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AM. ZOOLOGIST, 8:459-469 (1968). Some Thermal Requirements of Fiddler Crabs of the Temperate and Tropical Zones and Their Influence on Geographic Distribution DON CURTIS MILLER Department of Biological Sciences, Union College, Schenectady, N. Y. 12308, AND F. JOHN VERNBERG Duke University Marine Laboratory, Beaufort, North Carolina 28516 SYNOPSIS. Thermal stress is one environmental parameter that has greatly influenced the migration of crustaceans from the sea to land. Since a greater number of species of terrestrial crabs are found in the tropics than in the temperate zone, comparative studies of the influence of temperature on latitudinally separated populations were undertaken. Two tropical species, U. rapax and U. thayeri, may occur as far north as St. Augustine, Florida, or, following a severe winter, may be rare north of Cape Kennedy. The lethal elfect of the low temperatures recorded during one severe winter (1957-58) is supported by laboratory studies in which LD^, deaths occurred in 4.5 days at 10°C for U. rapax acclimated to 18°C. The experiment demonstrates that U. rapax cannot acclimate to and survive low tempeiatures. This contrasts markedly with the situation in semi-terrestrial crabs of the temperate zone, which are able to acclimate to cold. The distribution of Uca around Cape Cod Bay correlates well with the coastal hydrographic thermal gradient and supports Passano's suggestion that temperatures below 20° may be limiting as they inhibit proecdysis in U. pugnax. Such an inhibition is found experimentally in U. pugilator and in the tropical species, U. rapax. It is hypothesized that a shift in the thermodynamics of the processes underlying molting has not occurred in Uca of the temperate zone. The paucity of semi-terrestrial Brachyura in the temperate zone may be due to the failure of many species to evolve capacity-adaptations to carry out all requisite life processes at temperatures below 20°, or the resistance-adaptations necessary to survive the low temperatures of winter. Considerable knowledge regarding physiological adaptations of Crustacea for semi-terrestrial life has been obtained from studies of factors influencing distribution of organisms across the moisture gradient of the intertidal zone. In contrast to these investigations along the sea to land gradient, another approach that serves to demonstrate adaptations to the rigors of terrestrial life involves comparative studies along a latitudinal gradient, This is a valuable approach with such semi-terrestrial Crustacea as the fiddler crabs. Conditions within their intertidal habitat differ greatly with latitude, basically as insolation, coastal water temperatures, and tidal regimes vary. Additionali .• • . r r ly, the genus Uca comprises a large num6 6 " " b e r °£ species, most of which are limited to the tropics. Yet a few species have also successfully invaded the temperate zone. is certainly T h e l a t k u d i n a l apprOaCh ' ' . ' salient, for as we consider terrestrial adaptations, we should note that among brachyurans in general, very few species h b e e n successful i n adapting both to .. , . j Much of the original work reported in this paper . , ? , . y , . ' '. . was carried out by the senior author in partial fulfillment of the requirements for the degree, Doctor of Philosophy, at Duke University, and supported by N. S. F. Crams G-5577 and G-8788 to F. J Vernberg. The authors gratefully acknowledge the marine laboratories which provided facilities and assistance during this study: The Research Laboratory, Marine Studios, Marineland; Entomological Research Center, Florida State Board of Health, Vero Beach; Institute of Marine Biology, University of Puerto Rico; Marine Biologia llfe a b o v e t h e t l d e l m e a cal Laboratory, Woods Hole; and Duke University Marine Laboratory. and seasonally-fluctuating 459 n d t o a w l d e thermal re- 460 DON CURTIS MILLER AND F. JOHN VERNBERG gime. On our East coast, the ghost crab, Ocypode quadrata, is one of the most terrestrial forms. The principal semiterrestrial brachyurans of the temperate zone include three species of Uca and two of Sesarma. Along our Pacific coast also, the number of semi-terrestrial species in the temperate zone is small compared to the number in the tropics. A disparity between the number of species found in the tropics and that found in higher latitudes is generally recognized for a variety of aquatic and terrestrial habitats. Fluctuating thermal conditions appear to be most responsible for this disparity. Elucidation of the limiting action of latitudinal variables such as temperature is of interest not only to the biogeographer, but also to the comparative physiologist. Some thermal problems and adaptations to be discussed in this paper were observed during a study of various factors limiting the geographic distribution of certain fiddler crabs of the temperate and tropical zones. Although substrate preference and salinity tolerance were taken into consideration (to be reported in a subsequent paper), it was mainly studies on temperature that provided positive correlations with observed latitudinal distribution patterns of the crabs. The geographic distribution of Uca along the East and Gulf coasts can be described as follows: The three species of the temperate zone, U. pugnax, U. pugilator, and U. minax, reach the northern extreme of their range in the vicinity of Cape Cod, Massachusetts. They are reported to range as far south as Florida and along the Texas coast (Rathbun, 1918), although only U. pugilator has continuous distribution around the southern portion of Florida. Several species of tropical fiddler crabs are also found on the East coast of Florida: U. speciosa, U. mordax, U. rapax, and U. thayeri. The latter three species extend to the northern third of the coast, and hence they have a range which overlaps all three species of the temperate zone. FIELD STUDIES Field methods centered upon assessment of the success of populations at stations initially chosen for their apparent ecological or geographic importance, or both. Success of populations was measured by estimating density with the direct sampling method employed by Teal (1958) in his study of Uca. The carapace of crabs recovered was measured in order to obtain an expression of density based on the carapace area per 1/5 m2 sample. Density values were averaged for each station and the ratio of density : sample area expressed as a percentage of the 1/5 m2 sample unit. Sampling stations were chosen on the basis of their apparent relatively high population density, because the purpose of sampling was to determine maximal densities achieved by the crabs at a given location. When a relatively dense burrowing area was located within a habitat of homogeneous character, samples were taken in a transect across this area. Environmental data on temperature, salinity, substrate, and vegetational characteristics were collected at the time of sampling. In addition, data were collected over longer periods at certain geographically important stations. Studies near Boundaries of the Geographic Range in Florida, East Coast, 1958-1962 Two fiddlers of the temperate zone and three tropical species reach the limit of their respective geographic ranges along the East coast of Florida between Cape Kennedy and the border of Georgia. Uca pugnax and U. minax are quite rare along the central portion of the coast, south of Ponce de Leon Inlet. The observed northern limits of the range for the tropical species are as follows: U. speciosa, just north of Cape Kennedy; U. rapax, in the vicinity of St. Augustine; and U. thayeri, north of Jacksonville Beach. Salmon (1967) found U. mordax as far north as Daytona Beach. The population density achieved by crabs at some of the stations close to the 461 THERMAL REQUIREMENTS OF FIDDLER CRABS TABLE 1. Maximal density of Uca near the boundaries of its geographic range, Florida East Coast. Areas with allopatric distribution. Av. carapace area: Sample area Percentage No . crabs/sample Av. (range) Station and habitat 1958 1960 1962 1958 1960 1962 Uca pugnax Crescent Beach, Short Spartina 5(4-7) 11(8-14) 11(9-13) 4.9 5.8 4.9 14(9-22) n —5 12 (7-20) n z= 11 18(17-20) n= 3 12(8-17) 20(14-31) n = 10 11(7-17) n= 4 9(7-11) n= 5 6.7 85 9.1 5.0 4.2 5.8 Crescent Beach, Salicornia marsh Johnson's Fish Camp, 4 mi. so. Marineland, Batis marsh Mouth of Bulow Creek, Volusia Co., Batis marsh Uca minax Mouth of Bulow Creek, Volusia Co. Silty Batis and Salicornia marsh Uca rapax Pepper Park, Ft. Pierce, clay, sand, and shell fragments on tidal barren Uca thayeri Marineland, low Batis and yellow mangrove marsh Pepper Park, Ft. Pierce, muddy bank with some surface sand n — 4 7.8 4(2-5) 4(3-7) n= 5 12 (7-18) n= 6 9(6-11) n= 4 3.87 2.8 6.2 7(4-9) n= 4 5(4-6) n= 3 limits of their geographic range is presented in Table 1. For most of these species, population densities obtained at stations well within their respective geographic range are also included for comparison (Table 2). Few data are available for U. minax and U. thayeri, because they often inhabit creek banks or build deep and complex burrows where it is difficult to use the direct sampling method. The densities of U. rapax reported here must be 5.6 7.7 7.4 interpreted with some caution, since Salmon (1967) recently found that U. mordax occurs sympatrically with U. rapax between Stewart and Daytona Beach, Florida. These two species are very similar morphologically but distinct in their sound production and courtship display. None of the specimens retained from our study at the stations in question appear to be U. mordax, however. Populations of U. pugnax and U. mi- TABLE 2. Maximal density of Uca in North Carolina and Puerto Rico. Species and habitat No. samples No. crabs/sample Av. (range) A. Beaufort, North Carolina U. pugilator—Silty sand beach 9 12 Clean sand beach 12 U. pugnax—Tall Spartina marsh 7 Short Spartina marsh B. Parguer; Puerto Rico U. rapax—muddy tidal flat 12 Salt flat, fine shells and clay 10 U. thayeri—Ecotone between black man8 groves and muddy tidal flat Av. carapace area: Sample area 41 (27-58) 27 (14-42) 14 (7-20) 13(8-19) 23.4 11(6-15) 15(11-30) 6(3-8) 45 6.7 7.4 4.8 7.7 7.9 462 DON CURTIS MILLER AND F. JOHN VERNBERG nax were found to inhabit large areas of the marsh at the stations listed in Table 1, and they achieved high densities in favorable portions of their habitat. The densities for U. pugnax in Florida are comparable to those recorded in the vicinity of Beaufort, North Carolina. Hence, for the species of the temperate zone there was reduction neither in the maximal density achieved by the populations nor in the general size of the area inhabited by the crabs as far south as the Bulow Creek station. This station is only 30 miles, measuring latitudinally, from the Ponce de Leon Inlet near New Smyrna Beach, the vicinity of the southern extreme of the range of these crabs. The tropical crab, U. rapax, was found as far north as St. Augustine, yet population densities comparable to those observed in Puerto Rico were found only at Ft. Pierce, some 170 miles, latitudinally, south of St. Augustine. The populations of U. rapax found along the northern portion of the Florida coast were distributed sympatrically, occupying the narrow portion of the intertidal zone between the high sandy areas inhabited by U. pugilator, and the lower muddy marsh of U. pugnax. At several stations between Marineland and Oak Hill, the average carapace area density achieved by U. rapax ranged from 2.0 to 2.5% of the sample area. Temperature is suggested as one major factor limiting U. rapax in the marshes of northern Florida. In 1957, Tashian and Vernberg (1958) found U. rapax near St. Augustine. Yet the next year, following a very severe winter, no specimens were found north of Flagler Beach, and U. rapax was rare in marshes near New Smyrna Beach. Subsequent studies in 1960 and 1962 showed re-establishment of small and sparse populations in these areas. The disappearance of U. rapax in northern Florida subsequent to 1957 is thought to be due to winter kill. There were two prolonged cold spells in this region during January and February, 1958. At Marineland, the mean daily air tem- perature was below 13°C during nearly two-thirds of this period. This included four consecutive days in January and eight in February with a mean temperature below 8°C (unpublished records, Marine Studios). While comparable data on temperature are not available for the Uca habitats at this locality, it is plausible that temperatures approaching 10° prevailed at the level to which the crabs burrowed. In the laboratory the median lethal death point (LD50) at 10° for U. rapax was found to occur in 4.5 days. This value is based on a run utilizing 60 crabs collected in September at Ft. Pierce, Florida, and acclimated to 18° for one week prior to exposure to 10°. The suggestion that low winter temperatures limit the northward distribution of adults of the tropical species, U. rapax, in Florida is in agreement with findings of Vernberg and Tashian (1959) on thermal death limits. They observed a marked difference in survival between U. rapax and U. pugnax upon exposure to cold. At 7°C the LD.,0 for U. rapax was 30-40 minutes, while mortality for U. pugnax was very low, even after two weeks. Vernberg and Tashian concluded that U. rapax is not capable of acclimating to low thermal conditions, while U. pugnax can. This conclusion, based on thermal tolerance data, was soon substantiated in the same species by Vernberg (1959), in a study of the influence of temperature acclimation on O2-consumption of the whole animal. Figure 1 depicts the genotypic limits of O2-consumption in U. rapax and U. pugnax, using data from coldacclimated (15°) and warm-acclimated (25°) animals. Of interest to the present discussion is the inability of the tropical crab, U. rapax, to make significant metabolic compensation to temperatures of 15° and below. In a recently completed study of temperature and salinity tolerances of larval Uca, Vernberg and Costlow (unpublished) found that first zoeae of U. rapax are amazingly resistant to low temperature. No mortality occurred among the THERMAL REQUIREMENTS OF FIDDLER CRABS 463 25% in any experimental group, except for U. minax at 667<c, when maintained at 36°. It is significant that few differences were seen between the tolerances of U. pugnax and U. minnx to these conditions and that of U. pugilator, even though the latter species thrives along the southern coast of Florida. It is apparent that U. pugnax and U. minax are not restricted to the northern Florida coasts by limitations in the adaptations of the adults to high temperature. Two studies on laboratory-reared larvae have also failed to show meaningful differences in the thermal adaptations of U. pugnax or U. minax compared with lemperoflure 'c more southerly species. Considering O2FIG. 1. Genotypic limits o£ O2 consumption of consumption in first zoea, megalops, fiddler crabs from the tropical and temperate and young crabs, Vernberg and Costlow zones. These limits were determined at various (1966) observed no clear relationship betemperatures by Vernberg (1959) using data from ween geographic distribution and metabcold- and warm-acclimated animals. (Reproduced from Temperature: Its Measurement and Control olism. Likewise, their recent study of in Science and Industry, American Institute of Phys- tolerances in larval Uca did not show any ics, vol. 3, Part 3, J. D. Hardy, Editor, by permisconsistent differences either among the sion of Reinhold Book Corporation, a subsidiary of three species of the temperate zone, or Chapman-Reinhold Inc., 1963, New York). when these three species were compared larvae at 5°C after 4 hr o£ exposure, while with the tropical crabs, U. rapax and U. the LD50 for adult U. rapax is 35 min at thayeri. 7°C. These data suggest that early zoeal stages of this tropical species may be able Studies Near Boundaries of the Geographto survive in the coastal waters north of ic Range in Massacliuset.ls, 1959 Florida, yet the species does not become Field studies carried out along the Masestablished because a later stage is less sachusetts coast considered only two of tolerant to low temperatures. the species in this part of the temperate The factors limiting the range of the two crabs of the temperate zone at Ponce zone: U. pugnax and U. pugilator. The de Leon Inlet have not been determined, third, U. minax, has been collected at a although the following experiments on West Falmouth marsh (Prosser, Sandeen, survival at different combinations of tem- personal communications) and recorded perature and salinity were conducted. from the other side of Buzzards Bay by The laboratory tests examined the tolerance Rathbun (1918), but was not found by of all three temperate-zone species to the us. Along the south shore of Cape Cod combined stress of high temperature (32 to large populations of both U. pugnax and 36°C) and extremes of salinity (6.0 and U. pugilator are found. The densities at&&'/,,). While salinities of these magnitudes tained by U. pugnax at two stations near are common in the tropics, temperatures at Woods Hole (Table 3) are comparable to this high level would not plausibly prevail those seen in North Carolina (Table 2). longer than the daytime 12-hr period of In contrast, very low densities were resolar heating. Yet in the laboratory, even corded for U. pugilator in this area. This after six days of exposure to the above is most certainly due to the heavy collectstress conditions, mortality did not exceed ing pressure imposed upon these popula- 464 DON CURTIS MILLER AND F. JOHN VERNBERG tions by workers at the Marine Biological Laboratory. On the north side of the Cape, the distribution reflects the summer atmospheric and hydrographic thermal gradient that exists along the shore line of Cape Cod Bay. Large populations of both species, attaining high densities, are 8. to irS 2 3« oq <£> p 06 oo ~ 1 SS. i a. O> »£> Th ^ g OI00O O found in the vicinity of Wellfleet and First Encounter Beach. Proceeding westward, the populations became smaller and smaller with respect to the area of beach or marsh inhabited. U. pugilator was not found any farther west than Barnstable Harbor, nor was it located in a search of protected sandy areas as far north as Cape Ann. U. pugnax was found in a marsh near East Sandwich Beach, inhabiting an area less than 25 m2, yet with a high density. Very small populations of this species were also found at three northern stations along the Massachusetts mainland: South Duxbury and Brant Rock, just above Plymouth, and Danvers, just north of Boston. Except for Wellfleet and First Encounter Beach, U. pugnax was found only in uniquely sheltered microhabitats, along tidal creeks some distance inland from the bays. In these areas, local warming is enhanced during the summer; the coastal topography protects the marshes from sea breezes, and the long circuitous marsh creeks enhance warming of the flooding tidal waters as well. © c*t od Did a "a, g o s •s ° 3 S o u u c e •J O C •" ' The success of fiddler crabs along the eastern shore of Cape Cod Bay can also be correlated with local warming, which is enhanced by shoals that extend offshore for several miles. In this region, the 15-fathom contour is up to 7 nautical miles off shore . Considerable atmospheric warming of the shoal waters does occur, according to Bigelow (1927). He observed the maximum temperatures of shore waters around Cape Cod Bay to occur from the last week of July into midAugust. By mid-August the 18° isotherm enclosed the shore waters all along Massachusetts Bay and down into Cape Cod Bay as far as Sandwich. Here there is little shoaling and the 15-fathom contour lies within 1 to 2 miles off shore. The remainder of the shore water of Cape Cod Bay east of Sandwich was above 18°, with 20° being the maximum observed. These differentials in temperature of the coastal waters can be validly related to the habitat temperature of Uca in the summer, 465 THERMAL REQUIREMENTS OF FIDDLER CRABS TABLE 4. Effect of temperature on molting in eyestalkless Uca. No. of crabs (after initial mortality) Temp, treatment % °C Molt Post-treatment % in pro- % Reecdysis maining U. pugnax 40 40 40 39 40 Controls 20 15.3 17.6 20.2 0 0 10 21.9 24.6 35.9 97.5 50 0 0 41 52 70 77.5 46.2 27.5 29.5 0 0 87.5 18.0 0 0 92.8 86.7 95 U. rapax 14 15 17 20 15 20.0 22.7 25.1 27.5 70 80 0 20 53 85 80 27.5 0 0 23 33 30 15.2 18.0 20.0 0 3 0 22 22.3 25.0 31.8 54.2 0 0 6.7 73 71 0 0 35.3 47 10 0 Total % Remaining % Molt Mean duration of proecdysis and standard deviation (20 days at 29.5°) 0 62.5 0 57.5 0 52.5 0 30.8 0 17.5 62.5 57.5 62.5 66.7 67.5 33.5 -i- 3.63 31.6 •+- 5.08 25.7 -i- 5.35 22.0 •+- 4.92 19.0 ± 5.83 0 — % Molt 0 70 (24 days at 27.5°) 21.4 71.4 6.7 73.3 5.9 35.3 10 0 0 0 71.4 73.3 70.6 80 80 35.8 28.0 24.0 14.9 10.0 -t- 2.62 -t- 3.63 -»- 5.13 -+- 4.57 ± 2.41 Controls 15 100 V. pugilator 24 91.3 87.9 90 45.8 8.3 46.6 13.3 (22 days at 25°) 21.7 52.2 73.6 76.6 41.7 8.3 9.1 0 0 0 13.3 — 52.2 38.3 -t- 5.23 76.6 76.6 73.5 36.2 •+• 6.75 30.2 •+• 5.11 62.5 23.7 -+- 3.94 17.9 ± 6.63 0 — Controls 20 25 85 when the burrows are open. It is this water that will be covering the marshes at high tide, and hence it contributes directly to the crab's summer thermal regime. INFLUENCE OF LOW TEMPERATURE ON GROWTH AND MOLTING One way in which low temperature may limit these semi-terrestrial crabs north of Cape Cod is by its inhibiting effect on molting. Passano (I960) demonstrated that low temperature blocked the proecdysial phase of the molting cycle in U. pugnax. Molting can normally be induced by removing the eyestalks and hence extirpating the X-organ-sinus gland complex, which produces molt-inhibiting hormone (MIH). In his experiments, at least 70% of the crabs maintained at 22.2° and above molted within 23 days, while none of the crabs held at 20° or below molted during this period. Temperatures between 15° and 22° considerably extended the duration of proecdysis, hence delaying molting, and at 15°C and 0 70 below, proecdysis was not initiated. The onset of proecdysis can be determined by observing a sharp increase in the rate of regenerative growth of a walking limb, which is known to be dependent on proecdysis. This increased rate of growth of the new limb, which is now influenced by molting hormone (MH) produced by the Y-organ, will continue until ecdysis (Bliss, 1960; Passano and Jyssum, 1963). Passano's experiment has been repeated using the same species, and two additional ones, U. pugilator and U. rapax. Figure 2 shows the rate, expressed as cumulative percentages, at which molting occurred in each experimental group. Table 4 summarizes the data, which were similar in all three species to those of Passano. There were two differences with U. pugnax: 10% of the group at 20.2°C molted during the experimental period, while none in Passano's 20° group molted. Also, all of the curves expressing percentage of ecdysis as a function of time were 466 DON CURTIS MILLER AND F. JOHN VERNBERG smaller, ranging from 13-18 mm in breadth of carapace. Another variable affecting molting time in eyestalkless crabs is their nutritional state. Should the inhibiting effect of low temperatures on molting play a substantial shifted to the left about three days, and the mean duration of proecdysis was shorter in the present experiment. These results may reflect differences in the size of the experimental animals. The North Carolina U. pugnax were all 00 U. pugnax 80 60 : : : : | : A - 2 4 .6° C B - 21. 9 C - 20 .2 D- 17. 6 E- 29.5° C 15 3 40 / / / IW y yy /z'A A/B.' 20 / • / E o -^\\/ 1 / y 0 Groups - AH • 1 10 No. I 15 20 of Treatment : : •' / 25 Days y 1 1 1 t 30 35 40 45 Groups - 30 35 2A 100 U. p u g i l a t o r o> c i All 80 25.0°C a o 6° o * 40 CD 20 E o 10 2B 15 20 No. of Treatment 25 Days 40 45 4G7 THERMAL REQUIREMENTS OF FIDDLER CRABS 100 . U. rapax All 80 Groups — 27.5° C 60 * 40 > E o 20 10 15 No. of 20 25 Treatment 2C FIG. 2. Cumulative percentages of molting in Uca for each temperature-treatment group following removal of eyestalks. All groups in each experiment role in limiting Uca north of Cape Cod, it remains speculative whether temperature is acting on a larval stage or on the adults. The occurrence of a few small populations of U. pugnax discontinuously distributed in sheltered habitats north of Plymouth suggests that at least during some years the larvae are able to develop in these colder bay waters. Also, during Vernberg and Costlow's recent investigation of larval tolerances, larvae of both U. pugnax and U. pugilator molted at 15°. They did not complete development; but this could be due as much to the rearing technique as to temperature, since Uca is very difficult to rear in the laboratory. DISCUSSION OF THE INFLUENCE OF LOW TEMPERATURE ON SEMI-TERRESTRIAL CRUSTACEA Low temperature appears to limit certain fiddler crabs geographically (1) by killing adult tropical Uca through extreme winter lows in northern Florida, 30 35 40 45 Days were maintained at one high temperature following the 23-day initial period of temperaturetreatment. and (2) by blocking proecdysis in crabs north of Cape Cod. The basic difference between these two thermal effects is one of intensity. Low temperature may be ecologically limiting through (a) immediate lethal inhibiting effects, which cause death after relatively short exposure to cold by inhibiting basic metabolic processes, and (b) delayed lethal or non-lethal inhibiting effects, which do not curtail basic metabolic processes, but do inhibit other systems such as those responsible for growth and reproduction; the organism is affected in direct proportion to the duration and magnitude of the non-lethal low. Adaptations to immediate lethal effects of temperature are termed resistanceadaptations (Precht, 1958). Acclimation to cold serves as a resistance-adaptation to low temperatures in the case of semiterrestrial crabs of the temperate zone, such as Uca, Pachygrapsus crassipes (Roberts, 1957), and Hemigrapsus oregonensis and H. nudus (Todd and Dehnel, 1960). 468 DON CURTIS MILLER AND F. JOHN VERNBERG Non-lethal effects of an environmental factor have been discussed in detail by F. E. J. Fry (1947). Using fishes as his principal examples, Fry distinguished four ways that a non-lethal factor may influence an organism: masking, directing, controlling, or limiting. According to Precht's terminology, adaptations of temperature-dependent systems to the nonlethal inhibiting effects of low temperature are called capacity-adaptations. Compensation of metabolic rate to low temperatures following acclimation to cold is one capacity-adaptation found in many aquatic poikilotherms of the temperate zone, including those semi-terrestrial brachyurans investigated to date. Various different patterns of compensation to thermal stress occur, not only between species, but also intraspecifically. Variations within a species may include differences between ontogenetic stages as well as between populations, and may often be correlated with the temperatures of the specific habitats involved. Vernberg (1959) observed a correlation between patterns of the metabolism/temperature curves and regional thermal regimes in studies on U. pugnax from North Carolina and Alligator Harbor, Florida, and U. rapax from Jamaica. The Alligator Harbor population, which experiences high summer temperatures and cold winter conditions, proved to be intermediate in its metabolic response after acclimation. Cold-acclimated crabs compensated like the U. pugnax from North Carolina, but when warm-acclimated they behaved like U. rapax from Jamaica. An obvious conclusion is that the specific pattern of the compensatory adaptation to changes in temperature is the result of selection by the local thermal regime. There are some problems of non-lethal inhibition by low temperature for which no adaptation appears to have evolved in Uca from the temperate zone. Present evidence suggests that the minimal temperature required for molting may be similar in crabs from the temperate and tropical zones. Preliminary experiments on low- temperature inhibition of locomotory activity suggest that species of the temperate zone have not developed a capacityadaptation to resolve this problem. With summer animals acclimated to 18°C for one week, locomotory inhibition occurred between 11 and 12°C in the three species of the temperate zone, and between 13 and 14°C in U. rapax and U. thayeri. Broader comparative studies involving additional temperature-dependent systems must be undertaken before a meaningful generalization can be developed with regards to capacity-adaptations in semiterrestrial Crustacea. Some relevant biological systems include those involved with growth, metamorphosis of larval stages, and gametogenesis. If it were true that a semi-terrestrial group of the temperate zone, such as Uca, had not evolved many capacity-adaptations to low temperature, one would expect them still to require seasonal periods of tropical-like temperatures in order to carry out certain life processes. The tropical zone is characterized as having daily minimal air temperatures above 18 to 20°C. The following air temperatures, which have primary influence on the thermal regime of the estuarine intertidal zone, serve to illustrate similar summer and differing winter conditions. Consulting U. S. Weather Bureau data for 1961 from Morehead City, North Carolina, and Magueyes Island, Puerto Rico, we find the ranges for the warmest week were 23.5-32°C at Puerto Rico, and 23-32°C at North Carolina. The ranges for the coldest week were 20-28° for Puerto Rico and —3 to 5.5° in North Carolina. These ranges represent the averaged daily minimum and maximum temperatures observed during a calendar week. At Beaufort, North Carolina, the "tropical season" (with temperatures continually above 18°) occurs from early June to midSeptember. The duration and intensity of the "tropical season" diminish proportionately with increasing latitude, and so does the number of terrestrial and semiterrestrial crabs found along the coast. THERMAL REQUIREMENTS OF FIDDLER CRABS Sesarma cinereum is found only as far north as Chesapeake Bay, and Ocypode quadrata is rare east of New Jersey, although adults have been reported as far north as Block Island, Rhode Island (Rathbun, 1918). 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