance with their weighted averages in the epibryon. In bold are species that were relevant only in the epibryon.
Navicula SpeciesElevation [m a.s.l.] T [°C] Discharge [L s−1] pH Conductivity [µS cm−1] N-NO3
[µg L−1]
SO42−ClCa2+Mg2+Na+K+
N. antonii12477.54.37.710950.6603.52.8233.544.13.61.4
N. cryptocephala7126.968.67.71920.44.41.229.26.51.10.4
N. cryptotenella6698.93.67.92680.63.50.842.712.00.50.3
N. dealpina6259.90.97.73581.311.48.861.012.95.01.5
N. exilis8937.432.06.5860.76.64.79.01.23.21.0
N. leistikowii14355.58.37.81810.55.70.731.66.11.10.4
N. lundii15425.58.26.7480.311.90.415.75.41.00.6
N. moenofranconica7198.11.47.83941.011.016.462.410.48.81.0
N. tripunctata4649.71.67.82821.010.51.741.712.71.40.5
Table 2. List of Navicula species selected with >three records and >1.2% max abundance with their weighted averages in the epilithon.
Table 2. List of Navicula species selected with >three records and >1.2% max abundance with their weighted averages in the epilithon.
Navicula SpeciesElevation [m a.s.l.] T [°C] Discharge [L s−1] pH Conductivity [µS cm−1] N-NO3
[µg L−1]
SO42−ClCa2+Mg2+Na+K+
N. antonii8098.407.65642.070.84.983.321.53.20.9
N. cryptocephala6866.51197.91790.31.90.532.65.90.20.2
N. cryptotenella4499.657.63161.16.72.866.64.42.00.6
N. exilis8997.71046.61090.74.15.810.61.82.30.9
N. leistikowii6859.077.92680.31.70.544.811.60.30.3
N. tripunctata42210.317.56992.835.14.960.524.65.02.3
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Cid-Rodríguez, M.; Cantonati, M.; Angeli, N.; Bilous, O.; Al-Harbi, M.; Lange-Bertalot, H.; Levkov, Z.; Piana, L.; Spitale, D.; Saber, A.A. The Diatom Genus Navicula in Spring Ecosystems with the Description of Navicula aquaesuavis sp. nov. Water 2024, 16, 2751. https://doi.org/10.3390/w16192751

AMA Style

Cid-Rodríguez M, Cantonati M, Angeli N, Bilous O, Al-Harbi M, Lange-Bertalot H, Levkov Z, Piana L, Spitale D, Saber AA. The Diatom Genus Navicula in Spring Ecosystems with the Description of Navicula aquaesuavis sp. nov. Water. 2024; 16(19):2751. https://doi.org/10.3390/w16192751

Chicago/Turabian Style

Cid-Rodríguez, María, Marco Cantonati, Nicola Angeli, Olena Bilous, Maha Al-Harbi, Horst Lange-Bertalot, Zlatko Levkov, Lucia Piana, Daniel Spitale, and Abdullah A. Saber. 2024. "The Diatom Genus Navicula in Spring Ecosystems with the Description of Navicula aquaesuavis sp. nov." Water 16, no. 19: 2751. https://doi.org/10.3390/w16192751

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop