Gryllus montis Weissman & Gray, 2019

Weissman, David B. & Gray, David A., 2019, Crickets of the genus Gryllus in the United States (Orthoptera: Gryllidae: Gryllinae), Zootaxa 4705 (1), pp. 1-277 : 198-204

Gryllus montis Weissman & Gray , n. sp.

Mountain Wood Cricket

Figs 132 , 201–206 , Table 1

‘G. #25, #31’, ‘mountain Gryllus’ and ‘red legged Gryllus’ of DBW notebooks. Distribution. Arizona and western New Mexico.

Recognition characters and song. A polyphyletic complex of sky island taxa, with variable and geographically structured DNA, that we treat here as one “species” because of absence of clearly distinguishing morphological, song, or ecological characters to separate what appears to be up to 4 clades (see Discussion below). A small to medium sized, narrow body, short tegmina, early maturing, generally with black head and pronotum, leaf litter inhabiting, slow chirping cricket found in mountainous, wooded terrain from 1280–2560m, almost always with a tree canopy overhead. Cerci medium length, never longer than ovipositor in situ. Tegmina in both sexes black but can have a tegminal bar, especially in females with reddish hind legs. Hind legs usually black except for reddish inner aspect of hind femur, although most individuals in populations from western New Mexico and Ramsey Canyon, Arizona, have entire rear leg reddish. Frequently the only Gryllus at a site and populations, with few males singing, can be dense. Song ( Fig. 202 , R 13-71 ) 3–5 p/c (range 3–6), 90–150 c/m, PR at 25°C 18–25 (range 17.5–27.8).

G. montis can be separated from other slow chirping western US taxa, as follows: DNA Clade 2 individuals from type locality (Ramsey Canyon, AZ) and DNA Clade 3 individuals most genetically similar to Mohave Desertseparated, and allopatric G. veletisoides but distinguished by cerci 2–4 mm shorter in G. veletisoides which is only found at low elevations and not associated with mountain top woodlands. From Organ Mts., New Mexico, endemic G. sotol (nearest populations are ~ 265 km apart), separated by later maturing, generally more teeth/mm in G. sotol which is associated with open Chihuahuan Desert as opposed to under mountain top tree covered habitats. From ecologically, morphologically and DNA Clade 1 genetically similar but allopatric (nearest populations are ~ 510 km apart on opposite sides of the Rocky Mts.) Davis Mts., Texas, endemic G. planeta , by G. montis having a slower pulse rate ( Table 1 , p. 18), slightly longer cerci, and longer ovipositor. From morphologically and similar song G. lightfooti , distinguished by microhabitat: under tree canopy for G. montis vs. more open, adjacent shrub-grasslands, frequently with Yucca elata , for G. lightfooti . G. montis , despite being at higher, cooler elevations, can become adult a full month before G. lightfooti . Cerci in G. montis never longer than ovipositor in situ while some 50% of G. lightfooti females are. Adult female G. lightfooti typically have distinctive tegminal bars while few females of G. montis do. Chirp rate is more rapid in G. lightfooti . Also, morphologically similar to G. veletis but distinguished by cerci 2–4 mm longer in G. montis and the latter’s preference for tree cover. G. montis DNA Clade 4 and G. veletis are microsympatric at NM, Catron Co., just southwest of Reserve (S01-39) and 3.5 km south of Reserve (S07-53), and separable there by longer cerci length in faster chirping G. montis with entire hind leg reddish, as opposed to almost solid black hind legs of G. veletis . Separated from allopatric (nearest populations are 480 km apart on opposite sides of the Continental Divide) G. transpecos by ITS2 genetics, habitat, shorter ovipositor and longer cerci in the latter. Compared to occasionally sympatric (Kitt Peak, S13-36; road to Hualapai Mt Park, S90-56; Bog Springs, Madera Canyon ) G. longicercus , cerci shorter than ovipositor tip in G. montis with less file teeth and a faster pulse rate ( Table 1 , p. 18). Similar to slow chirping G. saxatilis but G. montis has shorter cerci, a non-rocky habitat, and earlier maturation when individuals from similar elevations compared.

Holotype. Male ( Fig. 203 ): Arizona, Cochise Co., Ramsey Canyon Reserve near Sierra Vista , 1-vi-2013, 5233’, 31° 27’ 34.7” -110° 17’ 44.6”. S13-17, R13-67, G2475. 16 S GenBank accession # MK 446561; ITS2 GenBank accession # MK 441899 . BL21.46, HF 11.4, LC 10.93. Right tegmen removed: 128 teeth, FL 3.35, TL 10.8, TW 4.55. Type deposited in CAS, Entomology #19266.

Paratypes. (267♂ 189♀). Arizona : Clade 1: Chiricahua National Monument, Visitor’s Center, 5348’, 2-vi- 2013 (S13-21) 15♂ 10♀ . Portal , Southwestern Research Station, 20-viii-2012, 5400’ (S12-103) 1♂ 4♀ . Chiricahua Mts. , Herb Martyr Dam Campground, 5620’, 22-vi-2008 (S08-51) 3♂ 1♀ , DC Lightfoot. Cave Creek Canyon, Sunny Flat Campground, 5107’, 21-vi-2008 (S08-50) 6♂ 3♀ , DC Lightfoot. Clade 2: Cochise Co., Bisbee , 5500’, 1-vi-2013 (S13-18) 7♂ 6♀ . Coronado National Forest , Reef Campsite, 29-ix-2012, 7150’, 31.42873° -110.28987° (S12-123) 5♂ 2♀ , all collected as nymphs. Huachuca Mts. , Parker Canyon Lake, 7-iv-2004, 5400’ 4♂ . Ramsey Canyon Preserve , 1-vi-2013 (S13-17) 15♂ 18♀ . Pima Co., Kitt Peak , 17-vi-1990 (S90-52) 3♂ 4♀; picnic area at mile 10.5, 6277’, 8-vi-2013 (S13-36) 9♂ 5♀. Santa Cruz Co., Madera Canyon Rec Area , 4900’, 26-vii-1990, (S90- 79) 14♂ 12♀ ; 5-vii-1994 (S94-57) 7♂ 5♀ ; 11-ix-2010, as nymphs, 5887’, 2010-082 1♂. Pajarito Mts. , Sycamore Canyon, 4017’, 8-iv-2004, 31.4303° -111.1895°, 1♂ , as nymph. Clade 3: Coconino Co., Sedona, 4680’, 25-vi-1980 (S80-44) 2♂ ; 16-v-1995 (S95-37) 1♂ ; 12-vi-1996 (S96-62) 1♂. Hwy 89A 4 m N Sedona, 4900’, 25-vi-1980 (S80- 43) 1♂ ; 12-vi-1996 (S96-63) 3♂ 3♀ ; 15-vi-2007 (S07-60) 4♂ 8♀. Hwy 89A 6 m N Sedona, 5350’, 15-vi-2007 (S07-59) 3♂ . Hwy 89A 8.9 m N Sedona, 15-vi-2007 (S07-58) 2♂ 1♀ . 9 m S Flagstaff on Hwy 89A, MP 390 , 6500 ’ 5-viii-1991 (S91-76) 10♂ 6♀ . 15 m S Flagstaff on Hwy 89A, 6000’, 25-vi-1980 (S80-42) 12♂ 13♀ . Graham Co., Pinaleño Mts. , Hwy 366, Mt. Graham, 5000-8400’, 4-vii-1994 (S94-53) 10♂ 3♀ ; 10-vi-2012, 7900’ (S12-18) 11♂ 4♀. Mohave Co., Hualapai Mt. Park, 6700’, 19-vi, 1990 (S90-55) 11♂ 11♀ ; 3-viii-1991 (S91-62) 1♂ 2♀; 16-vi- 2007 (S07-62, 63) 6♂ 1♀. Road between Hualapai Mt. Park and Kingman: 12.7 m SE Kingman, 6000’, 3-viii-1991 (S91-63) 4♂ 5♀ ; 13-vi-2012 (S12-30) 15♂ 10♀ . 11 m SE Kingman , 5700’, 3-viii-1991 (S91-64) 2♂ ; 16-vi-2007 (S07-65) 2♂ . 8.7 m SE Kingman , 5400’, 19-vi-1990 (S90-56) 4♂ ; 3-viii-1991 (S91-65) 9♂ 8♀ ; 13-vi-2012 (S12- 31) 3♂ 2♀. Mt. Lemmon Recreational Area , Mile 13, 5900’, 27-vii-1990 (S90-81) 6♂ 1♀ ; 7-vii-1994 (S94-60) 8♂ 6♀ ; Mile 11.7, 5800’, 27-vi-2009 (S09-50) 3♂ 4♀ ; Mile 11.3, 5840’, 11-vi-2012 (S12-22) 8♂ 18♀ . Oracle , 4260’, 18-viii-1998 (S98-64) 4♀ . Yavapai Co., Prescott National Forest , Hwy 89A 25 m NE Prescott, 6820’, 30-vi-1994 (S94-38) 7♂ . Sedona Airport, 12-vi-1996, 5060’ (S96-61) 2♂ ; 15-vi-2007 (S07-61) 1♂. New Mexico: Clade 4: Catron Co., Reserve, 5870’ 20-v-2001 (S01-39) 3♂ . Hwy 12 2.2 m SW Reserve, 6020’, 3-vii-1994 (S94-51) 10♂ 1♀ (female collected as last instar) ; 20-v-2001 (S01-40) 2♂ 1♀ ; 14-vi-2007 (S07-53) 2♂ 5♀. Hwy 180 1 m E AZ—NM border, 7880’, 20-v-2001 (S01-41) 4♂, 1 male nymph; 14-vi-2007 (S07-54) 4♂ 3♀.

Derivation of name. “montis” meaning of the mountains to reflect where this complex is found.

Geographic range. Fig. 204 .

Habitat. Straminicolous (living in leaf litter), highest known inhabiting US Gryllus and, along with geographically restricted G. planeta , only obligate forest Gryllus west of Texas. Found in most (every?) sky island woodlands above 1250m of western New Mexico and Arizona. Associated with oaks, pines and occasional junipers and living in leaf litter on forest floor. Also in riparian situations with ash and sycamores (AZ, 6 m N Sedona, S07-59). Rarely in open dirt area at 2408m surrounded by pines (AZ, Mt. Graham, S12-18). After sunset, individuals of both sexes walk around on top of leaf litter with males rarely singing. Nevertheless, some males (e.g. S07-54, near AZ-NM border) sing well into the night at low temperatures that suppress singing in males of most other species.

Life cycle and seasonal occurrence. One generation/year. No egg diapause S91-76 (14.5 km S Flagstaff), S07- 54 (near AZ-NM border), S12-18 (Mt. Graham), S12-103 (Southwest Research Station), S13-17 (Ramsey Canyon). Even in late spring/early summer on Mt Graham, at 2573m (S94-53, 4-vii-1994) and 2408m (S12-18, 10-vi-2012), most of population apparently adult for a while since many with damaged cerci. Yet at the lower type locality (Ramsey Canyon, S13-17), only ~30% of population adult on 1-vi-2013. Both sexes readily attracted to oatmeal trails.

We collected a number of late instar nymphs from AZ, Cochise Co., Reef Campsite (S12-123, 2180m), on 29-ix- 2012, and initially kept them at 27C° on 12L/12D. By 29-xi-2012, 5♂ and 2♀ had molted to adult. Subsequently, all individuals exposed to outdoor photoperiod and temperatures between 12-22°C. Males first started singing in April. If this behavior reflects natural life cycle, then G. montis at Reef Campsite may overwinter as either adults or late instars.

Variation. File tooth number: Individuals on Mt. Lemmon with higher tooth numbers (range 143-171) than elsewhere ( Table 1 , p. 18). Hind femur color: The entire rear leg of most individuals from western New Mexico and the type locality of Ramsey Canyon are reddish. Females in such populations more likely to have tegminal bars. Ovipositor length: Longest known ovipositor (19.8 mm) is from a female from Reef Campsite, Cochise Co. , AZ (S12-123), at 2180m, that was raised to adult in the laboratory.

DNA. This complex appears likely to be polyphyletic (Gray et al. 2019, and see Discussion below) with affinities to other mid to high elevation Southwestern species (e.g. G. sotol , G. planeta , and G. transpecos ) as well as to west coast G. veletisoides .

Discussion. The Madrean Sky Islands of Arizona, Sonora, Chihuahua, and New Mexico are a set of some 60 high elevation mountains rising out of lowland valleys and surrounded by Sonoran and Chihuahuan Deserts ( Warshall 1995). As such, populations of flightless crickets located on such mountain peaks are probably genetically isolated. We are unsure about the relationships of these populations of G. montis as different genes, and the multilocus species’ tree analysis, segregate into different clades. Thus, we summarize these genetic relationships here but leave decisions as to species’ boundaries for future investigations. Should any of these clades have at least one distinguishing morphological character, then species’ status for that clade would be appropriate.

Sequencing ~500 genes with the multilocus technique yields support for 4 clades ( Fig. 201 , and Gray et al. 2019): Clade 1 is found in far southeastern Arizona and includes 2 localities in the Chiricahua Mts.: Chiricahua National Monument (G2464, S13-21) and at the Southwestern Research Station (G2416, S12-103). Clade 2 is found distributed across other southern Arizona sky islands, and includes populations from Huachuca Mts. (G2475, S13- 17, type locality of Ramsey Canyon); Quinlan Mts. (G2491, S13-36, Kitt Peak); Pajarito Mts. (2004-073, Sycamore Canyon); Santa Rita Mts. (2005-012, Madera Canyon ); and the Mule Mts. (G2471, S13-18, Bisbee). Clade 3 is distributed across the remainder of our Arizona mountain localities: Santa Catalina Mts. (G1353, S09-50, Mt. Lemmon); Pinaleno Mts. (G2241, S12-18, Mt. Graham); Hualapai Mts. (G1151, S07-62, Hualapai Mt. Park); and around Sedona (G1097, S07-60) and to the north towards Flagstaff (G1126, S07-59; and G1051, S07-58). Clade 4 includes two New Mexico localities along the border with Arizona (G1123, S07-54) and around the town of Reserve (G1048, S07-53).

If we apply the four clade names from the multilocus analysis to additional samples with sequenced 16S mtDNA ( Fig. 205 ) or ITS2 nDNA ( Fig. 206 ) based on geography, we get additional support for the distinctness of some clades, although with variable consistency. The distinctness of Clade 4 from Clades 1-3 is supported by all analyses; however, we note that inclusion of the Clade 4 samples as G. montis appears to make G. montis polyphyletic. The 16S gene sequences yield a much messier picture: Clade 1 (Chiricahua Mts.) shares haplotypes with G. veletis ; Clade 4 (NM/AZ border, Continental Divide region) shares haplotypes with G. lightfooti ; Clade 3 individuals from the same population, tend to cluster together, but not necessarily especially close to other Clade 3 localities. For ex- ample, Kingman, AZ, Clade 3 samples are well clustered but somewhat separate from Sedona, AZ, Clade 3 samples. The nuclear ITS2 gene sequences demonstrate that G. montis Clade 1 is distinct from G. veletis despite their 16S DNA being the same. G. montis Clade 4 is likewise distinct from G. lightfooti in ITS2 despite their 16S DNA being the same (Tamura-Nei ITS2 distances: within G. montis Clade 4 0.0097 ± 0.0052; within G. lightfooti 0.0073 ± 0.0050; between G. montis Clade 4 and G. lightfooti 0.0307 ± 0.0040). Both Clade 2 and Clade 3 ITS2 sequences do cluster generally together, but with a few anomalous Clade 2 sequences and two groups of Clade 3 sequences, some apparently close to G. longicercus ITS2.

The multilocus analysis also varies in placement of G. montis Clade 1 depending upon analysis method: concatenated analysis places G. montis Clade 1 within the Veletis Group, whereas Astral analysis places G. montis Clade 1 with G. montis Clade 2. Given the apparent capture of G. veletis mtDNA by G. montis Clade 1 and G. lightfooti mtDNA by G. montis Clade 4, and the inconsistency between the concatenated and the Astral analyses, we predict that further more detailed genetic data, e.g. RAD-seq, will reveal a history of hybridization among the southwestern montane species of Gryllus .

During altitudinal transects in Arizona, starting in high elevation trees, one hears G. montis seamlessly transition to lower elevation, more open grassland G. lightfooti on Kitt Peak, Mt. Lemmon, Mt. Graham, Madera Canyon , and the Sedona area, with no or a very narrow zone of overlap. Also, G. montis can be narrowly sympatric, during such transects, with the lower elevation slow chirper G. longicercus (Kingman, Bisbee, Kitt Peak, Mt. Lemmon) . G. montis microsympatric with both G. lightfooti and G. longicercus at 8.4 km SE Hualapai Mt. Park (S90-56) at 1524m, and in the town of Bisbee (S13-18). All 3 sympatric slow chirpers are acoustically distinguishable as follows: G. longicercus with individual pulses countable, both G. montis and G. lightfooti with pulses not countable but chirp rate some 50% slower in former compared to latter.

Hualapai Mt. Park, Mohave Co., AZ, is at 1829m, in good forest, and G. montis is common there. As one drives down Hualapai Mt. Road toward Kingman, female field crickets are occasionally observed wandering on the road. We can thus easily see the transition from almost all black G. montis , without tegminal bars, while under the tree canopy, to G. lightfooti , with tegminal bars, once into more open shrub-grassland. This shift is also seen while driving out of Madera Canyon in the Santa Rita Mountains. For example, at Bog Springs campground area under tree cover at 1527 m elevation, G. montis and G. longicercus found microsympatric (19-viii-2004); within 2.2 km linear distance into Sonoran grassland on Proctor Road at 1333 m elevation, both species completely replaced by G. lightfooti (10-ix-2010). The same situation occurs as one loses elevation going east from the Southwestern Research Station, near Portal, toward New Mexico.

Even surprising for a cricket species that lives at high elevations, repeated attempts to kill adults from Herb Martyr Dam, Chiricahua Mts. (S08-51), by placing them in a home freezer (-15°C) for 1-2 hours duration, all failed. Such treatment normally kills adult Gryllus of all species. On the fourth try, freezing them overnight succeeded.

Parasitized by tachinid Exoristoides johnsoni at both 40 km NE Prescott (S94-38, 2 males: one with 2 and second with 3 larvae); and 3.5 km SW Reserve (S94-51, 2 males: one with 1 and second with 2 larvae). Parasitized by mermithids: 1 female Ramsey Canyon (S13-17). One of seven males collected 26-vii-2005 at Miller Canyon, Huachuca Mountains (31.42620°, -110.25816°) parasitized by tachinid Ormia ochracea (1 larvae).

Figures

FIGURE 13. One second spectrogram of G. bimaculatus, same male as in Fig. 12.

FIGURE 14. Head on view of male G. locorojo showing head stripes.

FIGURE 15. Five second calling song of G. locorojo: (R12-3) commercial pet store, at 22°C.

FIGURE 16. One second spectrogram of G. locorojo, same male as in Fig. 15.

FIGURE 17. ITS2 gene tree. G. brevicaudus samples: S03-8 (G5); S16-1 (G3354, G3393); G. insularis samples: Guadalupe Island, Baja California Norte, Mexico; G. bryanti samples: Andros Island, Bahamas; G. alexanderi sample: Clarion Island, Colima, Mexico.

FIGURE 18. Holotype male, and labels, of G. brevicaudus.

FIGURE 19. Top: Live male (Jasper Ridge, S92-44) G. brevicaudus showing distinctive yellow-orange markings that contrast with rest of black cricket. Bottom: Female from Palo Alto, CA (S87-33) showing short ovipositor.

FIGURE 20. Five second waveform (A) and one second spectrogram (B) of calling song (R03-8) of G. brevicaudus from San Benito Co., CA (S03-8), recorded at 24.5°C.

FIGURE 21. Known distribution for G. brevicaudus. Star shows type locality.

FIGURE 22. Left Panel: G. bryanti (on left) vs. sympatric G. assimilis (right), both from Bahamas. Note head wider than pronotum in G. bryanti. Right Panel: Three second waveform of typical single-pulse chirp calling song of G. bryanti (neotype male, GBM08, Andros Island, at 25 °C).

FIGURE 23. Male holotype (right) and female allotype (left) G. ovisopis.

FIGURE 24. Holotype male (left), G. thinos. Female (right) from type locality showing typical, linear head stripes.

FIGURE 25. Calling song of G. thinos (R07-125) Cameron Co., TX (S07-25), at 25°C: (A) five second waveform, (B) one second spectrogram.

FIGURE 26. Known distribution of G. thinos.

FIGURE 27. ITS2 gene tree showing some separation between Padre Island and Boca Chica samples of G. thinos.

FIGURE 28. Five second waveforms of calling songs of (A) G. pennsylvanicus and (B) G. firmus. G. pennsylvanicus (R04-110) Whatcom Co., WA (S04-91), at 25°C. G. firmus: (R03-255) Gainesville, FL (S03-85), at 25°C.

FIGURE 29. One second spectrograms of (A) G. pennsylvanicus and (B) G. firmus; same males as in Fig. 28.

FIGURE 30. ITS2 gene tree. G. firmus samples: S03-85 (G60, G61, G62); S07-25 (G1073, G1074); S07-26 (G1186, G1235); S10-63 (G1920, G1922); S10-67 (G1915); S11-29 (G2165, G2029, G2034); S13-41 (G2709); S13-59 (G2716); G. pennsylvanicus samples: S08-74 (G709, G710); S11-107 (G2208); S11-108 (G2211).

FIGURE 31. Five second calling song of G. pennsylvanicus (R04-110) Whatcom Co., WA (S04-91), at 25°C.

FIGURE 32. Populations of G. pennsylvanicus studied by us.

FIGURE 33. Size differences, in G. pennsylvanicus, between northern (right) from Berrien Co., Michigan, and southern (left) from Saline Co., KS [S02-49]).

FIGURE 34. Map of G. pennsylvanicus showing variation in file tooth number across the United States. File teeth range from 124 (Vancouver, S00-54)) to 223 (Oklahoma City, S02-48).

FIGURE 35. Long ovipositor G. pennsylvanicus from Saline Co., KS (S02-49).

FIGURE 36. Regression G. pennsylvanicus showing a weak correlation between number of file teeth and hind femur length, the latter a proxy for body size.

FIGURE 37. Regression G. pennsylvanicus vs. G. veletis demonstrating longer ovipositors in the former taxa. Specimens from only the 6 localities discussed in text.

FIGURE 38. Lectotype male, G. firmus, specimen and labels.

FIGURE 39. Populations of G. firmus that we studied.

FIGURE 40. Five second calling song in G. firmus: (R03-255) Gainesville, FL (S03-85), at 25°C.

FIGURE 41. Color variation in Texas G. firmus: lighter, coastal specimens, with head stripes (2 upper photos and lower left), Cameron Co., TX, S07-26 vs. darker, inland specimen (lower right, Schulenburg, TX, S10-65).

FIGURE 42. Egg hatch from single field collected G. firmus (S13-65) from near Schulenburg, TX, showing a mixed egg diapause pattern.

FIGURE 43. Regression file tooth number vs. length hind femur in ‘G. #19’ vs. ‘G. near #19.’

FIGURE 44. Regression length ovipositor vs. length hind femur in ‘G. #19’ vs. ‘G. near #19.’

FIGURE 45. Regression body length vs. ovipositor length using combined data for G. firmus and G. pennsylvanicus from Larson et al. (2013).

FIGURE 46. Regression pronotal width vs. ovipositor length using combined data for G. firmus and G. pennsylvanicus from Larson et al. (2013).

FIGURE 47. Regression hind femur length vs. ovipositor length using combined data for G. firmus and G. pennsylvanicus from Larson et al. (2013).

FIGURE 48. Regression hind femur length vs. ovipositor length in G. firmus vs. G. pennsylvanicus.

FIGURE 49. Regression cercus length vs. ovipositor length in G. firmus vs. G. pennsylvanicus.

FIGURE 50. Regression cercus length vs. hind femur length in G. firmus vs. G. pennsylvanicus.

FIGURE 51. Regression number of file teeth vs. pulse rate in G. firmus.

FIGURE. 52. Regression number of file teeth vs. pulse rate in G. pennsylvanicus showing males with higher numbers of file teeth have lower pulse rates.

FIGURE 53. Regression number of file teeth vs. pulse rate for combined comparison between G. firmus and G. pennsylvanicus.

FIGURE 54. ITS2 gene tree. G. multipulsator sample: S03-41 (G577); G. assimilis samples: S10-64 (G1901); S16-12 (G3367, G3373); G. locorojo sample: type locality (Rainbow Mealworms); G. veintinueve samples: S02-39 (G134); S07-21 (G1139); S07-27 (G1140, G1211); S09-71 (G1451); OK, Love Co., Hwy 32 at Boggy Creek (2015-055).

FIGURE 55. Five second waveform (A) and one second spectrogram (B) of calling song (R09-89) of G. veintinueve from type locality (S09-71), recorded at 25°C.

FIGURE 56. Regression width pronotum vs. length hind femur in G. veintinueve vs. sympatric G. veletis, showing near morphological separation.

FIGURE 57. ITS2 gene tree. G. veintinueve samples: S02-39 (G134); S07-21 (G1139); S07-27 (G1140, G1211); S09-71 (G1451); OK, Love Co., Hwy 32 at Boggy Creek (2015-055). G. vernalis samples: S03-56 (G27, G1739); S03-62 (G31, G33). G. fultoni samples: S03-62 (G32, G34); S03-64 (G35), S07-22 (G1138). G. veletis samples: S03-58 (G39); S03-60 (G30); S15-9 (G2939); S15-16 (G2927, G2934); S15-21 (G2899); S15-24 (G2936); S15-25 (G2963, G2968, G2983); S15-53 (G3304, G3343).

FIGURE 58. Holotype male (left), G. veintinueve, paratype (middle) female (S09-71), and color variant (right) male (S02- 46).

FIGURE 59.. Known US distribution of G. veintinueve.

FIGURE 60. Five second waveforms of calling songs of (A) G. assimilis and (B) G. multipulsator. (A) G. assimilis: (R13-231) Rio Hondo, TX (S13-44), at 25°C; (B) G. multipulsator: (R15-325) Pima Co., AZ (S15-108), at 25.4°C.

FIGURE 61. One second spectrograms of G. assimilis (A) and G. multipulsator (B), same males as in Fig. 60.

FIGURE 62. ITS2 gene tree. G. assimilis samples: S10-64 (G1901); S16-12 (G3367, G3373); G. multipulsator sample: S03- 41 (G577); G. locorojo sample: type locality (Rainbow Mealworms); G. veintinueve samples: S02-39 (G134); S07-21 (G1139); S07-27 (G1140, G1211); S09-71 (G1451); OK, Love Co., Hwy 32 at Boggy Creek (2015-055).

FIGURE 63. Neotype male, Gryllus assimilis, photographs and labels.

FIGURE 64. Color variation in G. assimilis from reddish female (left, Brackettville, TX, S10-63) to dark male (right, Quintana Roo, Mexico, S02-12). Note head narrower than pronotum and hirsute and dull pronotum surface.

FIGURE 65. Top: Five second waveform of calling song of G. assimilis (R13-231) Rio Hondo, TX (S13-44), at 25°C; Bottom: One second waveform of same song showing individual pulses.

FIGURE 66. Known US distribution, G. assimilis within native range (also found introduced in south Florida, see SINA: https://sina.orthsoc.org/).

FIGURE 67. Holotype male, Gryllus multipulsator, specimen and labels.

FIGURE 68. Color variation in G. multipulsator, from reddish male (left, Riverside Co., CA, S03-41); brown female (middle, Santa Cruz Island, CA, S04-65); black male (right, Riverside Co., CA, S03-41).

FIGURE 69. Top: Five second waveform of calling song of G. multipulsator (R15-325) Pima Co., AZ (S15-108), at 25.4°C; Middle: One second waveform of same song showing individual pulses; Bottom: Expansion of an individual chirp showing decreasing pulse rate towards end of chirp.

FIGURE 70. Known US distribution, G. multipulsator.

FIGURE 71. Five second waveforms of calling songs of (A) G. rubens, (B) G. texensis, and (C) G. regularis. (A) G. rubens: (R13-220) Tulsa, OK (S13-68), at 25°C; (B) G. texensis: (R13-224) Rio Hondo, TX (S13-44), at 26°C; (C) G. regularis (R99- 211) Sinaloa, MX (S99-86), at 25.5°C.

FIGURE 132. ITS2 gene tree. G. planeta samples: S15-61 (G3088, G3094, G3114, G3135, G3344, G3345, G3347); S15-63 (G3130). G. veletis samples: S03-58 (G39); S03-60 (G30); S15-9 (G2939); S15-13 (G2884, G2929); S15-16 (G2927, G2934); S15-21 (G2894, G2895, G2896, G2899, G2942); S15-24 (G2936); S15-25 (G2963, G2968, G2983); S15-53 (G3304, G3343); S15-62 (G3131, G3134); S15-67 (G3137, G3144); S15-78 (G3145, G3147); Salt Lake City, UT (2009-013). Most ITS2 sequenced western US G. veletis samples match closely with the two eastern US samples from near the type locality, but a few samples from eastern NV, central NM, and west TX are genetically somewhat divergent. G. montis Clade 1 ITS2 sequences fall within this Group, but alternative placements are supported by different genes and analysis methods (see under G. montis, page 201, for discussion).

FIGURE 201. Known distribution of G. montis, with locality coding based on multilocus DNA Clade.

FIGURE 202. A. Typical calling song of G. montis (R13-71) from the type locality (S13-17), recorded at 25.5°C. B. One second spectrogram of typical calling song of G. montis, same male as in A.

FIGURE 203. Holotype male (left) and type locality female (right) of G. montis.

FIGURE 204. Known distribution of G. montis.

FIGURE 205. 16S gene tree, indicating multilocus DNA clade based on locality. G. montis Clade 1 samples (orange) mostly have 16S DNA like G. veletis, as do two G. montis Clade 3 samples (blue, both from Mt. Graham). G. montis Clade 2 samples (green) fall into two groups. G. montis Clade 3 samples mostly fall into two geographically separated groups (Hualapai Mtn. near Kingman, AZ, and Sedona, AZ area). G. montis Clade 4 samples have 16S DNA like G. lightfooti. Collection stop numbers: G. montis samples: S07-45 (G1194); S07-54 (G1123, G1154, G1226); S07-58 (G1051, G1216); S07-59 (G1095, G1126); S07-60 (G1052, G1201); S07-62 (G1102, G1151); S07-63 (G1129, G1207); S07-65 (G1103, G1132); S08-50 (G690, G691); S08-51 (G700); S12-18 (G2241, G2249); S12-30 (G2251, G2257); S12-31 (G2262); S12-103 (G2416); S13-17 (G2475, G2857, G2859); S13-18 (G2461, G 2471); S13-21 (G2462, G2464, G2466); S13-36 (G2487, G2489, G2491, G2499); Parker Canyon Lake, Cochise Co., AZ (2004-44, 45, 47, 50, 73); Madera Canyon, Bog Springs, Santa Cruz Co., AZ (2004-118, 2005-003, 012); Madera Canyon, Mt. Wrightson picnic area, Santa Cruz Co., AZ (2010-082); Cave Creek Canyon, Chiricahua Mts., Cochise Co., AZ (2005-115, 122, 127, 131, 133, 136, 137, 143); Miller Canyon, Huachuca Mts., Cochise Co., AZ (2005-169, 176, 179, 181, 192, 193, 194); Reef Camp, Huachuca Mts., Cochise Co., AZ (2012-219, 220, 226). G. veletis samples: S04-107 (G2861, G2862); S07-51 (G1155, G1159); S07-53 (G1120, G1122, G1157); S07-57 (G1056, G1093); S07-72 (G1150); S08-53 (G703, G704); S09-63 (G1355); S15-19 (G2892, G2960, G2999); S15-25 (G2955, G2963, G2968, G2983, G2992); S15-51 (G3099, G3127); S15-53 (G3343); S15-67 (G3144); S15-78 (G3145, G3147). G. lightfooti samples: S09-51 (G1368); S09-59 (G1350); S11-86 (G2205); S11-88 (G2206). G. saxatilis samples: S15-89 (G3201, G3203). G. planeta samples: S15-61 (G3088, G3094, G3114, G3135, G3347); S15-63 (G3130).

FIGURE 206. ITS2 gene tree, indicating multilocus DNA clade based on locality. G. veletis samples: S03-58 (G39); S03-60 (G30); S15-9 (G2939); S15-16 (G2927, G2934); S15-21 (G2895); S15-24 (G2936); S15-25 (G2968, G2983); S15-53 (G3343); S15-62 (G3131, G3134, G3304); S15-67 (G3137, G3144). G. montis samples: S07-53 (G1046, G1047, G1048); S07-54 (G1123, G1226); S07-58 (G1051, G1094, G1216); S07-59 (G1095, G1096, G1126); S07-60 (G1052, G1097, G1127, G1128, G1201); S07-62 (G1102, G1151); S07-63 (G1129); S07-65 (G1103, G1132); S08-50 (G690, G691); S09-50 (G1353); S12-18 (G2241, G2249); S12-22 (G2273); S12-30 (G2251); S12-103 (G2416); S13-17 (G2472, G2475, G2857); S13-18 (G2461, G2471, G2482; S13-21 (G2462, G2464, G2466, G2467); S13-36 (G2487, G2489, G2491); Parker Canyon Lake, Cochise Co., AZ (2004-44, 45, 50, 73); Madera Canyon, Bog Springs, Santa Cruz Co., AZ (2004-118, 2005-003, 004, 009, 012); Miller Canyon, Huachuca Mts., Cochise Co., AZ (2005-169, 176, 180, 181, 182); Reef Camp, Huachuca Mts., Cochise Co., AZ (2012-219, 220, 222, 223, 226). G. longicercus samples: S12-23 (G2245, G2247, G2260, G2261); S15-52 (G3086, G3276).