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. 2008 Jun 4;4:7. doi: 10.1186/1746-1448-4-7

Rotifers from selected inland saline waters in the Chihuahuan Desert of México

Elizabeth J Walsh 1,✉, Thomas Schröder 1, Robert L Wallace 2, Judith V Ríos-Arana 3, Roberto Rico-Martínez 4
PMCID: PMC2441627  PMID: 18533042

Abstract

Background

In spite of considerable efforts over past decades we still know relatively little regarding the biogeography of rotifers of inland waters in México. To help rectify this we undertook an extensive survey of the rotifer fauna of 48 water bodies in the Chihuahuan Desert of México.

Results

Of the sites surveyed, 21 had salinities ≥ 2000 μS cm-1 and in these we found 57 species of monogonont rotifers and several bdelloids. Species richness in the saline sites varied widely, with a range in species richness of 1 to 27 and a mean (± 1SD) = 8.8 (± 6.2). Collectively all sites possess relatively high percent single- and doubletons, 33.3 and 21.7%, respectively. Simpson's Asymmetric Index indicated that similarity in rotifer species composition varied widely among a set of 10 sites. These were selected because they were sampled more frequently or represent unusual habitats. These SAI values ranged from 0.00 (complete dissimilarity) to 1.00 (complete similarity). The Jaccard Index varied between 0.00 and 0.35. This observation probably reflects similarities and differences in water chemistry among these sites. Inland saline systems differed in their chemical composition by region. Conductivity was related to hardness and alkalinity. In addition, hardness was positively associated with chloride and sulfate. RDA showed that several species were positively associated with chloride concentration. Other factors that were significantly associated with rotifer species included the presence of macrophytes, nitrate content, oxygen concentration, TDS, latitude and whether the habitat was a large lake or reservoir.

Conclusion

This study illustrates the diversity of the rotiferan fauna of inland saline systems and the uniqueness among waterbodies. Conservation of these systems is needed to preserve these unique sources of biodiversity that include rotifers and the other endemic species found in association with them.

Background

Rotifers are widely recognized as being important components of freshwater ecosystems, and whether this assessment is based on numbers or biomass, their contribution to trophic dynamics in these waters is striking. In some instances their importance even exceeds that of the microcrustaceans: cladocerans and copepods [1]. In estuarine and marine habitats, rotifers are generally thought to play a minor role in community dynamics [2-5]. Therefore brackish and marine rotifers, with the notable exception of the Brachionus plicatilis species complex, have received little attention worldwide. Because of its value in aquaculture [6-8], this species complex has received special attention and this intense study has yielded valuable insights into evolutionary processes such as cryptic speciation and molecular phylogenetics [9-12] and genomics [13]. In addition, rotifer species inhabiting saline and subsaline lakes in northern Canada possessed greater haplotype diversity than their freshwater counterparts [14].

While quite a bit is known about zooplankton present in México (e.g., copepods [15,16]; cladocerans [17], few reports have been published on brackish and marine rotifers [3,18,19]. Although some of these studies have focused on species diversity and community dynamics [4], none of them have included the Chihuahuan Desert.

With increased exploitation of aquifers for agriculture, cattle, industry, and drinking water, we can expect an increase in the salinization of existing watersheds and water sources particularly in arid areas. These changes will negatively impact ecosystem processes [20]. Here we examine selected inland saline waters in the Chihuahuan Desert of México, a region renowned for its high biodiversity in terrestrial and aquatic systems [21-24]. We also present an initial species list of the rotifers, group sites by water chemistry, conduct pair-wise comparisons of rotifer community diversity between sites, and investigate ecological correlates of rotifer presence/absence.

Results

Water chemistries

With the exception of Cuatro Ciénegas (CC), sites in different regions cluster together as expected from their shared basins and geochemistries (Figs. 1, 2, 3, 4). The variety of water sources (springs, playas, rivers, seeps, wetlands) sampled at CC likely explains the spread in the data for these systems. In general these systems have higher conductivity, chloride, and sulfate than the others. Sulfate and chloride were positively associated with hardness in all sites. Alkalinity was less variable than other selected parameters.

Figure 1.

Figure 1

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Characterization of study sites by water chemistry. Upper left panel - conductivity, chloride, and sulfate; upper right panel - conductivity, hardness, and alkalinity; lower left panel - hardness, chloride, and alkalinity; lower right panel - hardness, sulfate, and chloride. Sampling regions: black - San Luis Potosί; dark grey- Cuatro Ciénegas; white - Ojos Altos; light grey - Ojos en de Medio, de la Punta, de la Casa, Caliente (Camargo); cross hatched - Presa Chihuahua, Presa la Boquilla, Presa Francisco I. Madero, Lago Colina; hatched - Méxican spring flowing into Rio Grande downstream of Big Bend National Park (TX, USA).

Figure 2.

Figure 2

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RDA of all Méxican sites. Left panel: ordination of species; Right panel: ordination of samples. Sampling regions: black – San Luis Potosí; dark grey – Cuatro Ciénegas; white – Ojos Altos; light grey – Ojos en Medio, de la Punta, de la Casa, Caliente (Camargo); cross hatched – Presa Chihuahua, Presa la Boquilla, Presa Francisco I. Madero, Lago Colina; hatched – Mexican site south of Big Bend National Park (TX, USA).

Figure 3.

Figure 3

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RDA of Méxican sites with conductivity ≥2000 µS cm-1. Left panel: ordination of species; * these species share a vector with other species: BracBide with PolyDoli, PolyVulg, GastStyl; CollCrat with CephPan, LecaCorn; TrioTetr with PlatQuad; Right panel: ordination of samples. Sampling regions: black - San Luis Potosί; dark grey - Cuatro Ciénegas; white - Ojos Altos; light grey - Ojo Caliente (Camargo).

Figure 4.

Figure 4

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RDA of Méxican sites with conductivity ≥3000 µS cm-1. Left panel: ordination of species; * these species share a vector with other species: HeteHete with LecaCrep, LecaUndu; ColuUnci with TrioTetr, DicrForc, PlatQuad; CephForf with TripPlic, LecaArcu; Right panel: ordination of samples. Sampling regions: black - San Luis Potosί; dark grey - Cuatro Ciénegas; white - Ojos Altos; light grey - Ojo Caliente (Camargo).

Site similarities in species richness

We found 57 species of monogonont rotifers in aquatic systems with salinities >2000 μS cm-1, and, of these, 34 also were present when salinities were ≥ 3000 μS cm-1 (Table 1). In addition, we found many bdelloid species, but only Philodina megalotrocha was identified to species. For new records in México and total species count see [25]. Many of these species occurred as singletons (33.3%) or doubletons (21.7%), a feature that has been reported previously [25]. When comparing species composition between sites using the Simpson's Asymmetric similarity Indices (SAI), we found values ranging from 0.00 to 1.00. An SAI of 1.00 indicates complete unity of one site to the next, while SAI = 0.00 means complete dissimilarity of one site to the next (Table 2). The Jaccard Index also varied greatly among sites (i.e., 0.00 and 0.35, Table 3). In general, sites at Cuatro Ciénegas were quite distinct from those near Ciudad Juárez, MX. For example, disparity in SAI values between Ojos Altos A (site 1) and several sites at CC (sites 18–27) can be attributed to the paucity of species in the former and the richer fauna in the later (Table 2). A few sites had SAI values reflecting similarity in species composition: e.g., Rio Mesquites (site 18) and Las Playitas (site 27) and Los Hundidos (site 24) and Los Gatos (site 26) had reciprocal pairwise SAI values of approximate 0.5 (Table 2). Such similarity in rotifer fauna probably reflects the similarity in water chemistry of these sites, which is high in CaSO4.

Table 1.

Species found in high salinity aquatic habitats in México (*found at salinities ≥ 3000 μS cm-1)

Number Species Abbreviation Sites found
1 Adineta sp. * AdinSp 34
2 Anuraeopsis fissa* Gosse, 1851 AnurFiss 22, 26, 45
3 Ascomorpha saltans Bartsch, 1870 AscoSalt 17, 21
4 Brachionus angularis* Gosse, 1851 BracAngu 42, 45
5 Brachionus bidentatus* Anderson, 1889 BracBide 45
6 Cephalodella sp.* CephSp 27
7 Cephalodella forficula* (Ehrenberg, 1832) CephForf 20, 21
8 Cephalodella gibba* (Ehrenberg, 1832) CephGibb 18, 20, 22, 23, 27
9 Cephalodella gracilis* (Ehrenberg, 1832) CephGrcl 3, 34
10 Cephalodella cf. graciosa Wulfert, 1951 CephGrac 21
11 Cephalodella megalocephala* (Glascott, 1893) CephMega 17, 20, 23, 26, 27, 28
12 Cephalodella panarista Myers, 1924 CephPana 22
13 Cephalodella sterea* (Gosse, 1887) CephSter 3, 4, 20
14 Collotheca crateriformis Offord, 1934 CollCrat 22
15 Colurella colurus (Ehrenberg, 1930) ColuColu 24, 26
16 Colurella obtusa* (Gosse, 1886) ColuObtu 3, 4, 17, 18, 34
17 Colurella uncinata (Müller, 1773) ColuUnci 20, 21, 22
18 Dicranophorus forcipatus (O.F. Müller, 1786) DicrForc 20, 23
19 Eosphora ehrenbergi* Weber & Montet, 1918 EospEhre 20, 26, 27
20 Euchlanis dilatata Ehrenberg, 1832 EuchDila 28, 44
21 Gastropus stylifer* (Imhof, 1891) GastStyl 45
22 Hexarthra oxyuris* (Sernov, 1903) HexaOxyu 24, 26, 35
23 Keratella americana Carlin, 1943 KeraAmer 17
24 Lecane aeganea Harring, 1914 LecaAega 4
25 Lecane arcula* Harring, 1914 LecaArcu 20, 43, 44
26 Lecane bulla* (Gosse, 1851) LecaBull 3, 17, 18, 19, 20, 21, 22, 23, 24, 26, 27, 28, 34, 44
27 Lecane closterocerca* (Schmarda, 1859) LecaClos 3, 20, 22, 34, 43
28 Lecane cornuta (O.F. Müller, 1786) LecaCorn 22
29 Lecane crepida Harring, 1914 LecaCrep 24, 44
30 Lecane hornemanni* (Ehrenberg, 1834) LecaHorn 3, 20, 34
31 Lecane inermis* (Bryce, 1892) LecaIner 3, 21, 24
32 Lecane leontina (Turner, 1892) LecaLeot 21, 44
33 Lecane luna* (O.F. Müller, 1776) LecaLuna 17, 20, 21, 22, 23, 26, 35
34 Lecane lunaris* (Ehrenberg, 1832) LecaLunr 3, 17, 18, 20, 26
35 Lecane nana* (Murray, 1913) LecaNana 17, 20
36 Lecane obtusa* (Murray, 1913) LecaObtu 20, 21, 26
37 Lecane punctata (Murray, 1913) LecaPunc 17, 21
38 Lecane pyriformis (Daday, 1905) LecaPyri 3, 17
39 Lecane quadridentata* (Ehrenberg, 1832) LecaQuad 20, 22, 45
40 Lecane spinulifera* Edmondson, 1935 LecaSpin 21, 24, 26
41 Lecane thalera (Harring & Meyers, 1924) LecaThal 3, 17, 19, 26
42 Lepadella (= Heterolepadella) heterostyla* (Murray, 1914) HeteHete 24
43 Lecane undulata * Segers & Dumont, 1993 LecaUndu 3, 4, 24
44 Lepadella ovalis/patella* (O.F. Müller, 1786) LepaOvPa 1, 2, 3, 4, 17,18, 19, 20, 21, 22, 23, 24, 26, 27, 35
45 Lepadella triptera* (Ehrenberg, 1830) LepaTrip 17, 20, 21, 26
46 Notholca acuminata* (Ehrenberg, 1832) NothAcum 20, 22, 23, 24, 26
47 Notommata tripus Ehrenberg, 1838 NotoTrip 21
48 Philodina megalotrocha* Ehrenberg, 1832 PhilMega 18, 20, 21, 28
49 Platyias quadricornis (Ehrenberg, 1832) PlatQuad 20
50 Polyarthra dolichoptera* Idelson, 1925 PolyDolic 45
51 Polyarthra vulgaris* Carlin, 1943 PolyVulg 45
52 Proales similis* de Beauchamp, 1907 ProaSimi 20, 27, 24, 34
53 Proales sordida Gosse, 1886 ProaSord 18
54 Proales cf. wesenbergi Wulfert, 1960 ProaWese 21
55 Resticula melandocus (Gosse, 1887) RestMela 23
56 Scaridium bostjani* Daems & Dumont, 1974 ScarBost 20, 28
57 Trichocerca cf. intermedia* (Stenroos, 1898) TricInte 18, 20, 23
58 Trichotria tetractis (Ehrenberg, 1830) TricTetr 20
59 Tripleuchlanis plicata (Levander, 1894) TripPlic 20
60 Unidentified bdelloids* Bdel 1, 2, 3, 4, 17, 18, 19, 20, 21, 23, 24, 26, 27, 28, 34, 43, 44
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Locality codes: Ojos Altos A* (1), Ojos Altos B (2), Ojos Altos C (3), Ojos Altos D (4), Poza la Becerra (17), Rio Mesquites*(18), Poza Azul (19), Poza Tortugas* (20), Poza Churince (21), Entrance to Ejido El Venado (22), Tio Julio (23), Los Hundidos Main pool* (24), Los Gatos* (26), Las Playitas* (27), wetland north of Los Hundidos*(28), Poza Los Arcos* (34), La Campaña*(35), Rio la Lloviznosa (42), Manantial los Peroles (43), Manantial San Sebastian (44), San Francisco Cattle Tank*(45). Note: For complete list of species found in all Méxican sites sampled contact the corresponding author.

Table 2.

Simpson's asymmetric percent similarity indices (SAI) for 10 selected sites* in the Méxican Chihuahuan Desert

Sites 1 18 20 24 26 27 28 34 35 45
1 -- 1.00 1.00 1.00 1.00 1.00 0.50 0.50 0.50 0.00
18 0.22 -- 0.78 0.33 0.38 0.44 0.33 0.22 0.11 0.00
20 0.07 0.26 -- 0.19 0.37 0.23 0.19 0.15 0.04 0.04
24 0.17 0.25 0.42 -- 0.58 0.33 0.17 0.17 0.17 0.00
26 0.07 0.21 0.67 0.47 -- 0.33 0.14 0.07 0.13 0.07
27 0.25 0.50 0.86 0.50 0.63 -- 0.38 0.25 0.13 0.00
28 0.17 0.50 0.83 0.33 0.40 0.50 -- 0.17 0.00 0.00
34 0.14 0.29 0.57 0.29 0.14 0.29 0.14 -- 0.00 0.00
35 0.50 0.50 0.50 1.00 1.00 0.50 0.00 0.00 -- 0.00
45 0.00 0.00 0.14 0.00 0.14 0.00 0.00 0.00 0.00 --
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* Site numbers are the same as reported in Table 1. Upper right half of table: SAI for the first versus the second site (e.g., 1 v. 2; 1 v. 3; 9 v. 10). Mean (± 1SD) = 0.30 (0.31). Lower left half of table: SAI for the second versus the first site (e.g., 2 v. 1; 3 v. 1; 10 v. 9). Mean = 0.32 (0.28).

Table 3.

Jaccard Index for 10 selected sites* in the Méxican Chihuahuan Desert

Sites 1 18 20 24 26 27 28 34 35 45
1 -- 0.22 0.07 0.17 0.07 0.25 0.14 0.13 0.33 0.00
18 -- 0.24 0.17 0.16 0.31 0.25 0.14 0.10 0.00
20 -- 0.15 0.31 0.22 0.18 0.13 0.04 0.03
24 -- 0.35 0.25 0.13 0.12 0.17 0.00
26 -- 0.28 0.12 0.05 0.13 0.05
27 -- 0.27 0.15 0.11 0.00
28 -- 0.08 0.00 0.00
34 -- 0.00 0.00
35 -- 0.00
45 --
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* Site numbers are the same as reported in Table 1. The mean Jaccard Similarity Index for the same sites = 0.13 (0.10).

Ecological correlations

In terms of ecological parameters, the first four canonical axes in the RDA of all Méxican sites explained 14.2% of the variance in the species data (Table 4). The most important environmental variable in the model was whether or not the habitats were reservoirs or large lakes. None of the saline sites sampled belonged to this habitat type (Fig. 2, right panel). Species assemblages found at sites other than lakes or reservoirs were ordinated with chloride concentration, nitrate concentration, oxygen concentration, and presence of many macrophytes. In general, most samples from CC were positively correlated with these variables, whereas samples from the Ojos Altos and San Luis Potosí were negatively correlated.

Table 4.

Summary of RDA statistics for the first four axes of all Méxican sites

Axis 1 Axis 2 Axis 3 Axis 4
Eigenvalues 0.048 0.042 0.029 0.023
Species-environment correlations 0.802 0.649 0.717 0.720
Cumulative percentage variance of species data 4.8 9.0 12.0 14.2
Cumulative percentage of species-environment relation 27.4 51.4 68.1 81.1
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Rotifer species that were ordinated together with the variable lakes/reservoirs included many planktonic species, such as Keratella cochlearis, Trichocerca rattus, T. similis, Polyarthra cf. luminosa, P. euryptera, P. vulgaris, P. remata, Asplanchna girodi, A. brightwellii, S. oblonga, and S. pectinata (Fig. 2, left panel). Species that were positively associated with chloride are Notholca acuminata, Dicranophorus forcipatus, Collotheca crateriformis, Cephalodella panarista, Lecane cornuta and Lepadella ovalis/patella.

The RDA performed on the dataset of sites with conductivity ≥ 2000 μS cm-1 separates species assemblages at CC from those found in the Ojos Altos and at San Luis Potosí, respectively (Fig. 3, right panel), with 21.2% of the variance in the species data being explained by the first four canonical axes (Table 5). Species assemblages of different sites at CC vary more than those at the other sampling regions and are ordinated along gradients formed by the presence of macrophytes and chloride concentration, nitrate concentration, seasonality (summer) and TDS. Species found mostly in the Ojos Altos and San Luis Potosí and negatively correlated with chloride are L. aeganea, B. bidentatus, P. dolichoptera, and P. vulgaris (Fig. 2, left panel). In CC sites a large group of species is ordinated with presence of macrophytes and chloride concentration: L. bulla, Philodina megalotrocha, Cephalodella megalocephala, Lecane punctata and L. closterocerca. Another group of species was correlated with seasonality (summer): Lecane obtusa, L. lunaris, Lepadella triptera, Hexarthra oxyuris, Proalis similis, Eosphora ehrenbergi, and Euchlanis dilatata.

Table 5.

Summary of RDA statistics for the first four axes of Méxican sites with a conductivity ≥ 2000 μS cm-1

Axis 1 Axis 2 Axis 3 Axis 4
Eigenvalues 0.102 0.057 0.028 0.025
Species-environment correlations 0.791 0.790 0.651 0.674
Cumulative percentage variance of species data 10.2 15.9 18.7 21.2
Cumulative percentage of species-environment relation 43.4 67.7 79.6 90.4
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The RDA of the dataset containing the sites with conductivity ≥ 3000 μS cm-1 again identified chloride, the presence of macrophytes, alkalinity, and site order, as the most important variables explaining the variance in the species data (Fig. 3). Site order signifies that the waterbody consisted of a series of pools that were ordered downstream from the spring source. In this analysis 30.4% of the total variance can be explained by the first four canonical axes (Table 6). Occurrence of Lecane spinulifera, Colurella colurus, Hexarthra oxyuris, Eosphora ehrenbergi, Proales similis, and bdelloids at CC sites was positively correlated with alkalinity and chloride concentration, whereas the majority of species correlated with presence of macrophytes included Philodina megalotrocha, Cephalodella forficula, Colurella uncinata, Dicranophorus forcipatus, Lecane arcula, Platyias quadricornis, Scaridium bostjani, Trichocerca intermedia, Trichotria tetractis, and Tripleuchlanis plicata. Brachionus bidentatus, B. angularis, P. dolichoptera, P. vulgaris, and Gastropus stylifer were found in San Francisco cattle tank (San Luis Potosí) and were negatively correlated with chloride.

Table 6.

Summary of RDA statistics for the first four axes of Méxican sites with a conductivity ≥ 3000 μS cm-1

Axis 1 Axis 2 Axis 3 Axis 4
Eigenvalues 0.142 0.091 0.041 0.029
Species-environment correlations 0.858 0.935 0.793 0.756
Cumulative percentage variance of species data 14.2 23.4 27.4 30.4
Cumulative percentage of species-environment relation 46.39 77.0 90.4 100.0
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Discussion

While zooplankton inhabiting saline aquatic habitats have received some attention worldwide (e.g., China [5], Spain [26-29], Canada [14,30], Western US [31,32], Africa [33-36], Japan [37], Australia [38-41], Arabia [42]), there is a genuine need for additional studies of rotifers in saline and marine environments of México [3]. A recent study noted that 74% of rotifer species in México (n = 42) were cosmopolitan, 5% were restricted to North America, 10% were tropical, and 4% were shared with Europe-Asia-Africa [43]. Most work on rotifers in saline habitats in México has been done by Sarma and his colleagues. For example, Sarma & Elías-Gutiérrez [44] found 31 rotifer species in their survey of an estuarine lagoon; 11 of which were found in our study (Platyias quadricornis, Tripleuchlanis plicata, Colurella uncinata, Lepadella ovalis, Lecane bulla, L. closterocerca, L. hornemanni, L. luna, L. obtusa, L. pyriformis, and L. thalera). In addition, Sarma et al. [3] reported 37 species of rotifers in Mecoacan, a brackish (5–35 ‰) lagoon located in Tabasco. Our survey of 48 waterbodies in the Mexican Chihuahuan desert shared few of these species (Anuraeopsis fissa, Ascomorpha saltans, Brachionus angularis, Euchlanis dilatata, and Lecane bulla) all of which have reportedly cosmopolitan distributions [45]. Another recent study [19] reported 128 taxa from 36 aquatic sites in southeastern México including some brackish habitats. Of these species, 23 (A. fissa, B. bidentatus, C.obtusa, C. uncinata, E. dilatata, K. americana, L. arcula, L. bulla, L. closterocerca, L. cornuta, L. crepida, L. hornemanni, L. leontina, L. luna, L. lunaris, L. obtusa, L. spinulifera, L. thalera, L. triptera, Platyias quadricornis, Polyarthra dolichoptera, Scaridium bostjani and Tripleuchlanis plicata) also were found in our survey.

In a larger study of freshwater habitats in the Méxican Chihuahuan Desert that includes the sites reported here, Wallace et al. [25] note that many species occurred as singletons or doubletons, and species inhabiting particular sites are quite unique. Here we further address community similarity among high salinity habitats using the SAI, and again the uniqueness of communities is apparent (Table 2). While our study adds substantially to the characterization of rotifer communities, clearly much more research needs to be accomplished if we are to develop a good understanding of the biogeography of rotifers in saline waters in North America.

The saline systems in the Mexican part of the Chihuahuan Desert have less total dissolved solids and lower conductivity than some of the waters of the Northern Chihuahuan Desert in the United States, notably those at White Sands National Monument, New Mexico and the Bottomless Lakes near Roswell, New Mexico. Only few species typical for saline waters were found over a wide range of aquatic habitats in the Chihuahuan Desert, such as Proales similis. However, a redundancy analysis performed on the data of all the saline systems that we have sampled in the Chihuahuan Desert, showed that the presence or absence of macrophytes is an important variable in determining species composition in all of these systems (unpublished data).

High salinity and conductivity levels can have major impacts on zooplankton community structure. A study in coastal lakes found that salinity level had significant impacts on zooplankton [46], leading the authors to predict that relatively small increases in salinity levels will cause reduced biodiversity of freshwater ecosystems. In a mesocosm experiment manipulating salinity, Hart et al. [31] found dramatic shifts in zooplankton community structure and shifts in the abundance of many species. As salinity increased, densities of the dominant rotifer species decreased and at the highest salinities 2 species were reduced to very low numbers. Shiel and his colleagues found that salinity was a significant, but site-specific, factor in determining rotifer community composition in rivers in the Lake Eyre Basin [41]. Saline systems had reduced species richness compared to their freshwater analogs (0–4 versus 0–31). In the Mexican saline systems studied here, as salinity increases the number of species found decreases substantially (Table 1; Fig 1, 2, 3). Chloride is a significant factor in determining the occurrence of rotifers. Some species are positively correlated with chloride content and others negatively associated (see Results, Fig 2a, 3a). It appears in our systems that typical planktonic freshwater species (e.g., Asplanchna brightwellii, A. priodonta, K. americana, K. cochlearis, and Synchaeta pectinata) are replaced by salinity tolerant species such as Hexarthra oxyuris and Notholca acuminata.

Conclusion

Inland saline systems often harbor diverse and unique community assemblages. Unfortunately, human exploitation can be extremely disruptive to ecosystem processes and services provided by these important water sources. During our sampling efforts, several historical springs near Janos, México were dry. In addition, Ojo de la Casa has recently dried and Ojo en de Medio has dried and re-surfaced in the past year, probably due demands of a geothermal electrical plant for cooling water and agricultural and domestic uses. Increasing human population size and global climate change will only make this scenario more prevalent. Thus, it is imperative that governmental agencies establish policies that protect these fragile ecosystems [47].

Methods

Sampling strategy

As part of a larger study on Chihuahuan Desert waters [25,48-50] we sampled 48 sites in the Méxican portion of the Chihuahuan Desert. Sites included springs, cattle tanks, tinajas, rivers, reservoirs, and artificially constructed ponds. Some of these systems comprised multiple basins with varying degrees of inter-site connectivity. Of these, 11 sites had salinities ≥ 2000 μS cm-1, 10 additional sites had salinities from ≥ 3000 μS cm-1. It should be noted that sampling effort was not equal among all sites, some sites were sampled only once while others were sampled up to 7 times (Ojos Altos).

Our sampling strategy attempted to provide an All Taxa Biological Inventory (ATBI) [51]; to accomplish this we collected samples from planktonic, littoral, and benthic habitats using plankton nets (64 μm), grab samples (e.g., aquatic plants for sessile forms), and aspirating samplers. We calculated species richness (S), Jaccard's Similarity Index and Simpson's Index of Asymmetry [52,53]. The keys used in this study were as follows: Monogononta [54-64] and Bdelloidea [65,66]. Additional details of our methodology are described in [25,48,49].

Analysis

To compare physical aspects of the aquatic habitats sampled, we constructed three-way plots of selected water chemistry parameters. To investigate ecological correlates of species distributions we conducted Redundancy Analyses (RDA) using CANOCO for Windows 4.54 [67]. Three RDAs were done: one using the complete dataset of the 48 sites sampled, a second analysis with a subset of data including the sites with conductivity >2000 μS cm-1, and a third on a subset of data with sites with conductivity ≥ 3000 μS cm-1. Environmental variables were sequentially added to the model of each analysis when they provided extra fit to the model at a significance level of p < 0.05. The significance of variables was determined with Monte Carlo tests running 9999 permutations.

Competing interests

The authors declare that they have no competing interests.

Authors' contributions

EJW, TS, RLW, JVRA, and RRM all participated in collecting trips and in species identifications. EJW drafted the manuscript. TS ran the statistical analyses (three-way plots of water chemistry and Redundancy Analyses). RLW calculated the Jaccard's and Simpson's Asymmetric Indices. All authors read and approved the final manuscript.

Contributor Information

Elizabeth J Walsh, Email: ewalsh@utep.edu.

Thomas Schröder, Email: tschroeder@utep.edu.

Robert L Wallace, Email: wallacer@ripon.edu.

Judith V Ríos-Arana, Email: jrios@uacj.edu.

Roberto Rico-Martínez, Email: rrico@correo.uaa.mx.

Acknowledgements

M. Silva-Briano, A. Adabache, R. Galván-De la Rosa, N. Salas-Mercado, G. Santos-Medrano, R. deRegnier, A. Palomeque, G. Jimenez-Guerrero & M. Stensberg provided assistance in sampling. Adolfo Sosa & Hector Javier Gonzalez-Martínez helped locate several sampling sites at Cuatro Ciénegas, Chihuahua. Jeffrey Bennett at BBNP provided logistical support in sampling the hotspring in the lower canyons downstream of BBNP. H. Segers provided expert review of our species identifications. Collections were made under permit #09436 from the Secretario de Medio Ambiente y Recursos Naturales to M. Silva Briano. We thank the Comisión Federal de Electricidad for permission to sample Presa de la Boquilla. This material is based upon work partially supported by an American Association for the Advancement of Science Women's International Science Collaboration (WISC) travel grant award, the National Science Foundation under DEB #0516032, National Center for Research Resources (NCRR), a component of the National Institutes of Health (NIH) Grant Number 5G12RR008124. and ADVANCE #0245071 (UTEP), T & E, Inc., & Funds for Faculty Development (Ripon College). The contents are solely the responsibility of the authors and do not necessarily represent the official views of NSF, NCRR or NIH.

References

  1. Wallace RL, Snell TW, Ricci C, Nogrady T. In: Guides to the Identification of the Microinvertebrates of the Continental Waters of the World 23. Dumont HJ, editor. Leiden: Backhuys Publishers; 2006. Rotifera: Volume 1 Biology, Ecology and Systematics; pp. 1–299. [Google Scholar]
  2. Iltis A, Riou-Duvat S. Variations saisonniéres du peuplement en rotifères des eaux natronées du Kanem (Tchad) Cah OSTROM ser Hydrobiol. 1971;5/2:101–112. [Google Scholar]
  3. Sarma SSS, Nandini S, Ramírez PG, Cortés JEM. New records of brackish water Rotifera and Cladocera from Mexico. Hidrobiológica. 2000;10:121–124. [Google Scholar]
  4. Sarma SSS, Elguea-Sánchez B, Nandini S. Effect of salinity on competition between the rotifers Brachionus rotundiformis Tschugunoff and Hexarthra jenkinae (De Beauchamp) (Rotifera) Hydrobiologia. 2002;474:183–188. [Google Scholar]
  5. Wen Z, Zhi-Hui H. Biological and ecological features of inland saline waters in North Hebei, China. Internat J Salt Lake Res. 1999;8:267–285. [Google Scholar]
  6. Gallardo WG, Hagiwara A, Snell TW. Use of GABA to enhance rotifer reproduction in enrichment culture. Aquaculture Res. 2001;32:243–246. [Google Scholar]
  7. Kotani T, Ihara K, Hagiwara A. Cross-mating of euryhaline rotifer Brachionus plicatilis strains as a means to develop useful strains for larval fish food. Aquaculture. 2006;261:495–500. [Google Scholar]
  8. Lubzens E, Zmora O, Barr Y. Biotechnology and aquaculture of rotifers. Hydrobiologia. 2001;446/447:337–353. [Google Scholar]
  9. Gómez A, Carvalho GR, Lunt DH. Phylogeography and regional endemism of a passively dispersing zooplankter: Mitochondrial DNA variation in rotifer resting eggs. Proc R Soc Lond B. 2000;267:2189–2197. doi: 10.1098/rspb.2000.1268. [DOI] [PMC free article] [PubMed] [Google Scholar]
  10. Gómez A, Adcock GJ, Luna DH, Carvalho GR. The interplay between colonization history and gene flow in passively dispersing zooplankton: Microsatellite analysis of rotifer resting egg banks. J Evol Biol. 2002;15:158–171. [Google Scholar]
  11. Gómez A, Serra M, Carvalho GR, Lunt DH. Speciation in ancient cryptic species complexes: Evidence from molecular phylogeny of Brachionus plicatilis (Rotifera) Evolution. 2002;56:1431–1444. doi: 10.1111/j.0014-3820.2002.tb01455.x. [DOI] [PubMed] [Google Scholar]
  12. Suatoni E, Vicario S, Rice S, Snell T, Caccone A. An analysis of species boundaries and biogeographic patterns in a cryptic species complex: The rotifer – Brachionus plicatilis. Mol Phylo Evol. 2006;41:86–98. doi: 10.1016/j.ympev.2006.04.025. [DOI] [PubMed] [Google Scholar]
  13. Suga K, Mark Welch D, Tanaka Y, Sakakura Y, Hagiwara A. Analysis of Expressed Sequence Tags of the Cyclically Parthenogenetic Rotifer Brachionus plicatilis. PLoS ONE. 2007;2(8):e671. doi: 10.1371/journal.pone.0000671. doi:10:1371/journal.pone.0000671. [DOI] [PMC free article] [PubMed] [Google Scholar]
  14. Derry AM, Hebert PDN, Prepas EE. Evolution of rotifers in saline and subsaline lakes: A molecular phylogenetics approach. Limnol Oceanogr. 2003;48:675–685. [Google Scholar]
  15. Suárez-Morales E, Reid JW, Iliffe TM, Fiers F. Catálogo de los Copépodos (Crustacea) continentales de la Península de Yucatán, México. Comisión Nacional para el Conocimiento y Uso de la Biodiversidad (CONABIO) y El Colegio de la Frontera Sur (ECOSUR). México; 1996.
  16. Suárez-Morales E, Elías-Gutiérrez M. In: "Planctología Mexicana". Barreiro GMT, Meave DCME, Signoret PM, Figueroa TMG, editor. DF México: Sociedad Mexicana de Plancton (SOMPAC); 2003. Estado actual del conocimiento de los copépodos de aguas continentales de México; pp. 157–170. [Google Scholar]
  17. Elías-Gutiérrez M, Suárez-Morales E. In: "Planctología Mexicana". Barreiro GMT, Meave DCME, Signoret PM, Figueroa TMG, editor. DF México: Sociedad Mexicana de Plancton (SOMPAC); 2003. Estado actual del conocimiento de los cladóceros de México; pp. 171–184. [Google Scholar]
  18. Rico-Martínez R, Silva-Briano M. Contribution to the knowledge of the Rotifera of Mexico. Hydrobiologia. 1993;255:467–474. [Google Scholar]
  19. García-Morales AE, Elías-Gutiérrez M. Rotifera from southeastern Mexico, new records and comments on zoogeography. Anales del Instituto de Biología. Serie Zoología. 2004;75:99–120. [Google Scholar]
  20. Nielsen DL, Brock MA, Rees GN, Baldwin DS. Effects of increasing salinity on freshwater ecosystems in Australia. Aust J Bot. 2003;51:655–665. [Google Scholar]
  21. Dinerstein E, Olson D, Atchley J, Loucks C, Contreras-Balderas S, Abell R, Inigo Enkerlin E, Williams C, Castilleja G. Ecoregion-based conservation in the Chihuahuan Desert: A biological assessment. Washington DC: World Wildlife Fund; 2000. [Google Scholar]
  22. Minckley WL. In: Transactions of the Symposium on the Biological Resources of the Chihuahuan Desert region. Wauer RH, Riskind DH, editor. United States and Mexico; 1974. Endemic fishes of the Cuatro Ciénegas Basin, Northern Coahuila, Mexico; pp. 383–404. [Google Scholar]
  23. Hershler R. Systematic revision of the Hydrobiid snails (Gastropoda: Rissoacea) of the Cuatro Ciénegas Basin, Coahuila, Mexico. Malacologia. 1985;26:31–123. [Google Scholar]
  24. Souza V, Espinsoa-Asuar L, Escalante AE, Egularte LE, Farmer J, Forney L, Lloret L, Rodriguez-Martinez JM, Soberon X, Dirzo R, Elser JJ. An endangered oasis of aquatic microbial biodiversity in the Chihuahuan desert. PNAS. 2006;103:6565–6570. doi: 10.1073/pnas.0601434103. [DOI] [PMC free article] [PubMed] [Google Scholar]
  25. Wallace RL, Walsh EJ, Schröder T, Rico-Martínez R, Ríos-Arana JV. Species composition and distribution of rotifers in Chihuahuan Desert waters of México: is everything everywhere? Verh Internat Verein Limnol. in press .
  26. García CM, Echevarría F, Niell FX. Size structure of plankton in a temporary, saline inland lake. J Plankton Res. 1995;17:1803–1817. [Google Scholar]
  27. Serra M, Gómez A, Carmona MJ. Ecological genetics of Brachionus sympatric sibling species. Hydrobiologia. 1998;378/388:373–384. [Google Scholar]
  28. Ortells R, Gómez A, Serra M. Coexistence of cryptic species: ecological and genetic characterisation of Brachionus plicatilis. Freshw Biol. 2003;48:2194–2202. [Google Scholar]
  29. Gómez A, Montero-Pau J, Lunt DH, Serra M, Campillo S. Persistent genetic signatures of colonization in Brachionus manjavacas rotifers in the Iberian Peninsula. Mol Ecol. 2007;16:3228–3240. doi: 10.1111/j.1365-294X.2007.03372.x. [DOI] [PubMed] [Google Scholar]
  30. Derry AM, Prepas EE, Hebert PDN. A comparison of zooplankton communities in saline lakewater with variable anion composition. Hydrobiologia. 2003;505:199–215. [Google Scholar]
  31. Hart CM, González MR, Simpson EP, Hurlbert SH. Salinity and fish effects on Salton Sea microecosystems: zooplankton and nekton. Hydrobiologia. 1998;381:129–152. [Google Scholar]
  32. Tiffany MA, Swan BK, Watts JM, Hurlbert SH. Metazooplankton dynamics in the Salton Sea, California, 1997–1999. Hydrobiologia. 2002;473:103–120. [Google Scholar]
  33. De Ridder M. Annotated checklist of non-marine Rotifera from African inland waters. Zool Doc KMMA, Tervuren. 1986;21:1–123. [Google Scholar]
  34. De Ridder M. Distribution of rotifers in African fresh and inland saline waters. Hydrobiologia. 1987;147:9–14. [Google Scholar]
  35. De Ridder M. Additions to "Annotated checklist of non-marine Rotifera from African inland waters". Rev Hydrobiol Trop. 1991;24:25–46. [Google Scholar]
  36. De Ridder M. Additions II to "Annotated checklist of non-marine Rotifera from African inland waters". Biol Jb Dodonaea. 1994;61:99–153. [Google Scholar]
  37. Yamamoto K. Plankton Rotatoria in Japanese inland waters. Hydrobiologia. 1960;16:364–411. [Google Scholar]
  38. Brock MA, Shiel RJ. The composition of aquatic communities in saline wetlands in Western Australia. Hydrobiologia. 1983;105:77–84. [Google Scholar]
  39. Bayly IAE. The fauna of athalassic saline waters in Australia and the Altiplano of South America: comparisons and historical perspectives. Hydrobiologia. 1993;267:225–231. [Google Scholar]
  40. Campbell CE. Seasonal zooplankton fauna of salt evaporation basins in South Australia. Aust J Mar Freshw Res. 1994;45:199–208. [Google Scholar]
  41. Shiel RJ, Costelloe JF, Reid JRW, Hudson P, Powling J. ooplankton diversity and assemblages in arid zone rivers of the Lake Eyre Basin, Australia. Mar Freshwat Res. 2006;57:Z49–60. [Google Scholar]
  42. Segers H, Dumont HJ. Rotifera from Arabia, with descriptions of two new species. Fauna of Saudi Arabia. 1993;13:3–26. [Google Scholar]
  43. Elías-Gutiérrez M, Suárez-Morales E, Sarma SSS. Diversity of freshwater zooplankton in the neotropics: the case of Mexico. Verh Internat Verein Limnol. 2001;27:4027–4031. [Google Scholar]
  44. Sarma SSS, Elías-Gutiérrez M. Taxonomic studies of freshwater rotifers (Rotifera) from Mexico. Polskie Archiwum Hydrobiologii. 1997;44:341–357. [Google Scholar]
  45. Segers H. Annotated checklist of the rotifers (Phylum Rotifera), with notes on nomenclature, taxonomy and distribution. Zootaxa. 2007;1564:1–104. [Google Scholar]
  46. Schallenberg M, Hall CJ, Burns CW. Consequences of climate-induced salinity increases on zooplankton abundance and diversity in coastal lakes. Mar Ecol Prog Ser. 2003;251:181–189. [Google Scholar]
  47. Shepard WD. Desert springs – both rare and endangered. Aquatic Conservation: Marine and Freshwater Ecosystems. 1993;3:351–359. [Google Scholar]
  48. Wallace RL, Walsh EJ, Arroyo ML, Starkweather PL. Life on the edge: rotifers from springs and ephemeral waters in the Chihuahuan Desert, Big Bend National Park (Texas, USA) Hydrobiologia. 2005;546:147–157. [Google Scholar]
  49. Walsh EJ, Schröder T, Arroyo ML, Wallace RL. How well do single samples reflect rotifer species diversity? A test based on interannual variation of rotifer communities in Big Bend National Park (Texas, USA) Hydrobiologia. 2007;593:39–47. [Google Scholar]
  50. Walsh EJ, Schröder T, Wallace RL. Cryptic speciation in Lecane bulla (Monogononta: Rotifera) in the Chihuahuan Desert zooplankton? Verh Internat Verein Limnol. in press .
  51. Dumont HJ, Segers H. Estimating lacustrine zooplankton species richness and complementarity. Hydrobiologia. 1996;341:125–132. [Google Scholar]
  52. Kunin WE. Towards an asymmetric index of community similarity. Oikos. 1995;73:442–446. [Google Scholar]
  53. Simpson EH. Notes on the measurement of faunal resemblance. Am J Sci. 1960;258-A:300–311. [Google Scholar]
  54. Edmondson WT. A formula key to the rotatorian genus Ptygura. Trans Amer Microsc Soc. 1949;68:127–135. [Google Scholar]
  55. Berzins B. On the Collothecacean Rotatoria, with special reference to the species found in the Aneboda district, Sweden. Arkiv Zoologi. 1951;1(37):565–592. [Google Scholar]
  56. Edmondson WT. In: Fresh-water Biology. 2. Edmondson WT, editor. New York : John Wiley and Sons, Inc; 1959. Rotifera; pp. 420–494. [Google Scholar]
  57. Koste W. Rotatoria. Die Rädertiere Mitteleuropas. Vol. 2. Berlin: Gebrüder Borntraeger; 1978. [Google Scholar]
  58. Stemberger RS. A Guide to Rotifers of the Laurentian Great Lakes. Cincinnati: U.S. Environmental Protection Agency (PB80-101280); 1979. [Google Scholar]
  59. Nogrady T, Pourriot R, Segers H. In: Guides to the Identification of the Microinvertebrates of the Continental Waters of the World. Dumont HJ, editor. Vol. 6. The Hague: SPB Acad Publishing; 1995. Rotifera. Vol.3: The Notommatidae and: The Scaridiidae; pp. 1–226. [Google Scholar]
  60. Segers H. In: Guides to the Identification of the Microinvertebrates of the Continental Waters of the World. Dumont HJ, editor. Vol. 2. The Hague: SPB Acad. Publishing; 1995. Rotifera. The Lecanidae (Monogononta) pp. 1–226. [Google Scholar]
  61. De Smet WH. In: Guides to the Identification of the Microinvertebrates of the Continental Waters of the World. Dumont HJ, editor. Vol. 9. The Hague: SPB Acad Publishing; 1996. Rotifera. Vol. 4: The Proalidae (Monogononta) pp. 1–102. [Google Scholar]
  62. De Smet WH, Pourriot. R. In: Guides to the Identification of the Microinvertebrates of the Continental Waters of the World. Dumont HJ, editor. Vol. 12. The Hague: SPB Academic Publishing; 1997. Rotifera. Vol. 5: The Dicranophoridae (Monogononta) and: The Ituridae (Monogononta) pp. 1–344. [Google Scholar]
  63. Wallace RL, Snell TW. In: Ecology and Classification of North American Freshwater Invertebrates. 2. Thorp J, Covich A, editor. New York: Academic Press; 2001. Rotifera; pp. 195–254. [Google Scholar]
  64. Jose de Paggi S. In: Guides to the Identification of the Microinvertebrates of the Continental Waters of the World. Nogrady T, Segers H, editor. Vol. 18. Leiden: Backhuys Publishers; 2002. Rotifera. Volume 6: Asplanchnidae; pp. 1–27. [Google Scholar]
  65. Donner J. Ordnung Bdelloidea. Bestimmungsbücher zur Bodenfauna Europas. Berlin: Akademie-Verlag; 1965. [Google Scholar]
  66. Ricci C, Melone G. Key to the identification of the genera of bdelloid rotifers. Hydrobiologia. 2000;418:73–80. [Google Scholar]
  67. ter Braak CJF, Smilauer P. CANOCO Reference manual and CanoDraw for Windows User's guide: Software for Canonical Community Ordination (version 4.5) Ithaca: Microcomputer Power; 2002. [Google Scholar]

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