Research Article
Print
Research Article
Stygobromus bakeri, a new species of groundwater amphipod (Amphipoda, Crangonyctidae) associated with the Trinity and Edwards aquifers of central Texas, USA
expand article infoRandy Gibson, Benjamin T. Hutchins§, Jean K. Krejca|, Peter H. Diaz, Peter S. Sprouse|
‡ United States Fish and Wildlife Service, San Marcos, United States of America
§ Texas State University, San Marcos, United States of America
| Zara Environmental LLC, Manchaca, United States of America
Open Access

Abstract

A new stygobitic groundwater amphipod species, Stygobromus bakeri sp. nov., is described from 4 central Texas limestone karst springs; John Knox Spring (Comal County), Jacob’s Well (Hays County), Mormon Spring (Travis County) and Salado Springs (Bell County). This species belongs to the predominately western Nearctic hubbsi species group of Stygobromus and differs from other species in the group by gnathopod 1 with row of 4 to 5 setae posterior to the defining angle, pereopods 6 and 7 with broadly expanded bases and distinct distoposterior lobes, gnathopods 1 and 2 with 2 rows of 3 singly inserted setae on the inner palm, and uropod 3 with single, slightly distal peduncular seta. Habitat, sympatric groundwater species, and conservation issues are discussed.

Keywords

cave, crenobiont, interstitial crustacean, karst, spring, stygobiont, stygobite, subterranean, sympatric, troglomorphy

Introduction

The Nearctic amphipod genus Stygobromus Cope, 1872 (Amphipoda, Crangonyctidae) currently includes 137 described species and 4 subspecies in the United States and Canada (Hay 1882; Hubricht 1943; Derzhavin 1945; Holsinger 1967; Holsinger 1969; Holsinger 1974; Holsinger 1978; Wang and Holsinger 2001; Holsinger 2009; Sidorov et al. 2010; Holsinger et al. 2011; Taylor and Holsinger 2011; Holsinger and Ansell 2014; Holsinger and Sawicki 2016; Cannizzaro et al. 2019; Palatov and Marin 2020). The genus is entirely stygomorphic, and, as with most groundwater-obligate taxa, low detection probability (a function of inaccessible habitat and low population densities), coupled with pervasive convergent evolution (Eberhard et al. 2009; Culver and Pipan 2015; Devitt 2019) results in an incomplete understanding of diversity and systematics within the genus. Many species, cryptic and otherwise, await description. Holsinger (1974) and Wang and Holsinger (2001) provisionally assigned 45 of 54 currently recognized taxa in the western United States and southwestern Canada to the hubbsi group. Although molecular data supporting systematic relationships are lacking for most taxa (but see Ethridge et al. 2013; Aunins et al. 2016; Cannizzaro et al. 2019), the hubbsi group is supported morphologically by lack of sternal gills on the pereonites and a combination of additional characters summarized by Wang and Holsinger (2001). The distribution of Stygobromus in Texas is mapped in Figure 1. In the Edwards Plateau and Balcones Escarpment of central Texas, USA, 9 Stygobromus species are documented alongside diverse assemblages of stygobiontic crustaceans (Holsinger 1967; Gibson et al. 2008; Hutchins 2018; Nissen et al. 2018). Four central Texas Stygobromus species belong to the tenuis group: S. balconis (Hulbricht, 1943), S. reddelli (Holsinger, 1966), S. russelli (Holsinger, 1967), and S. bifurcatus (Holsinger, 1967). Four comprise the central Texas endemic flagellatus group: S. flagellatus (Benedict, 1896), S. longipes (Holsinger, 1966), S. dejectus (Holsinger, 1967), and S. pecki (Holsinger, 1967). Stygobromus hadenoecus (Holsinger, 1966) is the sole described member of the hadenoecus group found in the western Edwards Plateau. The nearest hubbsi group species, S. limbus Wang & Holsinger, 2001, occurs more than 300 km away from the Edwards Plateau taxa in a southeastern extension of the Basin and Range Province of the western United States in far west Texas. Huston and Gibson (2018) reported an undescribed species in the hubbsi group from a single spring site in the Chisos Basin of Big Bend National Park, Texas, also within the Basin and Range Province. Only a single hubbsi group species, S. putealis (Holmes, 1909) from wells in Wisconsin, is currently known from east of North America’s western Cordillera (Wang and Holsinger 2001).

Stygobromus species of the hubbsi group are recorded in a variety of groundwater habitats including caves, wells, the hyporheic zone of surface streams, karstic and non-karstic springs, and hypotelminorheic seeps. Two species live in the depths (5–495 m) of Lake Tahoe (California and Nevada) although Wang and Holsinger (2001) hypothesized that their preferred habitat may actually be adjacent groundwater.

Figure 1. 

Stygobromus distribution in Texas. Red square expanded to view central Texas species. Individual undescribed species represented by S. sp. and S. spp. (flagellatus) refers to several undescribed site endemic species in the flagellatus group (Hutchins 2018).

Many groundwater habitats and groundwater-obligate organisms are at risk from a myriad of threats, including groundwater contamination, physical habitat destruction (e.g. gravel mining), and groundwater extraction (Burri et al. 2019; de Graaf et al. 2019), lending urgency to continued documentation of groundwater biodiversity. Here, we describe the 12th species of Stygobromus from Texas, USA and the first species belonging to the hubbsi group in the Edwards Plateau/Balcones Escarpment region, an area where groundwater extraction to meet the demand of a rapidly growing human population along the Interstate 35 highway corridor increasingly threatens groundwater resources.

Materials and methods

Specimens were collected from karst springs using 150–250 µm mesh drift nets and using multiple techniques at an underwater cave, Jacob’s Well (Fig. 2A) accessed via the resurgence entrance using SCUBA (Fig. 2B, C). Divers performed surveys at Jacob’s Well, Hays County on 20 occasions from May 2009 to June 2011, using visual searches, a drift net placed at a vertical constriction at -25 m depth and 42 m penetration, cloth lures secured to the side of the cave shaft near the entrance, and baited bottle traps placed in a broad, low room at -30 m depth and 70 m penetration. The visual search area within the underwater passage began at the shaft below the spring opening and up to a maximum penetration of 330 m. Hand sampling was performed using basters, fine aquarium dipnets, and centrifuge vials. Külköylüoğlu and Gibson (2018) and Külköylüoğlu et al. (2017) described collection details at John Knox Springs, Comal County. Surveys using 250 µm drift nets at springs in the city of Salado, Bell County (Fig. 3) began in 2015 and have continued seasonally as part of a monitoring project for the endangered Salado salamander, Eurycea chisholmensis Chippindale, Price, Wiens & Hillis, 2000 at 10 spring orifices at Robertson Springs and 2 spring orifices at the Downtown Spring Complex (Diaz and Warren 2019). Mormon Spring #3, in Travis County was sampled using 150 µm drift nets from 20 January to 23 February 2017. All samples were stored in 95% ethanol.

Figure 2. 

Comal, Hays, and Travis counties, Texas spring sites for Stygobromus bakeri sp. nov. Jacob’s Well A cave entrance B second constriction point (30 m water depth), Stygobromus bakeri sp. nov. were found deeper than this point C drift net at first constriction point (23 m water depth). John Knox Ranch D Blue Hole, perennial headwaters of Carper’s Creek E John Knox Spring issuing within Blue Hole. Mormon Spring #3 F Spring exposed under boat dock during drought G drift net on spring site. Photograph credit: Jean Krejca (A–C); courtesy of John Knox Ranch (D); Randy Gibson (E); Peter Sprouse (F, G).

Specimens were dissected, and mouthparts and appendages were mounted in glycerin. Images and measurements were acquired at multiple magnifications and focal points using an Olympus BX-45 compound stereomicroscope and Nikon DS-5M digital camera. Images were imported into Abode Illustrator Creative Suite 5 software and line drawing illustrations were produced using a Wacom Cintiq 22HD Interactive Pen Display. Nomenclature for setal arrangement on the mandibular palps follows Cole (1980) for segment 2 and Stock (1974) for segment 3. The “defining angle” of the gnathopod propodus is the area where the tip of the dactylus rests on the posterior margin of the palm. “Robust setae” and “setae” were used in place of the traditional “spine teeth” and “spines” following Watling (1989) and Cannizzaro et al. (2019).

Figure 3. 

Salado, Bell County, Texas spring sites for Stygobromus bakeri sp. nov. Robertson Spring Complex A Beetle Spring B Middle Spring C Ludwigia Spring D Creek Spring upwelling below water surface. Downtown Spring Complex E Big Boiling Spring F Anderson Spring. Photographs by Pete Diaz.

Results

Systematics

Class Crustacea Brünnich, 1772

Order Amphipoda Latreille, 1816

Suborder Senticaudata Lowery & Myers, 2013

Infraorder Gammarida Latreille, 1802

Parvorder Crangonyctidira Bousfield, 1973

Superfamily Crangonyctoidea Bousfield, 1973

Family Crangonyctidae Bousfield, 1963; emended by Holsinger 1977

Genus Stygobromus Cope, 1872

Stygobromus bakeri Gibson & Hutchins, sp. nov.

Fig. 4

Type locality

USA, Texas, Comal County, John Knox Ranch, John Knox Spring (29.9642, 98.1956).

Material examined

All sites are in Texas, USA. Holotype female (4.6 mm) – Comal County, John Knox Ranch, John Knox Spring: collected by Randy Gibson (RG), 6 May 2010, dissected slide mounts Texas State University Aquifer Biodiversity Collection. Allotype male (3.1 mm) – Comal County, John Knox Ranch, John Knox Spring: collected by RG, 16 April 2010. Paratypes – John Knox Spring: juvenile (1.7 mm) collected by RG, 6 January 2010; 2 males (3.5 and 3.6 mm) and juvenile (2.4 mm) collected by RG, 6 April 2010; 2 males (2.5 and 3.4 mm) collected by RG, 2 May 2010; juvenile (2.4 mm) collected by RG, 6 May 2010; damaged female (4.5 mm) collected by RG, 10 May 2010; 2 males (3.1 mm and 4.1 mm) collected by RG, 13 May 2010; male (3.5 mm) and juvenile (2.3 mm) collected by RG, 21 May 2010. – Hays County, Jacob’s Well (30.0345, -98.1261): male (4.2 mm) collected by Jean Krejca (JK), 21 October 2009; female (4.5 mm) collected by JK, 6 May 2010; female (3.5 mm) collected (≈ 43 m depth) by JK and James Brown, 4 August 2010; brooding female (4.4 mm), male (4.1 mm) and 2 juveniles collected by JK 31 May 2011; 2 males (4.4 and 2.9 mm) collected by JK, 16 June 2013; male (3.2 mm) collected by Matt Turner, 8 September 2013.

Additional material examined

– Travis County, Mormon Spring no. 3 (30.3132, -97.7747): 1 damaged female (4.4 mm) collected by P. Sprouse, 30 January 2017 (Zara # 9450, TMM # 91,955). – Bell County, Middle Robertson Spring (Robertson Springs Complex) (30.9444, -97.5410): female (4.2 mm) collected by Andy Gluesenkamp, 12 Dec 2009; juvenile (1.7 mm) collected by RG and Pete Diaz (PD), 30 July 2015; male (2.7 mm) collected by PD, 26 April 2017. Sam Bass Spring (Robertson Springs Complex) (30.9444, -97.5410): male (4.5 mm) collected (drift net) by PD and RG, 1 Mar 2016. Upper Ludwigia Spring (Robertson Springs Complex) (30.9444, -97.5411): male (3.1 mm), collected (drift net) by PD, 20 January – 6 June 2017. Creek Spring (Robertson Springs Complex) (30.9445, -97.5414): male (3.0 mm) collected by PD, 12 April 2018; 2 males (4.1 and 3.2 mm) collected by PD, 27 November 2018. Big Boiling Spring (Downtown Springs Complex) (30.9437, -97.5366): male (3.2 mm) collected by RG and PD, 25 September 2015. Anderson Spring (Downtown Springs Complex (30.9441, -97.5346): damaged specimen (2.9 mm) collected (drift net) by PD, 1 November 2016–20 January 2017. Whole paratypes are deposited in the National Museum of Natural History, Smithsonian Institution (USNM accession # 1638682–1638690) and Texas State University Aquifer Biodiversity Collection (ABC accession # 0021059–002171).

Diagnosis

Small stygobitic species similar to most members of the hubbsi group with mature females larger than males, gnathopod 2 larger than gnathopod 1, posterior margin of gnathopod 1 typically shorter than palm, and telson as long as broad with shallow notch in apical margin. Distinguished from other hubbsi group species by gnathopods 1 and 2 with 2 rows of 3 singly inserted setae on the inner palm, and combination of following characters: gnathopod 1 with row of 4 to 5 setae posterior to the defining angle (compare to S. quatsinensis Holsinger & Shaw, 1986 with 2 or 3 postmarginal setae, 3 hubbsi group species have 1 or 2 postmarginal setae and all others are lacking); pereopods 6 and 7 with broadly expanded bases and distinct distoposterior lobes (similar to S. salturus Wang & Holsinger, 2001); and uropod 3 with single, slightly distal peduncular seta (similar to S. lanensis Wang & Holsinger, 2001).

Figure 4. 

Stygobromus bakeri sp. nov. collected live from Jacob’s Well. Photograph by Jean Krejca.

Description

Female (4.6 mm). Antenna 1 (Fig. 5, A1): 39% length of body, ca. 1.7× longer than antenna 2; primary flagellum with 10 segments, aesthetacs on segment 3–10; accessory flagellum 2 segmented reaching up to flagellar segment 2. Antenna 2 (Fig. 5, A2): flagellum with 3 segments. Mandibles (Fig. 5, lMdb, rMdb): left mandible incisor 5-dentate, lacinia mobilis 5-dentate, with 5 robust, plumose accessory setae, molar protruding and non-triturative with tuft of setae on anterior margin, blade-like teeth and single long rastellate seta. Right mandible incisor 5-dentate, lacinia mobilis 3-dentate, 1 serrate, 1 forked apically, and last with row of denticles and long setae at base; accessory setae row with 2 robust serrate setae and tufts of long setae basally; molar and palp similar to left mandible. Palp 3-segmented, segment 2 and 3 subequal; segment 2 with 2 alpha and 1 beta setae, fringe of small hair-like setae lining inner margin and fringe of pubescence lining outer distal margin; segment 3 with 1 B seta, 5 E setae, 6 C setae, small hair-like D setae, A setae absent, and fringe of pubescence lining outer distal margin. Lower lip (Fig. 5, Li): covered in fine hairs with inner lobes poorly developed. Maxilla 1(Fig. 5, Mx1) inner plate with 4 plumose setae; outer plate with 7 comb-spines (1 with inner medial margin lined with setae, 2 serrate, and 4 gaffate); palp 2-segmented, with 3–4 setae (2 apical, 1–2 subapical) and ca. 10 small hair like setae. Maxilla 2 (Fig. 5, Mx2) inner plate with 13 setae, 7 longer plumose setae along inner margin and 6 shorter apical setae; outer plate with 9 setae (mostly finely serrate, and 1 with apical minute setule) and an additional shorter seta on outer margin. Maxilliped (Fig. 5, Mp) inner plate with 3 apical spine-teeth, 2 plumose submarginal setae, and 2 longer setae arising at base; outer plate with 8–9 long simple setae and 1 outer apical seta with apical marginal setules; palp 4 segmented, second segment about 2× longer and wider than third, segment 1 with seta on inner margin, segment 2 with 6–8 setae on inner margin, 2 of these finely serrate, apical seta longer than rest, segment 3 with 8–11 setae, a few finely serrate and many forked apically, a densely pubescent patch located on dorsal face from midline to outer margin of segment, segment 4 with 2 setae apically at base of nail, one seta on outer margin medially, nail subequal in length to segment 4.

Figure 5. 

Stygobromus bakeri sp. nov., Holotype ♀ (4.6 mm), John Knox Spring, Comal Co., Texas A1 antenna 1 A2 antenna 2 Li lower lip Mp maxilliped Mx1 maxilla 1 Mx2 maxilla 2. Paratype ♂ (3.1 mm), John Knox Spring, Comal Co., TX. lMdb left mandible and mandibular palp rMdb right mandible. Scale bars: 0.05 mm (Li, Mp, Mx1, Mx2, lMdb, rMdb); 0.1 mm (A1, A2).

Gnathopod 1 (Fig. 6, G1): propodus shorter than that of gnathopod 2; coxal plate longer than broad, with 1 ventral and 2 anterior marginal setae; basis with 5 long setae inserted along posterior margin; ischium with 2 setae and scale patch along posterior margin; merus with 9 posterodistal setae and patch of pubescence; carpus 36% length of propodus, with 9 setae; propodus 1.5× longer than widest point with 3 superior and 3 inferior medial setae, palm slightly convex with 10 inner and 11 outer bifurcate robust setae, 2 of these posterior to defining angle, defining angle rounded and sub angular, margin posterior to defining angle ca. half the length of the palm with 4–5 setae and scaly patch becoming finer at defining angle and granular along inner margin of dactylus depression; dactylus with 1 seta on outer margin and 3 on distal half of inner margin; dactylus nail ca. 21% length of dactylus.

Figure 6. 

Stygobromus bakeri sp. nov., Holotype ♀ (4.6 mm), John Knox Spring, Comal Co., Texas G1, G2 gnathopods (G1 palmer margin enlarged 2×) 1–2 U1U3 uropods 1–3 Pl1 pleopod 1 Tl telson. All body parts drawn to same scale.

Gnathopod 2 (Fig. 6, G2): propodus 1.3× longer than that of gnathopod 1; coxal plate quadrate, with 1 ventral and 2 anterior marginal setae; basis with 1 long seta on anterior margin, shorter seta on posterodistal margin; ischium with 1 seta and scale patch on posterior surface; merus with 2 posterodistal setae, scale patch on posterior surface; carpus 25% length of propodus, with 3 distal setae, 7 setae and scale patch on posterior surface; propodus ca. 2× longer than widest point with 3 superior and 3 inferior medial setae, palm straight to slightly convex with 11 inner and 13 outer bifurcate robust setae, 2 of these posterior to defining angle and 3 sets of paired setae, 2 of these posterior to defining angle, defining angle rounded, margin posterior to defining angle ca. half the length of the palm with scaly patch on poster margin becoming finer at defining angle and granular along inner margin of dactylus depression; dactylus with 1 seta on outer margin; dactylus nail ca. 15% length of dactylus.

Pereopod 3 (Fig. 7, P3): subequal in length to pereopod 4; coxal plate subquadrate with 2 apical setae; merus 1.2× longer than carpus; propodus 1.4× longer than carpus, 2 setae on outer distal margin; dactylus ca. 30% length of propodus, apical sensory seta on outer margin. Pereopod 4 (Fig. 7, P4): coxal plate deep, quadrate with 3 ventral marginal setae, reaching more than 50% length of basis; merus subequal in length to carpus; propodus 1.3× longer than carpus, 2 setae on outer distal margin; dactylus ca. 30% length of propodus, apical sensory seta on outer margin. Pereopod 5 (Fig. 7, P5): coxal plate bi-lobate with single seta on anteroventral margin; basis broad with posterior margin slightly convex; merus 75% length of carpus; propodus subequal to carpus, 4 setae on outer distal margin, 1 of these longer than dactylus; dactylus ca. 30% length of propodus, apical sensory seta on outer margin. Pereopod 6 (Fig. 7, P6): subequal in length to pereopod 7 and 25% longer than pereopod 5; coxal plate bi-lobate with single seta on posteroventral margin; basis broad with posterior margin convex; merus 90% length of carpus; propodus 1.2× longer than carpus, 1 seta on outer distal margin; dactylus ca. 30% length of propodus, apical sensory seta on outer margin. Pereopod 7 (Fig. 7, P7): coxal plate ovate with single seta on ventral margin; basis broad with posterior margin convex with well developed distoposterior lobe; merus 85% length of carpus; propodus 1.2× longer than carpus, 1 long and 2 shorter setae on outer distal margin; dactylus ca. 30% length of propodus, apical sensory seta on outer margin.

Figure 7. 

Stygobromus bakeri sp. nov., Holotype ♀ (4.6 mm), John Knox Spring, Comal Co., Texas. P3P7 pereopods 3–7 Plp pleonal plates (epimera).

Coxal gills on somites 2–7, stalked and subovate, smallest on pereopod 7 (Fig. 7, P3–P7). Brood plates present on somites 2–5 (Fig. 6, G2; Fig. 7, P3–P5) bearing long distal setae (not illustrated). Sternal gills absent but small processes sometimes visible on sternites between pereopods 3–7.

Pleonal plates (Epimera) (Fig. 7, Plp): posterior margins weakly convex with single setule; distoposterior corners weakly rounded; ventral margin weakly convex in plate 1 and 2 and nearly straight in plate 3, with single marginal seta on plate 2 and 2 setae on plate 3. Pleopods biramous, rami subequal, outer rami 7 segmented, inner rami 8 segmented, bearing many plumose setae, typical for genus (Fig. 6, Pl1). Uropod 1 (Fig. 6, U1): peduncle with 9–10 robust setae; inner ramus ca. 70% length of peduncle, slightly longer than outer ramus, armed with 3 inner and 5 apical robust setae; outer ramus with 1 inner and 6 apical robust setae. Uropod 2 (Fig. 6, U2): peduncle with 4 robust setae; inner ramus subequal to peduncle, ca. 30% longer than outer ramus, armed with 5 inner and 4 apical robust setae; outer ramus with 2 inner and 4 apical robust setae. Uropod 3 (Fig. 6, U3): peduncle with single slightly distal seta; 2ramus ca. 51–55% length of peduncle, with 2 apical setae. Telson (Fig. 6, Tl): quadrate (subequal in length and width) with apical v-shaped notch with depth ca. 20% length of telson, 8 to10 apical setae and bearing tufts comprised of 2 sensory setae on each lateral side.

Male (3.1 mm). Closely resembles female but typically smaller, with fewer setae on appendages, and differing in the following characters: Antenna 1 proportionally longer, up to 46% length of body; primary flagellum with 9 segments. Uropod 2 inner and outer rami subequal in length.

Etymology

Epithet bakeri honors David Baker, a citizen scientist, conservationist and visionary who has worked for decades to bring together scientists, politicians, funders, regulators and stakeholders from near and far to conserve the watershed of Jacob’s Well. David lived immediately over the underwater cave for some time, working hard to make his own property environmentally friendly and to educate those who visited. He formed the Wimberley Valley Watershed Association, a non-profit with the mission to protect Jacob’s Well and Cypress Creek.

Distribution and ecology

To date, this small species has been collected in 2 karst springs in southwestern Hays and northwestern Comal counties, Texas, a single karst spring 50 km northeast, on the shoreline of the Colorado River (usually emerging beneath a boat dock in Lake Austin) in Austin, Travis County, Texas and 2 karst spring complexes 74 km further northeast in Salado, Bell County, Texas (Fig. 1). All 4 sites are hydrogeologically distinct.

Jacob’s Well (Fig. 2A–C) is a natural spring and cave located in the bed of Cypress Creek with enterable passage typically 1–2 m in diameter, and mapped using cave SCUBA to about 42 m deep and 1.6 km in length. Water issues out of the cave from Glen Rose Limestone (Middle Trinity Aquifer) and flows down Cypress Creek: a tributary of the Blanco River (Gary et al. 2019). Stygobromus bakeri sp. nov. was only sampled successfully by hand, with divers using basters, dipnets, and centrifuge vials. Typically, the species was seen in the water column or on the floor, which consisted of silt, breakdown and cobble. Drift nets, bottle traps and cotton lures were not effective at capturing this species at Jacob’s Well. It was seen only in a deeper portion of the cave between 70 m and 215 m penetration. At 70 m penetration, the cave passage descends from -30 m to -42 m through a vertical slot called “The Knife Edge”, beyond which, S. bakeri sp. nov. was collected. But beyond 215 m, the passage ascends back to 30 m and the species was not observed in that section. The habitat was not obviously different in the areas where the species was observed, with the exception of the entrance area (within 70 m of the surface) that has both surface influence and passage constrictions with greater flow, leading to smooth, scoured rocks and less silt.

John Knox Spring (Fig. 2D, E) emerges from Lower Glenn Rose Limestone (Middle Trinity Aquifer) through a 0.3 m vertical crevice-like orifice 1 meter below the water surface and along the bank of a limestone grotto pool forming the headwaters of Carper’s Creek which discharges into the Blanco River. Interstitial surface insect fauna collected from this spring along with Stygobromus russelli (the most widespread Stygobromus species in central Texas) suggests that some portion of the flow might arise from hyporheic or vadose origin. Details of this habitat are described in Külköylüoğlu and Gibson (2018).

Robertson Springs (Fig. 3A–D) and Downtown Spring Complex (Fig. 3E, F) are 0.4 km apart, located on opposite sides of Interstate Highway 35 in the city of Salado. Both spring complexes comprise several spring orifices issuing from Edwards and Comanche Peak limestones forming spring runs that empty into Salado Creek. A diverse interstitial groundwater fauna (Table 1) including relatively widespread species has been recorded from these springs. Stygobromus bakeri sp. nov. was initially sampled by drift netting at Middle Robertson Springs (Norris et al. 2012). Robertson Springs has numerous spring openings (over 30 sites mapped during high flows) with variable discharge and substrate issuing from both banks and from under the 300 m long spring run. Stygobromus bakeri sp. nov. was collected at 4 spring sites throughout the run at different spring zones within the Robertson Springs complex (Diaz et al. 2016; Diaz and Warren 2019). The upper springs cease flowing seasonally and often produce troglofauna (terrestrial cave fauna) when flows resume after adequate rain events, while the lower springs are perennial and occasionally produce troglofauna. The Downtown Spring Complex is more discrete than Robertson Springs, with each of the 7 spring sites issuing from a single origin. Most of the springflow issues from Big Boiling Spring and flows down a short 5 meter spring run that empties into Salado Creek. Anderson Spring is 350 m downstream of Big Boiling Spring, has much less flow, issues from a fissure underneath a spring run (250 m downstream of the headwater Critchfield Spring), and flows 21 m before joining Salado Creek (Norris et al. 2012). Hydrological studies of this area in the Northern Segment of the Edwards Aquifer showed the Downtown Spring Complex to be part of an integrated fracture system with groundwater flow velocities recorded at 1.8 m/sec and confirmed mixing of groundwater and Salado Creek surface water at Big Boiling Spring (Wong and Yelderman 2017).

Table 1.

Groundwater fauna collected at each Stygobromus bakeri sp. nov. site. Stygobionts (S) are hypogean and colonize various groundwater habitats. Crenobionts (C) are epigean and preferentially colonize springs.

Taxon Stygobiont/c renobiont John Knox Spring Jacob‘s Well Salado Springs Mormon Spring #3
Turbellarians
Order Tricladida
Family Kenkiidae
Sphalloplana mohri Hyman, 1938 S X
Annelids
Order Lumbriculata
Family Lumbriculidae
Eremidrilus sp. 1 Fend & Rodriguez, 2003 S X X
Eremidrilus sp. 2 S X
Molluscans
Order Gastropoda
Family Cochliopidae
Phreatoceras taylori (Hershler & Longley, 1986) S X
Phreatodrobia conica Hershler & Longley, 1986 S X
Phreatodrobia micra (Pilsbry & Ferriss, 1906) S X
Phreatodrobia nugax (Pilsbry & Ferriss, 1906) S X X
Stygopyrgus bartonensis Hershler & Longley, 1986 S X
Family Hydrobiidae
Marstonia comalensis (Pilsbry & Ferriss, 1906) C X X X
Family Plueroceridae
Elimia comalensis (Pilsbry, 1890) C X X
Crustaceans
Order Amphipoda
Family Parabogidiellidae
Parabogidiella americana Holsinger, 1980 S X
Family Crangonyctidae
Stygobromus bifurcatus (Holsinger, 1967) S X X X
Stygobromus russelli (Holsinger, 1967) S X X X X
Stygobromus (flagellatus group) sp. nov. Cope, 1872 S X
Order Bathynellacea
Family Parabathynellidae
Texanobathynella bowmani Delamare Deboutteville, Coineau & Serban, 1975 S X
Order Isopoda
Family Asellidae
Caecidotea bilineata Lewis & Bowman, 1996 S X
Caecidotea reddelli (Steeves, 1968) S X X
Lirceolus bisetus (Steeves, 1968) X
Lirceolus hardeni (Lewis & Bowman, 1996) S X X X
Lirceolus pilus (Steeves, 1968) S X X
Order Podocopida
Family Candonidae
Comalcandona tressleri Külköylüoğlu & Gibson, 2018 S X
Schornikovdona bellensis Külköylüoğlu, Yavuzatmaca, Akdemir, Diaz & Gibson, 2017 S X
Pseudocandona albicans (Brady, 1864) C X
Pseudocandona cf semicognita (Schäfer, 1934) C X
Physocypria cf globula Furtos, 1933 C X
Darwinula stevensoni (Brady & Robertson, 1870) C X
Cypridopsis sp. (Brady, 1867) C X
Physocypria denticulata (Daday, 1905) C X
Chlamydotheca texasiensis (Baird, 1862) C X
Cypridopsis cf helvetica Kaufmann, 1900 C X
Arachnids
Order Trobidiformes
Family Arrenuridae
Arrenurus spp. Dugès, 1834 S X X
Insects
Order Coleoptera
Family Dytiscidae
Sanilippodytes sp. Franciscolo, 1979 C X X
Uvarus texanus (Sharp, 1882) C X
Family Elmidae
Microcyloepus pusillus (LeConte, 1852) C X X X
Salamanders
Order Urodela
Family Plethodontidae
Eurycea chisholmensis Chippindale, Price, Wiens & Hillis, 2000 C X
Eurycea pterophila Burger, Smith & Potter, 1950 C X X

Mormon Spring # 3 (Fig. 2F, G), which normally lies beneath Lake Austin on the Colorado River, issues from Fredericksburg Group consolidation (limestone, dolomite, chert, and marl). Lake Austin was constructed in 1940, replacing the damaged Austin Dam, which may have also inundated the spring. From time to time, the Lower Colorado River Authority lowers the level of Lake Austin to allow for dock maintenance. During the last such lowering of 3 m in January 2017, multiple spring complexes were visible over a stretch of about 100 m along the east shore of the lake. North to south, Mormon Springs numbers 1 and 2 emerged from sediment, without visible bedrock apertures. Mormon Spring # 3 consists of multiple bedrock outlets in a cutbank excavated in bedrock below a boat dock. The spring appears associated with the Trinity Aquifer but is located near the Edwards Aquifer boundary and could potentially be a gravity spring from local recharge intersected by the Colorado River. Alternatively, this spring could represent flow from the north, from the Balcones Escarpment. No dye tracing has been conducted at this spring to characterize its springshed.

Stygobromus bakeri sp. nov. co-occurs with S. russelli (all sites), S. bifurcatus (Jacob’s Well, Salado Springs, and Mormon Springs), and a large undescribed species of Stygobromus in the flagellatus group (Jacob’s Well). The presence of 4 Stygobromus species at Jacob’s Well is notable, and presumably all 4 species occupy different ecological niches. Due to its unusually small size and robust body, S. bakeri sp. nov. is able to inhabit both deep cave and shallow spring habitats. It may also occupy interstitial habitats such as the hyporheic zone of surface streams, although it was not collected in hyporheic samples from Carper’s Creek, near John Knox Spring. The small adult size and general stout teardrop body shape is reminiscent of Seborgia relicta Holsinger, 1980 and S. hershleri Holsinger, 1992 found in groundwater habitats (deep aquifer caves and wells, springs, and hyporheos) throughout the Edwards Plateau and Balcones Escarpment. Seborgia has not been found associated with the Glen Rose formation of the Trinity Aquifer nor with the northernmost section of the Edwards Aquifer extending north of the Colorado River in Austin to Salado where Stygobromus bakeri sp. nov. occurs (Fig. 1). The furthest northern record for Seborgia relicta is from Cold Spring issuing from the Edwards Aquifer on the southern bank of the Colorado River (Ladybird Johnson Lake) only 4 km downstream of Mormon Spring #3. Groundwater fauna records for Stygobromus bakeri sp. nov. sites (Table 1) include interstitial and relatively widespread, ecological generalist stygobionts and crenobionts, yet widespread cavernicolous stygobionts such as Cirolanides spp. isopods are absent at these sites (Holsinger 1967; Lewis 2000; Krejca 2009; Gibson et al. 2018; Hutchins 2018; Devitt et al. 2019; Schwartz et al. 2019; Alvear et al. 2020). Many of the springs have been thoroughly sampled and regularly monitored for multiple years, so the stygofauna is better characterized relative to many other Texas groundwater sites.

Key to Texas species of Stygobromus adapted from Holsinger (1967)

Species lengths reported from original descriptions for relative comparisons and likely vary.

1a Gnathopod 2 longer than gnathopod 1 2, hubbsi group
1b Gnathopod 1 longer or subequal to gnathopod 2 3
2a Pereopod 6 and 7 basis broadly expanded posteriorly with dorsoposterior lobe, adults < 6 mm long, central Texas S. bakeri sp. nov. Gibson & Hutchins
2b Pereopod 6 and 7 basis narrow, distoposterior lobe poorly developed, adults ≤ 13 mm long, rare, Culberson County, west Texas S. limbus Wang & Holsinger, 2001
3a Gnathopod 1 often stouter but subequal in length to gnathopod 2, pereopod 6 and 7 subequal in length 4
3b Gnathopod 1 stouter and usually longer that gnathopod 2, pereopod 7 longer than pereopod 6 8, tenuis group
4a Pereopod 4 coxal plate extending distally > ½ length of basis, pereopod 5–7 basis broadly expanded posteriorly, well defined distoposterior lobe, midwest Texas S. hadenoecus (Holsinger, 1966)
4b Pereopod 4 coxal plate extending distally < ½ length of basis, pereopod 5–7 basis posterior margin not entirely expanded, usually narrow or narrows distally with poorly defined distoposterior lobes, central Texas 5, flagellatus group
5a Uropod 3 with ≤ 3 apical setae, gnathopod 1 palmer margin straight or convex, telson with or without lateral setae, medium to large size (11–15 mm long) 6
5b Uropod 3 typically with ≥ 4 apical setae, gnathopod 1 palmer margin convex, telson without lateral setae, medium size (8–11 mm long) 7
6a Pereopod 5 basis subtriangular (expanded proximally), gnathopod 1 palmer margin convex with 2 rows each with many (ca. 20) robust bifurcated setae, pereopod 7 dactylus 1/4 length of propodus, telson often with multiple lateral setae (3 pair typical in females), large ≤ 15 mm long S. flagellatus (Benedict, 1896)
6b Pereopod 5 basis narrow (parallel sided), gnathopod 1palmer margin straight, with 2 rows each with fewer (ca. 10) relatively stouter robust bifurcated setae, pereopod 7 dactylus 1/3 length of propodus, telson sometimes with single pair of lateral setae, medium ≤ 11 mm long S. longipes (Holsinger, 1966)
7a Pereopods 5–7 dactylus 1/3 length of propodus; uropod 3 with 3 or 4 apical setae, ≤ 8 mm long, rare, Kendall and northern Bexar counties S. dejectus (Holsinger, 1967)
7b Pereopods 5–7 dactylus 1/4 length of propodus; uropod 3 with 5 apical setae, ≤ 11 mm long, rare, Comal County S. pecki (Holsinger, 1967)
8a Gnathopod palmer margins deeply concave (pronounced in larger specimens) 9
8b Gnathopod palmer margins straight to convex 10
9a Lateral sternal gills simple, rare, central Texas, ≤ 16 mm long S. balconis (Hubricht, 1943)
9b Lateral sternal gills bifurcated, widespread in northern Texas, ≤ 10 mm long S. alabamensis (Stout, 1911)
10a Gnathopod 1 palmer margin convex, large (recorded >14 mm long) widespread in central Texas S. bifurcatus (Holsinger, 1967)
10b Gnathopod 1 palmer margin straight, medium to large 11
11a Pereopod 5–7 slender (pereopod 7 carpus width ca. 15% that of length), pereopod 7 ca. 25% longer than pereopod 5, pereopod 7 basis posterior margin mostly straight (parallel sided), uropod 3 with 3 apical setae, telson with ca. 14 apical setae, large (≤14 mm long) rare, San Saba County S. reddelli (Holsinger, 1966)
11b Pereopod 5–7 less slender (pereopod 7 carpus width ca. 25% that of length), pereopod 7 ≥ 30% longer than pereopod 5, pereopod 5–7 basis posterior margin mostly convex, telson with ca. 11 apical setae, medium sized (≤12 mm long) widespread in central Texas S. russelli (Holsinger, 1967)

Discussion

The description of S. bakeri sp. nov. represents a southeast extension of the known range of the hubbsi group into the eastern Edwards Plateau and Balcones Escarpment of central Texas. Stygobromus putealis, described from eastern Wisconsin is the only other representative of the hubbsi group that occurs east of the western Cordillera of North America (Wang and Holsinger 2001). The presence of this species at Robertson Springs, over 70 km away from the other nearest known site for the species is somewhat unusual not only because of the distance, but because the sites are discharge points for 2 distinct karst aquifers, the Trinity and Edwards. However, at least 3 other Stygobromus species (S. bifurcatus, S. longipes, S. russelli) also occur in both the Trinity and Edwards aquifers, and limited, localized hydrologic connections between these aquifers have been documented (Tian et al. 2020), opening the possibility of inter-aquifer dispersal. Additionally, numerous members of the hubbsi group have been recorded from the hyporheic zone of surface streams (Wang and Holsinger 2001) which could provide another potential avenue for dispersal by S. bakeri sp. nov. While the current range of S. bakeri sp. nov. is within the range reported for other Stygobromus species (Hutchins 2018) and certainly within the 200 km range reported for macro-stygobionts by Trontelj et al. (2009), genetic analysis would still be prudent to evaluate whether southern and northern populations represent cryptic lineages.

At all sites where S. bakeri sp. nov. was detected, it occurs in apparently low abundance, particularly compared to co-occurring Stygobromus (e.g. at John Knox Spring, S. bakeri sp. nov. composed 10% of all Stygobromus (27 versus 236 S. russelli) collected from 6 January to 21 May 2010. In comparison, at Robertson Springs, the highest yearly abundance of S. bakeri sp. nov. was 5% of all Stygobromus (26 versus 532 S. russelli and S. bifurcatus combined) collected from 12 April to 7 November 2018. However, it is uncertain whether perceived rarity reflects actual rarity or a lack of effective sampling (Niemiller et al. 2018). Indeed, we lack much basic ecological information about the species including niche breadth and microhabitat preference. A better understanding of the species’ rarity and distribution is a high priority given growing threats to water quantity and water quality in the region.

Both Jacob’s Well and John Knox Springs are fed by the Trinity Aquifer, although the recharge area for John Knox Spring has not been delineated. Recharge for Jacob’s Well primarily occurs in an 80 km2 area within the Dry Cypress Creek watershed northwest of the spring (Gary et al. 2019). Increased pumping in the region has resulted in reduced spring flow at Jacob’s Well, which now flows intermittently (Hunt et al. 2013), and projected rapid human population growth in the region will put additional pressures on groundwater resources. Hays County is the 3rd fastest growing county, by percent, in Texas (Texas Demographic Center 2019). Desired future conditions set by Groundwater Management Area 9 allow for an increase in average drawdown of the Trinity Aquifer in the region up to approximately 9 m by 2060, which if realized, would result in reduced spring flow or spring failure for many Trinity-fed springs. A Recharge Study Zone created in January 2020 and a proposed Jacob’s Well Groundwater Management Zone afford some pumping curtailments and restrictions on new well construction in the region. Neither of these zones, however, provides conservation benefits for the John Knox Spring springshed, which probably occurs farther west in adjacent Comal County, Texas. Texas Parks and Wildlife Department recorded discharge measurements of 28–57 L/s at Carper’s Creek in 2005, 2007, and 2010 (Chad Norris, pers. comm.) and the springshed proportional to this discharge is assumed to be approximately 13–18 km2 (Marcus Gary, Edwards Aquifer Authority, pers. comm.).

The listing of several aquifer-obligate species in the adjacent Edwards Aquifer in the 1960s, 1970s, and 1980s spurred formation of the Edwards Aquifer Authority (EAA) in 1993. Charged with protecting minimum spring flows at Comal and San Marcos springs, the EAA implemented programs that helped protect groundwater recharge and reduce groundwater use (including enforcement of pumping limitations). The regulatory actions of the EAA and conservation measures established in the Edwards Aquifer Habitat Conservation Plan (HCP) have been successful in maintaining spring flow despite a rapidly growing population. Indeed, existing models predict that HCP conservation measures are sufficient to maintain springflows during drought-of-record conditions that would otherwise result in spring failure (Votteler and Gulley 2014). However, EAA jurisdiction does not cover sites at which S. bakeri sp. nov. occurs. Although similar regulatory frameworks do not exist for the Jacob’s Well and John Knox Springs area, the proposed management practices outlined by the Jacob’s Well Groundwater Management Zone were designed explicitly to maintain springflow during periods of drought (Gary et al. 2019).

Recharge of the northern section of the Edwards Aquifer and groundwater conservation in Salado is not regulated by the EAA. In this section of the aquifer, Clearwater Underground Water Conservation District is responsible for management of groundwater in Bell County. Recharge for the springs where S. bakeri sp. nov. and the federally threatened salamander, Eurycea chisholmensis occur are thought to be in the west and southwest portion of Bell County with flow moving generally southeast (Wong and Yelderman 2017). In addition, Brune hypothesized that the recharge to Salado Creek began from fissures along the Williamson and Bell county line (Brune 1981). Bell County is the most northern extension of the Edwards Aquifer in Texas (Wong and Yelderman 2017) and the most northern location known for many Edwards Aquifer associated taxa (Alvear et al. 2020). Edwards limestones thin in Bell County relative to areas to the south, and the southeastern extent of the county was described as being devoid of substantial caves (McKenzie and Reddell 1964).

Mormon Springs is located upstream, but near habitat for the federally endangered Barton Springs and Austin blind salamanders (Eurcyea sosorum Chippindale, Price & Hillis, 1993 and E. waterlooensis Hillis, Chamberlain, Wilcox & Chippindale, 2001), and is in the same aquifer formation as the federally endangered Jollyville Plateau salamander, E. tonkawae Chippindale, Price, Wiens & Hillis, 2000. Little is known about groundwater flow on the northeast side of the Colorado River on the Balcones Escarpment. Mormon Springs is not within a groundwater conservation district, and well pumping, mainly for domestic landscaping use, is unregulated.

Conclusion

The discovery of an undescribed Stygobromus amphipod from the Trinity and Edwards aquifers associated karst springs in Hays, Comal, Travis, and Bell counties in central Texas is unsurprising giving the high species richness and small-range endemism previously reported for the genus and previous documentation of numerous undescribed taxa (Holsinger et al. 2011). However, the assignment of S. bakeri sp. nov. to the predominantly western hubbsi group suggests that the hubbsi group may be more widespread than currently recognized and that additional investigation for small-bodied taxa west of the continental divide will yield additional undescribed species. Stygobromus bakeri sp. nov. is the 12th Stygobromus species described from Texas and can be distinguished from other Texas congeners by gnathopod 2 larger than gnathopod 1 and pereopods 6 and 7 with broadly expanded bases and distinct distoposterior lobes. Stygobrumus bakeri sp. nov. is distinguished from all other hubbsi group species by gnathopod 1 and 2 with 2 rows of 3 singly inserted setae on the inner palm, gnathopod 1 with row of 4–5 setae posterior to the defining angle, and uropod 3 with single, slightly distal peduncular seta. Molecular analysis is recommended to assess the relatedness of southern Trinity Aquifer populations versus northern Edwards Aquifer populations. Finally, the description of small-range endemic species in the region underscores the immediate need for a comprehensive groundwater management framework that ensures adequate groundwater habitat in the face of drought exacerbated by a changing climate and growing human populations.

Acknowledgements

Thanks to the land managers at Jacob’s Well for access to SCUBA and collection in the cave. James Brown and Gregg Tatum are cave divers that helped with cave diving logistics and collection of specimens and assisted author JKK with very technical SCUBA sampling, Krista McDermid helped process specimens. Special thanks to David Baker for logistical support and his decades-long dedication to the conservation of Jacob’s Well. We thank John Knox Ranch for the continual access to their property and their dedication to environmental education and preservation of one of the most pristine streams in the Texas Hill Country, The Robertson family and the Bell County Adaptive Management Coalition for support of conservation research and access to springs, wells, and caves in the area. We greatly appreciate the taxonomic expertise provided by Will Coleman, Steve Fend, Robert Hershler, Okan Külköylüoğlu, Kathryn Perez, and Ian Smith, and specialized knowledge from hydrologist Marcus Gary and field biologists, Andy Gluesenkamp, Jessica Gordon, Chad Norris, James Reddell, Jennifer Bronson Warren, and staff at the San Marcos Aquatic Resources Center.

The views presented herein are those of the authors and do not necessarily represent those of the U.S. Fish and Wildlife Service.

References

  • Alvear DA, Diaz P, Gibson R, Hutchins BT, Schwartz B, Perez KE (2020) Expanding the known ranges of the phreatic snails (Mollusca, Gastropoda, Cochlicopidae) of Texas, USA. Freshwater Mollusk Biology and Conservation 23: 1–17. https://doi.org/10.31931/fmbc.v22i2.2020.1-17
  • Aunins AW, Nelms DL, Hobson CS, King TL (2016) Comparative mitogenomic analyses of three North American stygobiont amphipods of the genus Stygobromus (Crustacea: Amphipoda). Mitochondrial DNA Part B 1: 560–563. https://doi.org/10.1080/23802359.2016.1174086
  • Benedict JE (1896) Preliminary descriptions of a new genus and three new species of crustaceans from an artesian well at San Marcos, Texas. Proceedings of the United States National Museum 18: 615–617. https://doi.org/10.5479/si.00963801.18-1087.615
  • Brady GS (1867) A synopsis of the recent British Ostracoda. Intellect Observer 12: 110–130.
  • Cannizzaro A, Balding GD, Stine M, Sawicki TR (2019) A new syntopic species of Stygobromus Cope, 1872 (Amphipoda: Crangonyctidae) from groundwaters in Georgia and Florida, USA, with notes on S. floridanus Holsinger and Sawicki, 2016. Journal of Crustacean Biology 39: 407–418. https://doi.org/10.1093/jcbiol/ruz034
  • Chippindale PT, Price AH, Wiens JJ, Hillis DM (2000) Phylogenetic relationships and systematic revision of central Texas hemidactyliine plethodontid salamanders. Herpetological Monographs 14: 1–80. https://doi.org/10.2307/1467045
  • Delamare Deboutteville C, Coineau N, Serban E (1975) Decouverte de la famille des Parabathynellidae (Bathynellacea) en Amerique du Nord: Texanobathynella bowmani n.g. n.sp. -Comptes Rendus Hebdomadaires de I’ Academie des Sciences, Paris, Serie D 280: 2223–2226.
  • Devitt TJ, Wright AM, Cannatella DC, Hillis DM (2019) Species delimitation in endangered groundwater salamanders: Implication for aquifer management and biodiversity conservation. Proceedings of the National Academy of Sciences of the United States of America 116: 2624–2633. https://doi.org/10.1073/pnas.1815014116
  • Derzhavin AN (1945) The subterranean amphipoda of Transcaucasus. Bulletin of the Academy of Sciences of Azerbaijan SSR 8: 27–43.
  • Diaz PH, Montagne M, Gibson R (2016) Salado salamander monitoring final report 2016. Texas Fish and Wildlife Conservation Office, United States Fish and Wildlife Service and Texas Fish and Wildlife Department report submitted to the Bell County Adaptive Management Coalition.
  • Diaz PH, Warren JB (2019) Salado salamander monitoring final report 2019. Texas Fish and Wildlife Conservation Office, United States Fish and Wildlife Service and Texas Fish and Wildlife Department report submitted to the Bell County Adaptive Management Coalition.
  • Dugès A (1834) Recherches sur l’ordre des Acariens en général et la famille de Trombidiés en particulier. Premier Mémoire. Annales des Sciences Naturelles, Zoologie et Biologie Animale 2: 5–46.
  • Eberhard SM, Halse SA, Williams MR, Scanlon MD, Cocking J, Barron JJ (2009) Exploring the relationship between sampling efficiency and short-range endemism for groundwater fauna in the Pilbara region, Western Australia. Freshwater Biology 54: 885–901. https://doi.org/10.1111/j.1365-2427.2007.01863.x
  • Ethridge JZ, Gibson JR, Nice CC (2013) Cryptic diversity within and amongst spring-associated Stygobromus amphipods (Amphipoda: Crangonyctidae). Zoological Journal of the Linnean Society 167: 227–242. https://doi.org/10.1111/j.1096-3642.2012.00877.x
  • Furtos N (1933) The Ostracoda of Ohio. Bulletin of the Ohio Biological Survey 29: 411–524.
  • Gary MO, Hunt BB, Smith BA, Watson JA, Wierman D (2019) Evaluation for the development of the Jacob’s Well Groundwater Management Zone in Hays County, Texas. Technical Report prepared for the Hays Trinity Groundwater Conservation District, Hays County, Texas. Meadows Center for Water and the Environment, Texas State University at San Marcos, TX. Report: 2019-05. July 2019, 58 pp. http://haysgroundwater.com/files/Documents/JW-Mgmt-Zone-Report_7.30.19.pdf
  • Holsinger JR (1967) Systematics, speciation, and distribution of the subterranean amphipod genus Stygonectes (Gammaridae). Bulletin of the United States National Museum 259, 176 pp. http://scholar.google.com/scholar_url?url=https%3A%2F%2Frepository.si.edu%2Fbitstream%2Fhandle%2F10088%2F10121%2FUSNMB_2591967_unit.pdf&hl=en&sa=T&oi=gga&ct=gga&cd=0&d=3367762336529767080&ei=T0P2×uaTK7uB6rQPxbmDwAo&scisig=AAGBfm0AYr2Gx054tN80Ulu6NuinN_wYew&nossl=1&ws=1536x760&at=Systematics%2C%20Speciation%2C%20and%20Distribution%20of%20the%20Subterranean%20Amphipod%20Genus%20Styognectes%20(Gammaridae)&bn=1
  • Holsinger JR (1974) Systematics of the subterranean amphipod genus Stygobromus (Gammaridae), Part I: Species of the Western United States. Smithsonian Contributions to Zoology 160: 1–63. https://doi.org/10.5479/si.00810282.160
  • Holsinger JR (1978) Systematics of the subterranean amphipod genus Stygobromus (Crangonyctidae), Part II: Species of the Eastern United States. Smithsonian Contributions to Zoology 266: 1–144. https://doi.org/10.5479/si.00810282.266
  • Holsinger JR, Longley G (1980) The subterranean amphipod crustacean fauna of an artesian well in Texas. Smithsonian Contributions to Zoology 308: 1–62. https://doi.org/10.5479/si.00810282.308
  • Holsinger JR, Shaw P (1987) Stygobromus quatsinensis, a new amphipod crustacean from caves on Vancouver Island, British Columbia, with remarks on zoogeographic relationships. Canadian Journal of Zoology 65: 2202–2209. https://doi.org/10.1139/z87-334
  • Holsinger JR (1992) Four new species of subterranean amphipod crustaceans (Artesiidae, Hadziidae, Sebidae) from Texas, with comments on their phylogenetic and biogeographic relationships. Texas Memorial Museum, Speleological Monographs 3: 1–22. http://www.nativefishlab.net/library/textpdf/19888.pdf
  • Holsinger JR (2009) Three new species of the subterranean amphipod crustacean genus Stygobromus (Crangonyctidae) from the District of Columbia, Maryland, and Virginia. In: Roble SM, Mitchell JC (Eds) A lifetime of contributions to myriapodology and the natural history of Virginia: A Festschrift in Honor of Richard L. Hoffman’s 80th Birthday. Virginia Museum of Natural History Special Publication 16. Martinsville, 261–276.
  • Holsinger JR, Ansell J, Shafer J (2011) Four new species of the subterranean amphipod genus Stygobromus (Amphipoda: Crangonyctidae) from shallow groundwater habitats on the Coastal Plain and eastern margin of the Piedmont in Maryland and Virginia, USA. Zootaxa 2972: 1–21. https://doi.org/10.11646/zootaxa.4067.1.7
  • Holsinger JR, Ansell L (2014) A new species of the subterranean amphipod genus Stygobromus (Amphipoda: Crangonyctidae) from two caves and a spring in western Maryland, USA with additional records of undescribed species from groundwater habitats in central Maryland. Zootaxa 3768: 386–394. https://doi.org/10.11646/zootaxa.3768.3.6
  • Holsinger JR, Sawicki TR (2016) A new species of the subterranean genus Stygobromus (Amphipoda: Crangonyctidae) from a cave spring in northern Florida, USA. Zootaxa 4067: 088–094. https://doi.org/10.11646/zootaxa.4067.1.7
  • Hunt BB, Norris C, Gary M, Wierman DA, Broun AS, Smith BA (2013) Pleasant Valley Spring: A newly documented karst spring of the Texas Hill Country Trinity Aquifer. Geological Society of America Annual Meeting, South-Central Section (4–5 April) Paper No. 39-3. San Antonio, Texas.
  • Huston DC, Gibson JR (2018) New record of an isolated spring population of Huleechius marroni Brown, 1981 in west Texas. Southwestern Entomologist 43(3): 803–806. https://doi.org/10.3958/059.043.0328
  • Hyman LH (1938) Additional North American cave planarians. Anatomical Record supplement 72(4): 1–137.
  • Kaufmann A (1900) Neue Ostracoden aus der Schweiz. Zoologischer Anzeiger 23: 131–133.
  • Krejca JK (2009) New records for Cirolanides texensis Benedict 1896 (Isopoda: Cirolanidae), including possible extirpations at impacted Texas Caves. Cave and Karst Science 35: 41–46.
  • Külköylüoğlu O, Yavuzatmaca M, Akdemir D, Diaz PH, Gibson R (2017) On Schornikovdona gen. nov. (Ostracoda, Candonidae) from rheocrene springs in Texas (U.S.A.). Crustaceana 90: 1443–1461. https://doi.org/10.1163/15685403-00003707
  • Külköylüoğlu O, Gibson JR (2018) A new Ostracoda (Crustacea) genus, Comalcandona gen. nov., from Texas, USA. Turkish Journal of Zoology 42: 18–28. https://doi.org/10.3906/zoo-1611-52
  • Lewis JJ (2001) Three new species of subterranean asellids from western North America, with a synopsis of the species of the region (Crustacea: Isopoda: Asellidae). Texas Memorial Museum, Speleological Monographs 5: 1–15. https://decapoda.nhm.org/pdfs/4217/4217.pdf
  • McKenzie D, Reddell JR (1964) The caves of Bell and Coryell Counties. Texas Speleological Survey 2: 1–63.
  • Niemiller ML, Porter ML, Keany J, Gilbert JH, Fong DW, Culver DC, Hobson CS, Kendall KD, Davis MA, Taylor SJ (2018) Evaluation of eDNA for groundwater invertebrate detection and monitoring: a case study with endangered Stygobromus (Amphipoda: Crangonyctidae). Conservation Genetics Resources 10: 247–257. https://doi.org/10.1007/s12686-017-0785-2
  • Nissen BD, Devitt TJ, Bendik NF, Gluesenkamp AG, Gibson R (2018) New occurrence records for stygobiontic invertebrates from the Edwards and Trinity aquifer in west-central Texas, USA. Subterranean Biology 28: 1–13. https://doi.org/10.3897/subtbiol.28.29282
  • Norris C, Gluesenkamp A, Singhurst J, Bradby D (2012) A biological and hydrological assessment of the Salado Springs Complex, Bell County, Texas. Texas Parks and Wildlife Department, Austin, 71 pp.
  • Palatov DM, Marin IN (2020) A new genus of the family Crangonyctidae (Crustacea, Amphipoda) from the Palearctic, with descriptions of two new species from the foothills of the Altai Mountains. Zoologicheskiy Zhurnal 99: 1160–1186. https://doi.org/10.31857/S004451342010013X
  • Pilsbry HA (1890) Remarks on certain Goniobases. Nautilus 4: 49–50.
  • Schwartz BF, Hutchins BT, Schwartz ZG, Hess AJ, Bonett RM (2019) Cirolanides wassenichae sp. nov., a freshwater, subterranean Cirolanidae (Isopod, Cymothoida) with additional records of other species from Texas, United States. Zootaxa 4543(4): 498–514. https://doi.org/10.11646/zootaxa.4543.4.2
  • Sidorov DA, Holsinger JR, Takhteev VV (2010) Two new species of the subterranean amphipod genus Stygobromus (Amphipoda: Crangonyctidae) from Siberia, with new data on Stygbromus pusillus (Martynov) and remarks on morphology and biogeographic relationships. Zootaxa 2478: 41–58. https://doi.org/10.11646/zootaxa.2478.1.2
  • Stock JH (1974) The systematics of certain Ponto-Caspian Gammaridae (Crustacea, Amphipoda). Mitteilungen Hamburg Zoologischen Museum and Institut 70: 75–95.
  • Taylor SJ, Holsinger JR (2011) A new species of the subterranean amphipod crustacean genus Stygobromus (Crangonyctidae) from a cave in Nevada, USA. Subterranean Biology 8: 39–47. https://doi.org/10.3897/subtbiol.8.1230
  • Tian L, Smith BA, Hunt BB, Doster JD, Gao Y (2020) Geochemical evaluation of hydrogeologic interaction between the Edwards and Trinity Aquifers based on multiport well assessment in Central Texas. In: Land L, Kromhout C, Byle MJ (Eds) NCKRI Symposium 8: Proceedings of the 16th Multidisciplinary Conference on Sinkholes and the Engineering and Environmental Impacts of Karst, 269–277. https://doi.org/10.5038/9781733375313.1032
  • Trontelj PC, Douady J, Fišer C, Giber J, Gorički Š, Lefébure T, Sket B, Zakšek V (2009) A molecular test for cryptic diversity in ground water: how large are the ranges of macro-stygobionts? Freshwater Biology 54: 727–744. https://doi.org/10.1111/j.1365-2427.2007.01877.x
  • Votteler TH, Gulley RL (2014) The Edwards Aquifer Habitat Conservation Plan: Resolution to over 50 years of water dispute. The Water Report 124: 1–10.
  • Watling L (1989) A classification system for crustacean setae based on the homology concept. In: Felgenhaur BE, Watling S, Thistle AB (Eds) Crustacean issues 6, Functional morphology of feeding and grooming in Crustacea. Rotterdam: AA Balkema, Netherlands, 15–26. https://doi.org/10.1201/9781003079354-2
login to comment