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First published online June 15, 2006
Journal of Experimental Biology 209, 2486-2494 (2006)
Published by The Company of Biologists 2006
doi: 10.1242/jeb.02280
Water vapour absorption in the penicillate millipede Polyxenus lagurus (Diplopoda: Penicillata: Polyxenida): microcalorimetric analysis of uptake kinetics
1 Department of Biology, 609 North College Avenue, Pomona College,
Claremont, CA 91711, USA
2 Department of Life Sciences and Chemistry, Roskilde University, DK-4000
Roskilde, Denmark
* Author for correspondence (e-mail: jcwright{at}pomona.edu)
Accepted 19 April 2006
| Summary |
|---|
|
|
|---|
86% RH. Owing to very
small and opposing heat fluxes from metabolism and passive water loss, the
measured flux provided a good measure of water uptake. WVA showed an uptake
threshold of 85% RH and linear sorption kinetics until >94% RH, when uptake
became asymptotic. Uptake was rapid, and would allow recovery from 20%
dehydration (by mass) in little over 5 h. The uptake flux scales
mass0.61, suggesting an area-limited mechanism. Polyxenus
possesses a cryptonephric system, analogous to that of tenebrionid beetle
larvae. Measurements of water absorption and desorption from faecal pellets
voided in different humidities gave an estimated rectal humidity of 85.5%. The
close congruence between this value and the WVA threshold provides evidence
for a cryptonephric uptake mechanism derived independently from that of
tenebrionids. Polyxenus represents the first documented example of
WVA in the myriapod classes.
Key words: water vapour absorption (WVA), Polyxenus lagurus, heat flux, calorimetry
| Introduction |
|---|
|
|
|---|
Although WVA has been documented for only a rather small number of
arthropod species their taxonomic diversity, combined with clear physiological
differences among the uptake mechanisms
(Hadley, 1994
), clearly shows
that it has evolved independently several times. Examples among the Insecta
include tenebrionid and anobiid beetle larvae
(Ramsay, 1964
;
Knülle and Spadafora,
1970
; Machin,
1975
; Machin,
1976
; Serdyukova,
1989
), flea larvae (Siphonaptera)
(Rudolph and Knülle,
1982
; Bernotat-Danielowski and
Knülle, 1986
), Psocoptera and Phthiraptera
(Rudolph, 1982
;
Rudolph, 1983
), desert
burrowing cockroaches Arenivaga spp.
(Edney, 1966
;
O'Donnell, 1977
;
O'Donnell, 1981a
;
O'Donnell, 1981b
;
O'Donnell, 1982a
;
O'Donnell, 1982b
), and
Thysanura (Noble-Nesbitt,
1969
; Noble-Nesbitt,
1970a
; Noble-Nesbitt,
1970b
; Noble-Nesbitt,
1975
; Neuhaus et al.,
1978
; Gaede,
1989
). WVA is also described in the Acari among the Chelicerata
(Lees, 1946
;
Rudolph and Knülle, 1974
;
Rudolph and Knülle, 1978
;
Arlian and Veselica, 1981
;
Knülle and Rudolph, 1983
;
Kraiss-Gothe et al., 1989
;
Sigal et al., 1991
;
Gaede and Knülle, 1997
;
Gaede and Knülle, 2000
;
Yoder and Benoit, 2003
), and
in the oniscidean isopods among the Crustacea
(Wright and Machin, 1990
;
Wright and Machin, 1993a
;
Wright and Machin, 1994b; Wright and
O'Donnell, 1992
). A capacity for WVA has not been described in the
non-acarine arachnids or in any of the myriapod classes.
Polyxenus lagurus (L. 1758) is the most common European millipede
in the aberrant basal subclass Penicillata Latreille 1831 (formerly
Pselaphognatha). This taxon comprises a single order Polyxenida Verhoeff 1934,
with a worldwide distribution and 160 described species
(Nguyen Duy-Jacquemin and Geoffroy,
2003
). Most of these belong to the family Polyxenidae and the
cosmopolitan genus Polyxenus. Like congenerics, Polyxenus
lagurus is minute, measuring 34 mm in length, and the body is
covered with fans of strongly sculpted trichomes
(Eisenbeis and Wichard, 1987
).
Caudally, Polyxenus spp. bear two dense brushes of long, detachable
spines with recurved tips that are released if the animal is attacked. They
form a remarkably effective defence mechanism, hooking onto the setae of ants
and spiders and then hooking into one another as the assailant attempts to
groom (Eisner et al., 1996
).
In a short period, the animal is entangled and helpless.
Polyxenus spp. are mesicxeric in habit, contrasting
markedly with most other Diplopoda. Their typical habitats are generally
described as litter and bark
(Schömann, 1956
;
Seifert, 1960
;
Eisenbeis and Wichard, 1987
;
David, 1995
), although the
present authors have most commonly collected P. lagurus from rocks
and old walls. They are diurnally active, feeding on algal films and lichens
(Schömann, 1956
;
Eisenbeis and Wichard, 1987
),
often in warm and dry conditions and direct sunlight. While most millipedes
have high integumental permeability, with standardized fluxes in the range of
0.12.5 µg h1 cm2
Pa1 (Appel,
1988
; Hopkin and Read,
1992
; Meyer and Eisenbeis,
1985
), P. lagurus is remarkably impermeable, with an
integumental conductance comparable to that of the most xeric insects.
Eisenbeis and Wichard (Eisenbeis and
Wichard, 1987
) measured losses for P. lagurus of about
0.012 µg h1 cm2 Pa1
in relative humidities of 0 and 33% RH, similar to the permeability of
Tenebrio molitor (L.) pupae
(Holdgate and Seal, 1956
) and
to values described for most mesicxeric arachnids (see
Hadley, 1994
). Even the large
desert millipede Orthoporus ornatus (Girard) has a permeability about
5 times greater (0.06 µg h1 cm2
Pa1) (Crawford,
1972
) than that of P. lagurus.
In spite of its low water-loss rates, the small size of P. lagurus
will impose whole-animal conductances or mass-specific water loss rates far
greater than those experienced by larger mesicxeric arthropods in the
100 mg to 10 g size range. Maintenance of long-term water balance in this
species will consequently require an effective avenue of water uptake. This is
made all the more critical by the ability of rock-encrusting lichens and algae
to withstand near-complete water losses
(Beckett, 1995
;
Kranner et al., 2003
),
reducing or eliminating the availability of pre-formed water to the epilithic
arthropod fauna during periods of drought. Whether P. lagurus depends
primarily on the existing water in food, dew, metabolic water or WVA is
unknown. The ability of P. lagurus to rehydrate rapidly in 98% RH has
been reported (Eisenbeis and Wichard,
1987
). Although they did not clarify whether liquid water might
have been available, or whether an active process was involved, Eisenbeis and
Wichard concluded that this represented water vapour uptake. To explore the
possibility that P. lagurus is able to absorb water vapour from
sub-haemolymph water activities, we used microcalorimetry to monitor water
exchange of this species in flowing air at precisely controlled relative
humidities. This method has been used with success in the study of WVA in
Tenebrio larvae (Hansen et al.,
2004
) and provides superior sensitivity to gravimetric
procedures.
| Materials and methods |
|---|
|
|
|---|
Calorimetric measurements used an isothermal Thermal Activity Monitor (TAM)
2277 (Thermometric, Järfälla, Sweden). All experiments were run with
individual animals using an air-flow rate of 100 ml h1 and
temperature of 25°C. Thermistors connecting to the animal cell (Cell 1)
recorded the total heat flux due to metabolism and water exchange. Full
details are given elsewhere (Hansen et
al., 2004
). In a subset of trials, the air-stream from Cell 1 was
passed into a second calorimeter cell containing 700 µl water. The humidity
of the air-stream exiting Cell 1 determines the amount of water that must be
evaporated to saturate the air exiting Cell 2, and hence the endothermic heat
signal in the second channel, provided that the air stream reaches saturation
during the passage. The latter was confirmed in controls with saturated
solutions of, respectively, NaCl (aw=0.753) and KNO3
(aw=0.936) (Greenspan,
1977
) in Cell 1 and in trials with variable air flow rates. These
control experiments concurrently suggested that a possible error due to a
vapour pressure deficit in the air leaving Cell 2 was small compared to other
experimental limitations. The heat signal from Cell 2 (µW) thus allows an
accurate determination of the equilibrium humidity in Cell 1. The vapour
density of this air stream (g l1) is readily calculated
knowing the latent heat of vapourization of water at 25°C (2443 J
g1) (Atkins and de Paula,
2002
):
![]() |
This value will be primarily determined by the RH of the initial air
stream, but also by the addition or removal of water vapour from Cell 1 by the
animal. By subtracting the heat signal measured in Cell 2 from a blank using
an empty cell, the net humidity change (%) resulting from the animal is
calculated. In order to convert a deviation in the measured signal (µW)
into a measure of water exchange, the integration of the signal over time is
simply divided by the latent heat of vapourization of water at 25°C:
![]() |
![]() |
Preliminary calorimetric runs showed two distinct features. First, the baseline-corrected heat signal in humidities between 70% and 85% was extremely small and negative, in the order of 0.20.4 µW. Second, a much larger negative signal indicating water vapour absorption was routinely seen in relative humidities above 86%. To study the sorption kinetics, we used a protocol starting at 84% and then increasing the humidity stepwise by increments of 2% every 4 h. Owing to the increasing equilibration times imposed by adsorption and desorption of water from the calorimetric cell at the highest humidities, experimental runs were not extended above 96% RH. In order to differentiate the positive (endothermic) water loss and negative (exothermic) metabolism components of the signal in non-absorbing animals, we also recorded the metabolic heat signal independently using hydrated animals in still air at 100% RH. This was done by loading an animal into the calorimetric cell and adding 2 small (ca. 1 µl) water droplets to the vertical sides of the cell to saturate the humidity. The cell was then sealed and lowered into the TAM 2277. The heat signal equilibrated within 1 h. The disparity between this signal and the signal in flowing air at sub-saturated humidities represents the humidity-dependent contribution of evaporative heat flux to the net signal. We were also able to estimate this value independently using the permeability calculated from the initial desiccation of animals in 0% RH.
| Results |
|---|
|
|
|---|
16 h) a sharp decrease signifies the
onset of WVA. Analogously, the black curve shows onset of WVA at
t
7 h (RH=86%) which ceases at t
18 h when RH has
reached 92%. Animals were sometimes observed to terminate WVA, only to start
again within a few hours, showing that both the initiation and termination of
WVA are clearly under voluntary control.
|
In principle, the baseline-corrected heat signal in non-absorbing animals represents the sum of the exothermic heat flux due to metabolism (HFmet) and the endothermic flux due to net (transpiratory and respiratory) water losses (HFwl). In 84% RH, the net signal (HFmet+HFwl), estimated for 10 non-absorbing animals, was about 0.20.4 µW, which is comparable to the detection level in perfusion experiments. The net value for inactive animals is only about 5% of HFWVA in 88% RH, and about 1% of the signal in 94%. We conclude that the accordance of the numeric values of HFWVA in Cell 1 and Cell 2 and the insignificant size of the sum (HFmet+HFwl) collectively suggest that the rate of WVA is reflected directly in HFWVA taken from Cell 1. Since the measurements in Cell 2 are more experimentally demanding, and have lower resolution due to the large background (cf. Fig. 1B), we base the following analyses on HFWVA values from Cell 1.
In humidities between 86% and 92%, HFWVA measured in Cell 1 was typically very uniform throughout the duration of WVA. By contrast, in 94% and 96% RH the signal showed a small asymptotic increase, typically stabilizing within 34 h at a value 1020% above the initial reading. This can be attributed to the depletion of the chamber RH by WVA, which in turn lowers the rate of WVA until steady-state equilibrium is attained. Since the amount of water removed from the air stream by the animal is quantified by HFWVA, the steady-state humidity in the chamber can be readily calculated by mass conservation considerations. Thus, the height of the steps in Fig. 1B shows that a change in RH of one unit corresponds to a heat flow of 16 µW (the same number can be derived theoretically from the equations in the Materials and methods section). It follows that the ambient humidity at steady-state WVA, RHss, can be written RHss=RHHFWVA/16. Applying this latter equation to our data shows that the reduction in ambient humidity due to WVA ranges from 0.1% RH for the lower to 0.7% RH for the higher uptake rates.
Mean uptake fluxes (± s.e.m.), expressed both as the negative heat signal (HFWVA; µW) and the calculated water uptake (in µg h1), are plotted as a function of ambient RH in Fig. 2; summary data for WVA are shown in Table 1. The humidity is specified by the steady-state values, RHss, defined above. Thus, in Fig. 2, each data point represents the average RHss ± s.e.m. for each RH step during WVA. Several animals initiated WVA in 86% RH, but with one exception it terminated again after a short period, possibly because WVA reduced the water activity of the calorimetric cell below the uptake threshold. The sorption curve extrapolates to an estimated uptake threshold of 85% RH (aw=0.85). Because of the extremely low passive loss at this humidity, the disparity between the threshold activity and CEA is negligible. The sorption curve shows an asymptotic profile with the uptake flux saturating as the humidity increases above 94%. Below this humidity, the sorption curve is linear with a slope of 1.94 µg h1 RH1. Standardized uptake fluxes in Table 1 are calculated using the linear portion of the sorption curve and express uptake as a function of the vapour pressure gradient between the ambient RH and the threshold (85%). The corresponding vapour pressure gradient was calculated assuming a saturation vapour pressure at 25°C of 3169 Pa; thus 1% RH represents 31.69 Pa.
|
|
The data shown in Fig. 2 are
not standardized for animal mass, so variation in uptake flux and/or uptake
threshold as a function of size will contribute variability to the data.
Animal masses for our trials varied approximately twofold, from 0.35 to 0.72
mg. In order to analyze the effects of body mass on uptake flux, the uptake
fluxes measured in different RH conditions were standardized for the vapour
pressure gradient between the uptake site and ambient air (µg
h1 Pa1), using the calculated threshold
activity of 0.85. A loglog comparison of standardized uptake flux
against body mass then permits the calculation of intraspecific scaling
parameters for WVA in Polyxenus (see
Wright and Machin, 1993a
). The
resulting least-squares regression generates a slope of 0.605±0.144
(± s.e.m.) (r2=0.33; N=38), thus
indicating that standardized uptake flux scales in proportion to body mass
(Mb)0.605. This is considered further in the
Discussion.
The metabolic heat flux measured for test animals in closed calorimetric cells at 100% RH had a mean value of 0.35±0.22 µW (N=4), which was not significantly different from zero. In subsaturated humidities, evaporative heat flux (HFwl) will also contribute to the net heat flow measured. This can be estimated for a given humidity based on the gravimetrically determined water loss rates of whole animals, shown in Table 2. These data give an estimated mean water loss for a 0.45 mg animal in 84% RH of 0.22 µg h1. Multiplying this value by the latent heat of evaporation of water (see above) gives an HFwl value of 0.15 µW. The negligible contribution of both metabolic heat flux and HFwl to the net measured heat signal, combined with the fact that they represent opposing heat signals, confirms the validity of quantifying WVA directly from the data in Cell 1.
|
As discussed above, the water recovery measured directly in Cell 2
generates the same (numerical) heat flow as the HFWVA observed in
Cell 1 during WVA. This shows that a possible increase in metabolic heat
output, HFmet, during WVA is below the experimental resolution in
Cell 2, which is about 1 µW. This resolution corresponds to about a
threefold increase above the standard metabolic rate (SMR). It is likely that
the actual increase in HFmet during WVA is considerably smaller,
based on measurements for Tenebrio molitor
(Hansen et al., 2006
) and the
low energetic cost of WVA predicted from the Gibbs equation
(Lees, 1948
;
Ramsay, 1964
;
Edney, 1977
;
O'Donnell and Machin, 1988
).
The very low metabolic cost of WVA, compared to the large HFWVA,
does not represent a violation of fundamental laws of thermodynamics since the
HFWVA is due to the latent heat of condensation. If water was
moving down an activity gradient solely in the liquid phase, the heat released
would be smaller than the metabolic heat consumed in generating that gradient,
in accordance with the 2nd law of thermodynamics.
| Discussion |
|---|
|
|
|---|
Water vapour uptake is rapid, plateauing at approximately 17 µg
h1 in 96% RH for a 0.45 mg animal. The linear portion of the
sorption curve between 86% and 92% RH represents a standardized uptake flux of
0.061 µg h1 Pa1. This is quite close to
the value of 0.104 µg h1 Pa1 estimated
for a 0.45 mg animal using the following allometric equation for a range of
vapour-absorbing arthropods:
![]() |
The exponent for interspecific scaling of standardized uptake flux is close
to the value of 0.67 that would be predicted for geometric scaling if uptake
flux were area-limited. Intraspecific scaling of standardized uptake flux has
only been studied in the larvae of the tenebrionid beetles Tenebrio
molitor and Onymacris marginipennis (Breme)
(Coutchié and Machin,
1984
), with both species showing similar exponents (0.355 and
0.418, respectively), lower than our estimate for Polyxenus. However,
measurements of rectal length and circumference for both species show a
strongly allometric scaling of rectal surface area with mass, and the
calculated exponents (0.370 and 0.379) provide a reasonable match to the
scaling of uptake flux, again indicating an area-limited process. The
intraspecific scaling of uptake flux against body mass in Polyxenus,
determined from the present study, has an exponent of 0.605±0.144.
Although the modest sample size and small mass range of the animals limits the
precision of this estimate, it indicates that uptake flux in
Polyxenus conforms to the predicted geometric scaling for an
area-dependent function, as seen for interspecific scaling.
The most physiologically and ecologically significant consequence of the
0.692 exponent for interspecific scaling of WVA is that mass-specific uptake
fluxes decrease in larger species. In small arthropods, WVA provides very
effective mass-specific water recovery
(O'Donnell and Machin, 1988
).
Our calculated uptake rates for P. lagurus would allow replenishment
of 3.7% mass loss per hour, or 20% in 5.4 h, by a representative 0.45 mg
animal in µ94% RH. Combined with the remarkably low integumental
permeability, measured here as 7.2±1.3 ng h1
cm2 Pa1, this renders the species
extremely well adapted to the highly exposed and frequently xeric microclimate
of bark and rock surfaces.
The site and mechanism of WVA in P. lagurus are not known, but the
structure of the rectum indicates a likely absorption site and colligative
process. Like the tenebrionid beetles, this species possesses a cryptonephric
system (Schlüter and Seifert,
1985
). The medial region of the 2 Malpighian tubules forms a
`thick meandering segment', lying closely apposed to the rectal wall and
ensheathed by a perinephric membrane. The cryotonephric system is well
established as the site for WVA in Tenebrio
(Ramsay, 1964
;
Machin, 1979a
;
Machin, 1979b
;
Tupy and Machin, 1985
). In
such a system, the presence of an osmotically impermeable perinephric
membrane, combined with the generation of high osmolalities within the tubule
lumina, provides a mechanism for the unidirectional movement of water from the
rectal lumen into the perinephric space surrounding the tubules
(Grimstone et al., 1968
). In
both Polyxenus and the tenebrionids, such a system likely evolved for
purposes of dehydrating the faeces, and by generating depressed water
activities it was elegantly pre-adapted for WVA. There are, to our knowledge,
no anatomical studies on hindgut structure in other Polyxenida to indicate
whether a cryptonephric system is present in other genera. The remaining
millipede orders apparently lack this specialization, with the Malpighian
tubules lying free in the haemolymph
(Seifert, 1979
;
Hopkin and Read, 1992
).
Physiological studies on specific ion concentrations and water activities
generated by the Malpighian tubules in Polyxenus have not been done,
but Glomeris marginata tubules transport sodium, not potassium, as
the primary cation driving fluid transport
(Farquharson, 1974
). This is
potentially significant since the saturation water activity for potassium
chloride is 0.85 (Winston and Bates,
1960
), making potassium a potentially problematic primary cation
for a species with an uptake threshold of 0.85. Machin and O'Donnell, however
(Machin and O'Donnell, 1991
),
showed that Onymacris marginipennis, with a WVA threshold of 0.841
(Coutchié and Machin,
1984
), still transports potassium as the primary cation in the
cryptonephric portion of the Malpighian tubules. Measured potassium
concentrations in the tubule lumina in vitro reached 3350 mmol
l1, sufficient to generate a water activity of 0.89 when
combined with peak measured concentrations for Na+ and
Cl. In view of some osmotic dilution of the preparation from
bathing saline in the rectal lumen, a space that is naturally air-filled, the
authors determined that the active accumulation of KCl by the cryptonephric
tubules probably generates lower activities, consistent with the WVA
threshold, in vivo. Since the measured threshold activity of 0.841 is
below the saturation activity for KCl, they concluded that KCl supersaturation
occurs in the tubule lumina. In view of the slightly higher threshold activity
determined here for Polyxenus, we might therefore reasonably expect
either K+ or Na+ to be the major cation transported by
the Malpighian tubules.
Corroborative evidence for a rectal uptake site was sought by examining
water exchanges from faecal pellets in hydrated animals. The amount of water
absorbed or evaporated from voided faecal pellets in different humidities
provides a sensitive means of determining the rectal water activity
(Wright and Machin, 1993b
).
Calorimetric runs examining water exchanges from faecal pellets were conducted
with fifteen freshly collected Polyxenus using various protocols
ranging from 0 to 96% RH. The amount of water that must be evaporated or
condensed to bring the faecal pellet into equilibrium with a given RH will
increase as the ambient water activity deviates further from the faecal pellet
(rectal) activity. The mass of water exchanged varies linearly with the
reciprocal of the water activity deficit or vapour pressure deficit
(Machin, 1975
;
Machin, 1979a
;
Machin, 1979b
).
Heat fluxes during the release of faecal pellets in relative humidities below 84% were easily distinguished as sharp endothermic spikes, lasting about 10 min in duration. Similar endothermic spikes were not seen in any higher humidity. Nine clear exothermic spikes were seen in non-absorbing animals in 88% and 90% RH, but were not reliably distinguishable in higher humidities, mainly because most animals initiated WVA and this made their identity ambiguous. One clear peak in 92% RH almost certainly arose from the water desorption from more than one voided pellet, based on its duration, and was excluded owing to this uncertainty. The integrated heat signal for each pellet was used to calculate the mass of water exchanged as described before. The results for all pellets are plotted in Fig. 3. Although variation in faecal pellet size will add variance to the data, the equilibrium vapour pressure deficit where no net water exchange occurs is independent of pellet size and well defined in the figure at 1/0.00218, equivalent to a water activity of 0.855. This indicates that the cryptonephric system functions to depress the rectal water activity to conserve water from the faeces, and the congruence of the activity values determined from faecal water exchange and the WVA sorption curve provides good experimental support for a rectal uptake site for WVA. This conclusion is further supported by the fact that faecal pellet spikes were not reliably distinguishable in the near-threshold humidities (84% and 86% RH), and were not resolved for some animals that nevertheless released faecal pellets into the calorimetric cell. If low rectal water activities are maintained for faecal dehydration, the initiation of WVA in above-threshold humidity would simply entail opening of the anal valves. This is consistent with the voluntary control over the onset and termination of WVA, and the simultaneous abrupt changes in water flux.
|
| List of symbols and abbreviations |
|---|
|
|
|---|
| Acknowledgments |
|---|
| References |
|---|
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|
|---|
Appel, A. G. (1988). Water relations and desiccation tolerance of migrating garden millipedes (Diplopoda: Paradoxsomatidae). Environ. Entomol. 17,463 -466.
Arlian, L. G. and Veselica, M. M. (1981). Effect of temperature on the equilibrium body water mass in the mite Dermatophagoides farinae. Physiol. Zool. 54,393 -399.[CrossRef]
Atkins, P. W. and de Paula, J. (2002). Atkins Physical Chemistry (7th edn). Oxford: Oxford University Press.
Beckett, R. P. (1995). Some aspects of the
water relations of lichens from habitats of contrasting water status studied
using thermocouple psychrometry. Ann. Bot.
76,211
-217.
Bernotat-Danielowski, S. and Knülle, W. (1986). Ultrastructure of the rectal sac, the site of water vapour uptake from the atmosphere in larvae of the oriental rat flea Xenopsylla cheopsis. Tissue Cell 18,437 -455.
Coutchié, P. A. and Machin, J. (1984). Allometry of water vapor absorption in two species of tenebrionid beetle laevae. Am. J. Physiol. 247,230 -236.
Crawford, C. S. (1972). Water relations in a desert millipede Orthoporus ornatus (Girard) (Spirostreptidae). Comp. Biochem. Physiol. 42A,521 -535.[CrossRef][Medline]
David, J.-F. (1995). Seasonal abundance of millipedes in a mediterranean oak forest (Southern France). Isr. J. Zool. 41,23 -31.[Medline]
Edney, E. B. (1966). Absorption of water vapour from unsaturated air by Arenivaga sp. (Polyphagidae, Dictyoptera). Comp. Biochem. Physiol. 19,387 -408.[CrossRef]
Edney, E. B. (1977). Water Balance in Land Arthropods. Berlin: Springer-Verlag.
Eisenbeis, G. and Wichard, W. (1987). Atlas on the Biology of Soil Arthropods. Berlin: Springer-Verlag.
Eisner, T., Eisner, M. and Deyrup, M. (1996).
Defense mechanisms of arthropods. I42. Millipede defense: use of detachable
bristles to entangle ants. Proc. Natl. Acad. Sci. USA
93,10848
-10851.
Enghoff, H. (1976). Morphological comparison of bisexual and parthenogenetic Polyxenus lagurus (Diplopoda: Polyxenida) in Denmark and Southern Sweden with notes on taxonomy, distribution and ecology. Entomol. Meddeldser 44,161 -182.
Farquharson, P. A. (1974). A study of the
Malpighian tubules of the millipede Glomeris marginata (Villers). II.
The effect of variations in osmotic pressure and sodium and potassium
concentrations on fluid production. J. Exp. Biol.
60, 29-39.
Gaede, K. (1989). Vergleichende untersuchungen zur wasserdampfsorptionsfähigkeit bei insekten und milben unter besonderer berüchsichtigung der merostigmata. PhD thesis, Free University of Berlin, Germany.
Gaede, K. (1991). Aktive aufnahme von wasserdampf aus ungesättigter atmosphäre bei arthropoden: sorptionkinetiken. Zool. Jahrb. Abt. Allg. Zool. Physiol. Tierre 95,135 -171.[Medline]
Gaede, K. and Knülle, W. (1997). On the mechanism of water vapour sorption from unsaturated atmospheres by ticks. J. Exp. Biol. 200,1491 -1498.[Abstract]
Gaede, K. and Knülle, W. (2000). Absorption of water vapour from unsaturated atmosphere and its ecological significance in mesostigmatic mites. Entomol. Exp. Appl. 94,111 -121.[CrossRef]
Greenspan, L. (1977). Humidity fixed points of binary saturated aqueous solutions. J. Res. Nat. Bur. Stand. Sect. A 81,89 -96.
Grimstone, A. V., Mullinger, A. M. and Ramsay, J. A. (1968). Further studies on the rectal complex of the mealworm Tenebrio molitor, L. (Coleoptera, Tenebrionidae). Philos. Trans. R. Soc. Lond. B Biol. Sci. 253,334 -382.
Hadley, N. F. (1994). Water Relation of Terrestrial Arthropods. San Diego: Academic Press.
Hansen, L. L., Ramlov, H. and Westh, P. (2004).
Metabolic activity and water vapour absorption in the mealworm Tenebrio
molitor L. (Coleoptera, Tenebrionidae): real-time measurements by
two-channel microcalorimetry. J. Exp. Biol.
207,545
-552.
Hansen, L. L., Westh, P., Wright, J. C. and Ramlov, H. (2006). Simultaneous and real-time measurements of metabolic activity, water exchange, and CO2 production rate (VCO2) in the mealworm Tenebrio molitor L (Coleoptera, Tenebrionidae). J. Insect Physiol. 52,291 -299.[Medline]
Holdgate, M. W. and Seal, M. (1956). The epicuticular wax layers of the pupa of Tenebrio molitor L. J. Exp. Biol. 33,82 -106.[Abstract]
Hopkin, S. P. and Read, H. J. (1992). The Biology of Millipedes. Oxford: Oxford University Press.
Knülle, W. (1984). Water uptake in mites and insects: an ecophysiological and evolutionary perspective. Acarology 6,71 -82.
Knülle, W. and Rudolph, D. (1983). Humidity relationships and water balance of ticks. In Physiology of Ticks (ed. F. D. Obenchain and R. Galun). pp.433 -470. Oxford: Pergamon Press.
Knülle, W. and Spadafora, R. R. (1970). Occurrence of water vapour sorption from the atmosphere in larvae of some stored-product beetles. J. Econ. Entomol. 63,1069 -1070.
Knülle, W. and Wharton, G. W. (1964). Equilibrium humidities in arthropods and their ecological significance. Acarologia 6,299 -306.
Kraiss-Gothe, A., Kalvelage, H. and Gothe, R. (1989). Inverstigation into the critical equilibrium humidity, active atmospheric water absorption and water content of Rhipicephalus evertsi mimeticus. Exp. Appl. Acarol. 7, 131-141.[Medline]
Kranner, I., Zorn, M., Tuck, B., Wornick, J., Beckett, R. P. and Batik, F. (2003). Biochemical traits of lichens differing in relative desiccation tolerance. New Phytol. 160,167 -176.[CrossRef]
Lees, A. D. (1946). Water balance in Ixodes ricinus L. and certain other species of ticks. Parasitology 37,1 -20.
Lees, A. D. (1948). Passive and active water
exchange through the cuticle of ticks. Discuss. Faraday
Soc. 3,187
-192.
Machin, J. (1975). Water balance in Tenebrio molitor, L. larvae; the effect of atmospheric water absorption. J. Comp. Physiol. B 101,121 -132.[Medline]
Machin, J. (1976). Passive exchanges during
water vapour absorption in mealworms (Tenebrio molitor): a new
approach to studying the phenomenon. J. Exp. Biol.
65,603
-615.
Machin, J. (1979a). Atmosphereric water absorption in arthropods. Adv. Insect Physiol. 14, 1-48.
Machin, J. (1979b). Compartmental osmotic
pressures in the rectal complex of Tenebrio larvae: evidence for a
single tubular pumping site. J. Exp. Biol.
82,123
-137.
Machin, J. (1983). Water vapour absorption in
insects. Am. J. Physiol.
244,R187
-R192.
Machin, J. and O'Donnell, M. J. (1991). Rectal complex ion activities and electrochemical gradients in larvae of the desert beetle, Onymacris: comparisons with Tenebrio. J. Insect Physiol. 37,829 -838.[Medline]
Machin, J., O'Donnell, M. J. and Coutchié, P. A. (1982). Mechanisms of water vapor absorption in insects. J. Exp. Zool. 222,309 -320.[CrossRef]
Meyer, E. and Eisenbeis, G. (1985). Water relations in millipedes from some Alpine habitat types (Central Alps, Tyrol) (Diplopoda). Bijdr. Dierkunde 55,131 -142.
Neuhaus, G., Siebler, H. and Thurm, U. (1978). Ein zur aufnahm atmosphärischen wassers befähigtes organ (Analsak von Lepisma). Verh. Dtsch. Zool. Ges. 71, 295.
Nguyen Duy-Jacquemin, M. and Geoffroy, J.-J. (2003). A revised comprehensive checklist, relational database, and taxonomic system of reference for the bristly millipedes of the world (Diplopoda, Polyxenida). Afr. Invertebr. 44, 89-101.
Noble-Nesbitt, J. (1969). Water balance in the
firebrat Thermobia domestica (Packard). Exchanges of water with the
atmosphere. J. Exp. Biol.
50,745
-769.
Noble-Nesbitt, J. (1970a). Water uptake from subsaturated atmospheres: Its site in insects. Nature 225,753 -754.[Medline]
Noble-Nesbitt, J. (1970b). Water exchanges in
the firebrat Thermobia domestica (Packard). The site of uptake of
water from the atmosphere. J. Exp. Biol.
52,193
-200.
Noble-Nesbitt, J. (1975). Reversible arrest of
uptake of water from subsaturated atmospheres by the firebrat Thermobia
domestica (Packard). J. Exp. Biol.
62,657
-669.
O'Donnell, M. J. (1977). Site of water vapor
absorption in the desert cockroach Arenivaga investigata. Proc.
Natl. Acad. Sci. USA 74,1757
-1760.
O'Donnell, M. J. (1981a). Fluid movements during water vapour absorption by the desert burrowing cockroach Arenivaga investigata. J. Insect Physiol. 27,877 -887.[CrossRef][Medline]
O'Donnell, M. J. (1981b). Frontal bodies: novel structures involved in water vapour absorption by the desert burrowing cockroach, Arenivaga investigata. Tissue Cell 13,541 -555.[Medline]
O'Donnell, M. J. (1982a). Water vapour
absorption by the desert burrowing cockroach: evidence against a
solute-dependent mechanism. J. Exp. Biol.
96,251
-262.
O'Donnell, M. J. (1982b). Hydrophilic cuticle:
the basis for water vapour absorption by the desert burrowing cockroach,
Arenivaga investigata. J. Exp. Biol.
99, 43-60.
O'Donnell, M. J. and Machin, J. (1988). Water vapor absorption in terrestrial organisms. In Advances in Comparative and Environmental Physiology. Vol.2 (ed. R. Gilles), pp 47-107. Berlin: Springer Verlag.
O'Donnell, M. J. and Machin, J. (1991). Ion
activities and electrochemical gradients in the mealworm rectal complex.
J. Exp. Biol. 155,375
-402.
Ramsay, J. A. (1964). The rectal complex of the mealworm Tenebrio molitor, L (Coleoptera, Tenebrionidae). Philos. Trans. R. Soc. Lond. A 248,280 -313.
Rudolph, D. (1982). Occurrence, properties and biological implications of the active uptake of water vapour from the atmosphere in Psocoptera. J. Insect Physiol. 28,111 -121.
Rudolph, D. (1983). The water vapour uptake system of the Phthiraptera. J. Insect Physiol. 29, 15-25.
Rudolph, D. and Knülle, W. (1974). Site and mechanism of water vapour uptake from the atmosphere in ixodid ticks. Nature 249,84 .[Medline]
Rudolph, D. and Knülle, W. (1978). Uptake of water vapour from the air: process, site and mechanism in ticks. In Comparative Physiology: Water, Ions and Fluid Mechanics (ed. K. Schmidt-Nielsen, L. Bolis and S. H. P. Maddrell), pp. 97-113. Cambridge: Cambridge University Press.
Rudolph, D. and Knülle, W. (1982). Novel uptake systems for atmospheric water among insects. J. Exp. Zool. 222,321 -333.[CrossRef]
Schlüter, U. and Seifert, G. (1985). Functional morphology of the hindgut-Malpighian tubule-complex in Polyxenus lagurus (Diplopoda; Penicillata). Bijdr. Dierkunde 55,209 -218.
Schömann, K. (1956). Zur biologie von Polyxenus lagurus (L. 1758). Zool. Jahrb. Syst. 84,195 -256.
Seifert, G. (1960). Die entwicklung von Polyxenus lagurus L. (Diplopoda: Pselaphognatha). Zool. Jahrb. Anat. 78,257 -312.[Medline]
Seifert, G. (1979). Considerations about the evolution of excretory organs in terretrial arthropods. In Myriapod Biology (ed. M. Camatini), pp. 353-372. London: Academic Press.
Serdyukova, I. R. (1989). Water vapour absorption in Anobiidae larvae (Coleoptera). Zool. Jahrb. 68,65 -70.
Sigal, M. D., Machin, J. and Needham, G. R.
(1991). Hyperosmotic oral fluid secretion during active water
vapour absorption and during desiccation-induced storage excretion by the
unfed female tick Amblyomma americanum. J. Exp. Biol.
157,585
-591.
Tupy, J. H. and Machin, J. (1985). Transport characteristics of the isolated rectal complex of the mealworm Tenebrio molitor. Can. J. Zool. 63,1897 -1903.
Wharton, G. W. and Devine, T. L. (1968). Exchange of water between a mite, Laelaps echidnina, and the surrounding vapor under equilibrium conditions. J. Insect Physiol. 14,1303 -1318.[Medline]
Winston, P. W. and Bates, D. H. (1960). Saturated solutions for the control of humidity in biological research. Ecology 41,232 -237.[CrossRef]
Wright, J. C. and Machin, J. (1990). Water
vapour absorption in terrestrial isopods. J. Exp.
Biol. 154,13
-30.
Wright, J. C. and Machin, J. (1993a). Atmospheric water absorption and water budget of terrestrial isopods (Crustacea, Isopoda, Oniscidea). Biol. Bull. 184,243 -253.[Abstract]
Wright, J. C. and Machin, J. (1993b). Energy-dependent water vapor absorption (WVA) in the pleoventral cavity of terrestrial isopods (Crustacea, Isopoda, Oniscidea): evidence for pressure cycling as a supplement to the colligative uptake mechanism. Physiol. Zool. 66,193 -215.
Wright, J. C. and O'Donnell, M. J. (1992).
Osmolality and electrolyte-composition of pleon fluid in Porcellio
scaber (Crustacea, Isopoda, Oniscidea): implications for water-vapor
absorption. J. Exp. Biol.
164,189
-203.
Yoder, J. A. and Benoit, J. B. (2003). Water vapour absorption by nymphal lone star tick Ambystomma americanum (Acari: Ixodidae), and its ecological significance. Int. J. Acarol. 29,259 -264.
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