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Millipedes faced with drought: the life cycle of a Mediterranean population of Ommatoiulus sabulosus (Linnaeus) (Diplopoda, Julida, Julidae)

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Growth, development and life-cycle duration of the millipede Ommatoiulus sabulosus (f. aimatopodus) were studied in a Mediterranean shrubland of southern France and compared with previous data from northwest Europe. Changes in the proportions of stadia during the course of the year were analysed in several generations. The results show that stadia VII and VIII are consistently reached after the first year of growth, and stadia IX and X after the second year. First reproduction may occur at the age of two years in males reaching maturity at stadium X, but not until the age of three in those reaching maturity at stadia XI and XII. Reproduction cannot occur until at least the age of three in females, which carry mature eggs from stadium XI onwards. In comparison with more northern populations, life-cycle duration is not shorter in the Mediterranean population but there are marked differences in its phenology: the breeding period is in autumn, so that juveniles of stadia II to VI are never faced with the summer drought, and larger individuals are mostly inactive in summer; moreover, all individuals moult once every winter. The results illustrate how julid millipedes of humid temperate regions could respond to higher temperatures and drier summer conditions in the context of climate change.
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Millipedes faced with drought: the life cycle of a Mediterranean population... 115
Millipedes faced with drought: the life cycle of a
Mediterranean population of Ommatoiulus sabulosus
(Linnaeus) (Diplopoda, Julida, Julidae)
Jean-François David1, Mathieu Coulis1
1 Centre d’Ecologie Fonctionnelle & Evolutive, UMR 5175, CNRS–Université de Montpellier, 1919 route de
Mende, F–34170 Montpellier cedex 5, France
Corresponding author: Jean-François David (jean-francois.david@cefe.cnrs.fr)
Academic editor: Ivan H. Tuf| Received 27 October 2014| Accepted 4 May 2015| Published 30 June 2015
http://zoobank.org/B7BBC82C-84CB-47C8-BBF4-AD8D8C3C31E9
Citation: David J-F, Coulis M (2015) Millipedes faced with drought: the life cycle of a Mediterranean population of
Ommatoiulus sabulosus (Linnaeus) (Diplopoda, Julida, Julidae). In: Tuf IH, Tajovský K (Eds) Proceedings of the 16th
International
Congress of Myriapodology, Olomouc, Czech Republic. ZooKeys 510: 115–124. doi: 10.3897/zookeys.510.8838
Abstract
Growth, development and life-cycle duration of the millipede Ommatoiulus sabulosus (f. aimatopodus)
were studied in a Mediterranean shrubland of southern France and compared with previous data from
northwest Europe. Changes in the proportions of stadia during the course of the year were analysed in
several generations. e results show that stadia VII and VIII are consistently reached after the rst year
of growth, and stadia IX and X after the second year. First reproduction may occur at the age of two years
in males reaching maturity at stadium X, but not until the age of three in those reaching maturity at sta-
dia XI and XII. Reproduction cannot occur until at least the age of three in females, which carry mature
eggs from stadium XI onwards. In comparison with more northern populations, life-cycle duration is not
shorter in the Mediterranean population but there are marked dierences in its phenology: the breeding
period is in autumn, so that juveniles of stadia II to VI are never faced with the summer drought, and
larger individuals are mostly inactive in summer; moreover, all individuals moult once every winter. e
results illustrate how julid millipedes of humid temperate regions could respond to higher temperatures
and drier summer conditions in the context of climate change.
Keywords
Millipedes, life cycle, phenology, climate change
ZooKeys 510: 115–124 (2015)
doi: 10.3897/zookeys.510.8838
http://zookeys.pensoft.net
Copyright Jean-François David, Mathieu Coulis. This is an open access article distributed under the terms of the Creative Commons Attribution License
(CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
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Jean-François David & Mathieu Coulis / ZooKeys 510: 115–124 (2015)
116
Introduction
In many organisms, ongoing climate change aects the timing of life-cycle events such
as activity, growth and reproduction (Parmesan 2006). When no long-term data sets
are available to analyse trends in local populations, potential phenological responses
to climate change can be studied by examining intraspecic variation in widespread
species that live in a wide range of conditions.
In millipedes (Diplopoda), geographic variation in life-cycle characteristics has
been documented for some species of European julids (Fairhurst 1974, David 1982),
but there is little precise information for populations living in the Mediterranean re-
gion. A number of widespread species such as Cylindroiulus caeruleocinctus (Wood),
Cylindroiulus punctatus (Leach), Leptoiulus belgicus (Latzel), Ommatoiulus rutilans (C.
L. Koch) and Ommatoiulus sabulosus (Linnaeus) have populations in this area, which
is typied by cool winters and hot, dry summers. e study of phenological character-
istics in Mediterranean populations of these species is particularly interesting, because
climate change scenarios predict warmer and drier summer conditions over large parts
of western Europe for the end of the 21st century (IPCC 2013). e purpose of the
present study is to describe the life cycle of a Mediterranean population of O. sabulosus
and to compare the results with those previously obtained further north in Europe,
so as to highlight dierences between populations from the two climatic zones. e
species has a wide distribution, from Finland and Scotland to Albania and Spain, in
contrast to most Ommatoiulus species that are conned to the Iberian peninsula and
north Africa (Akkari and Engho 2012). Two forms occur in southern France: that
in which adults have two orange-yellow bands on the back, and a typically Mediter-
ranean form, the so-called O. sabulosus aimatopodus (Risso), in which adults are black
dorsally. e latter form is the most common in southern France and often occurs at
high population densities in shrubland ecosystems on limestone (Coulis et al. 2013).
e post-embryonic growth and development of O. sabulosus were described in
detail by Halkka (1958) and Sahli (1969). e life cycle, i.e. the calendar of events be-
tween birth and reproduction, was studied under eld conditions by Halkka (1958) in
Finland, Sahli (1968) in Germany, Biernaux (1972) in Belgium and Fairhurst (1974)
in Great Britain. Reproduction occurs in late spring and summer in all these regions.
Biernaux (1972) tentatively suggested that both males and females mature in two years
in Belgium, but Fairhurst (1974) concluded that males take two or three years, and
females three or four years, to reach maturity in Great Britain. As regards Mediterra-
nean populations, Sahli (1991a, 1992) studied in detail the timing of male maturation
and adult–intercalary male successions (periodomorphosis) in O. sabulosus aimatopo-
dus from the Alpes-Maritimes and Provence, southern France. is author mentioned
that egg-laying occurs in late summer–early autumn (Sahli 1991a), but provided very
limited information on the growth, development and age at reproduction of females.
Sahli (1991b) suggested that females could breed only once before dying in Mediterra-
nean populations (semelparity), in contrast to Biernaux (1972) who concluded, based
on his own study of egg development in populations from Belgium, that females can
Millipedes faced with drought: the life cycle of a Mediterranean population... 117
breed in successive years (iteroparity). e presence of an abundant population of O.
sabulosus aimatopodus in a garrigue ecosystem of Provence provided the opportunity to
clarify some aspects of the species’ biology in the eld, with particular attention to how
this julid adjusts its phenology under warmer and drier conditions.
Methods
is study was conducted at the Massif de l’Etoile near Marseille, southern France
(5°25'E; 43°22'N), in a shrubland dominated by rockrose (Cistus albidus L.), kermes
oak (Quercus coccifera L.), rosemary (Rosmarinus ocinalis L.) and gorse (Ulex parviorus
Pourr.). e soil is shallow rendzina on limestone, in which rock fragments and stones
represent about 60% of the soil volume in the top 20 cm. e mean annual temperature
in the area is 15.1 °C, mean monthly temperatures ranging from 7.1 °C in January to
24.1°C in July, and the mean annual rainfall is 555 mm (Marseille 1981–2010 climate
normals). e driest months are June, July and August, during which the soil becomes
very dry. e millipede community, heavily dominated by O. sabulosus aimatopodus, also
comprises an abundant population of Polyxenus lagurus (Linnaeus) (Polyxenidae) and
rare specimens of Leptoiulus sp. (Julidae) and Trichoblaniulus sp. (Trichoblaniulidae).
Collections of millipedes were made using dierent methods. (1) Twenty three pit-
fall traps were set on the site in late March 2010 (8 days) and late April 2010 (10 days).
(2) Leaf litter and topsoil samples were taken within 25 × 25 cm quadrats in May 2010
(31 sampling units), November 2010 (12 s.u.), May 2012 (31 s.u.), October 2013 (15
s.u.), November 2013 (11 s.u.), March 2014 (12 s.u.), April 2014 (31 s.u.) and Septem-
ber 2014 (13 s.u.). Millipedes were extracted using Tullgren funnels. (3) Large individu-
als were also collected by hand in leaf litter to determine their reproductive status.
Individuals were assigned to a stadium by counting the rows of ocelli (R.O.) on
each side of the head (1 R.O. = stadium II, 2 R.O. = stadium III, etc.) (Engho et al.
1993). e method, however, was often dicult to apply from stadium XI onwards.
e numbers of podous rings (including the collum) and apodous rings (excluding
the telson) were counted. Intercalary males were distinguished from other males by a
much smaller rst pair of legs than in immature males, but not modied into hooks
as in copulatory males (Halkka 1958). Forty-two females of stadia X and higher were
dissected to determine whether mature eggs (i.e. brownish, subspherical eggs about 0.6
mm long) were present in the ovitube.
e growth of several cohorts in the eld was studied by examining changes in the
proportions of stadia in successive samples (Blower 1970). In addition, 40 individuals
of various stadia were reared in the laboratory for periods ranging from a few months
to two years. ey were kept in transparent plastic boxes containing sieved soil and
moist leaf litter. e boxes were placed in incubators tted with a glass door, in which
temperature followed the long-term monthly mean temperatures of Marseille, with a
daily thermoperiod of low amplitude. All millipedes received a pinch of powder yeast
every month and, occasionally, rabbit faeces as supplementary food.
Jean-François David & Mathieu Coulis / ZooKeys 510: 115–124 (2015)
118
Results
Post-embryonic growth and development in the eld
e stadia identied using the numbers of R.O., and the numbers of body rings count-
ed in each stadium, are indicated in Table 1. In terms of ring numbers, growth was
slightly dierent from that reported in more northern populations, with an extra apo-
dous ring in stadia III and IV. is was conrmed by the higher numbers of podous
rings from stadium IV onwards. e maximum number of stadia is uncertain because
it was generally impossible to decipher the exact number of R.O. in the largest indi-
viduals. However, a few males had at least 12 R.O. (stadium XIII) and a female with
57 podous rings had at least 13 R.O. (stadium XIV).
Sexual dimorphism was apparent at stadium VI. Although two males reared in
the laboratory reached maturity at stadium IX, the smallest adult males found in the
eld were in stadium X (Table 1). Immature males were numerous up to and includ-
ing stadium XI, indicating that many males mature for the rst time in stadia XI or
XII. Intercalary males were found from stadium XI onwards. Dissection of females in
late summer–early autumn, just before the breeding period (see below), showed that
ovigerous females carrying mature eggs were present in any stadium from stadium XI
onwards. None of the stadium X females that were dissected (n = 6) were ovigerous.
Phenology
Juveniles were active in leaf litter in late October as stadium II, in mid-November as sta-
dia II and III (Fig. 1b), and in mid-December as stadia III and IV. Also, a female kept for
Table 1. Growth and development of O. sabulosus in Provence. e number of rows of ocelli (R.O.), the
range of podous rings (collum included) and the numbers of apodous rings (telson excluded) are given for
each stadium. Male stages: Im. = Immature; Ad. = adult; Int. = Intercalary.
Stadium R.O. Podous rings / Apodous rings Male development
Juveniles Females Males
II 1 6 / 5
III 2 11 / 5,6
IV 3 16–17 / 6,7
V 4 22–24 / 6,7
VI 5 29–32 / 6,7,8 29–32 / 6,7 Im.
VII 6 35–38 / 5,6 36–39 / 5,6 Im.
VIII 7 42–45 / 3,4 41–45 / 2,3,4 Im.
IX 8 45–49 / 1,2,3 44–49 / 1,2,3 Im.
X 9 47–50 / 1,2 47–50 / 1,2 Im., Ad.
XI 10 48–53 / 1 48–50 / 1 Im., Ad., Int.
XII+ ≥ 11 49–57 / 0,1 50–55 / 0,1 Ad., Int.
Millipedes faced with drought: the life cycle of a Mediterranean population... 119
months in the laboratory produced stadium II juveniles in late October. Samples taken
in late March showed that the new generation was mainly in stadium V by the end of
winter (Figs 1c, 2a), which implies moulting during the winter. is result was conrmed
in laboratory rearings, in which juveniles that had hatched in October emerged from the
soil as stadium V in March. e rearings further showed that the new generation contin-
ued to grow rapidly in spring, from stadium V in March (rearing temperature: 10 ± 2°C)
to stadium VI in April (13 ± 2 °C) and to stadium VII in May (17 ± 2 °C), exactly as in
the eld (Fig. 2b). Sexual dierentiation at stadium VI thus occurs at the age of about
6 months. e pace of growth slowed markedly around the summer. Litter and topsoil
samples taken in early October showed that the smallest individuals, born in autumn of
the preceding year, were in stadia VII and VIII (Fig. 1a), indicating that only one moult
had occurred since May. All those one-year old millipedes were immature in both sexes.
During the second year of growth, no moult occurred from October to mid-No-
vember (Fig. 1b). At this time of year, the population becomes progressively inactive
in the soil, both in the eld and in the laboratory. One-year old millipedes moulted
once during the winter and emerged from the soil in late March as stadia VIII and
IX (Figs 1c, 2a). is was conrmed in laboratory rearings, in which six males and
females of stadium VIII collected in the eld in October burrowed into the soil in
October–November and emerged as stadium IX in March. Field samples taken in
2010 (Fig. 2) showed that the generation that was in stadia VIII and IX at the end of
winter remained in these stadia until May, moulted in mid-May (as shown by the large
Figure 1. Phenology of O. sabulosus in Provence (October 2013–April 2014). Stadia are indicated on the
horizontal axis and those of three identiable generations (G 2011 without any individuals, G 2012 and
G 2013) are grouped together. White bars = undierentiated juveniles and females; grey bars = immature
and intercalary males; black bars = adult males. Abundant (+) or very abundant (++) juveniles of stadia II
and III were not included in the calculation of percentages.
Jean-François David & Mathieu Coulis / ZooKeys 510: 115–124 (2015)
120
proportion of millipedes that were moulting at the time of sampling), and was still in
stadia IX and X in mid-November, at the age of two. e complete absence of stadia
IX and X in the autumn of 2013 (Fig. 1a, b) indirectly conrms that these stadia are
reached in two years, since, for unexplained reasons, there was no recruitment in the
autumn of 2011. Similarly, samples taken in the autumn of 2010 (Fig. 2c) suggest
there was no or little recruitment in that year, which was conrmed in subsequent
samples (data not shown).
e number of moults during the third year of growth cannot be deduced from
the eld data. Assuming that there are two further moults — one in winter and one
in spring, as in the second year of growth — most individuals of stadia XI and XII
found in the autumn of 2013 (Fig. 1a) would be three years old. However, this would
be inconsistent with the lack of juvenile recruitment in 2010, and it is likely that most
individuals in stadia XI and XII collected in the autumn of 2013 were actually born
before 2010.
Life-cycle duration
By combining the results on individual development and phenology, one may infer
that a small proportion of males that reach maturity at stadium X reproduce at the age
of two. However, many males that mature for the rst time at stadia XI and XII cannot
reproduce until the age of three. ere is no evidence that some females breed at the
age of two, since no ovigerous females were found in stadia IX and X in late summer.
Females need at least three years to reach stadium XI and lay eggs in early autumn.
Figure 2. Phenology of O. sabulosus in Provence (March 2010–November 2010). See explanations in
the legend to Fig. 1.
Millipedes faced with drought: the life cycle of a Mediterranean population... 121
e continuation of the life cycle was observed in a few adults reared in the labora-
tory. ree adult males collected in autumn moulted during the winter and emerged
from the soil in March as intercalary males. ey became mature again after a further
moult in spring and remained in the adult stage until the following autumn. Two large
females collected in autumn also moulted during the winter but, in contrast to males,
they did not moult again in spring or summer. One of these females bred in October,
overwintered a second time in the laboratory, and survived until the following Sep-
tember but without moulting. Post-mortem inspection showed that this female had no
apodous ring and contained no eggs.
Discussion
e present study provides the rst estimate of life-cycle duration for O. sabulosus in
southern France. e interpretation of our eld data was made easy by the generally
high abundance of juveniles and also by gaps between successive generations, possibly
due to reproduction failures and/or high juvenile mortality rates in some years. In the
population studied near Marseille, stadia VII and VIII are consistently reached after
the rst year of growth, and stadia IX and X after the second year. is pattern was ob-
served in three generations born between 2008 and 2012, despite some variation from
one year to another (e.g. the cohort born in 2008 was mainly in stadium VIII in late
March 2010, while that born in 2012 was mainly in stadium IX in late March 2014).
Our results dier from those of Sahli (1992), who assumed that stadia X and XI were
reached at the age of three in the region of Provence.
As adult males were found from stadium X onwards in our samples, some males
may reproduce at the age of two. However, males that reach maturity in stadia XI or
XII cannot reproduce until the age of three at the earliest. Also, ovigerous females,
which were found from stadium XI onwards in our samples, cannot breed until the
age of three at the earliest. Moreover, the presence of some stadium XI females without
any mature eggs in early autumn suggests they may start breeding at the age of four.
erefore, the duration of the life cycle, which corresponds to the age of females at rst
reproduction, is three or possibly four years in this Mediterranean population, i.e. the
same as in populations studied by Fairhurst (1974) in Great Britain.
It remains unclear whether each female breeds only once during its lifetime (semel-
parity) or can breed over several years (iteroparity). Sahli (1991a) assumed that O. sabu-
losus females might be semelparous in Mediterranean populations, reproduction being
spread over dierent stadia and dierent years in each generation. In the present study,
the single female that bred in the laboratory survived for a further year but died without
breeding again, so that there is still no direct evidence for iteroparity. Moreover, we did
not nd clusters of small oocytes at the same time as mature eggs in ovigerous females,
which Biernaux (1972) mentioned as evidence for iteroparity in O. sabulosus. On the
other hand, dissection of females in late summer–early autumn revealed that the pro-
portion of those not carrying mature eggs in stadia XI and higher was rather low (22%),
Jean-François David & Mathieu Coulis / ZooKeys 510: 115–124 (2015)
122
and the question is whether this is suciently high to be consistent with semelparity.
Semelparity would imply that many females in stadia XI, XII and even XIII postpone
reproduction until the next year(s), which should result in a substantial proportion of
females without eggs in early autumn. is topic requires further research.
Although Mediterranean conditions do not modify the length of the life cycle in
O. sabulosus, several phenological characteristics are very dierent between the popula-
tion of Marseille and more northern populations. First, there is a shift of the breeding
season. In northwestern Europe, the species generally breeds in summer (Sahli 1968,
Biernaux 1972, Fairhurst 1974). Under milder climate conditions, as on the island of
Jersey, the species tends to breed earlier (Fairhurst 1974). However, our study con-
rms that, in the Mediterranean region, the breeding period of O. sabulosus is delayed
until the autumn (Halkka 1958, Sahli 1991a). Juveniles of stadia II to IV were col-
lected only in this season. ey grow rapidly from autumn to the following spring
and the rst part of the life cycle is similar to that of Ommatoiulus moreleti (Lucas) in
southern Portugal, which breeds in late autumn–early winter (Baker 1984). In both
species, the earliest active stadia (stadia II to VI) are never faced with the hot and dry
conditions of the summer, which may be an adaptation of the Mediterranean popula-
tions of Ommatoiulus. It should be noted that, in other millipedes, the youngest stadia
are by far the least resistant to desiccation (David and Vannier 2001).
e seasonal patterns of activity and growth also dier between the two climatic
areas. In northern populations, there is generally a single period of activity and growth
from spring to autumn and the species is active in summer (Halkka 1958, Fairhurst
1974). e duration of the active season clearly increases with increasing temperatures
in areas where the risk of summer drought is low (cf. Halkka 1958, Fairhurst 1974,
Meyer 1985). In the Mediterranean population, however, activity stops during the
summer months, and our study has shown that there is at most one moult between
May and September. Similarly, in O. moreleti living at low altitudes in Madeira, Read
(1985) reported that growth slows down during the summer, presumably due to dry
conditions. e presence of two long periods of inactivity, in summer as well as winter,
largely explains why the life cycle of O. sabulosus is not shorter under Mediterranean
conditions, as would have been expected for millipedes living in a warmer climate
(David and Handa 2010).
Conclusion
e life cycle of O. sabulosus in the Mediterranean region appears to be inuenced
mainly by the summer drought. e dry season especially impacts phenology, i.e. the
timing of activity, growth and reproduction. Contrary to many organisms that breed
earlier in spring under warmer conditions, this julid breeds in autumn under Medi-
terranean conditions, so that juveniles are unlikely to be exposed to severe drought.
Moreover, larger stadia become inactive in summer and the total duration of activity
over a year is roughly the same as in northern populations. As a result, the life cycle is
Millipedes faced with drought: the life cycle of a Mediterranean population... 123
not shorter in the Mediterranean region than in Great Britain. Although it is too soon
to generalize, the life cycle of O. sabulosus in southern France is quite similar to that of
O. moreleti in southern Portugal, suggesting ways in which a number of julids could
respond to drier summer conditions in the context of climate change.
Acknowledgements
We thank Anais Rancon, Anne Gorgeon, Mathieu Santonja, and all the members of
the Bioux team who assisted in eld sampling. is study was conducted as part of
the CLIMED project funded by the French National Agency for Research (ANR-09-
CEP-007).
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... Cardboard roll traps consisted of a 50 mm diameter, 200 mm length PVC pipe with a piece of single sided corrugated cardboard (length: 250 mm × width: 50 mm rolled to form 50 mm diameter) inserted into the pipe. Rolls have not been used previously to capture millipedes though the trap is similar in nature to hay traps (David & Coulis, 2015;Tuf et al., 2015). Three rolls were placed approximately 2 m from the pitfall traps (i.e. 12 cardboard rolls per site). ...
... Females collected in our study carried mature eggs at a later stadial stage than found by Baker (1978c), who noted mature eggs at stadium 7. In France, David and Coulis (2015) found females of Ommatoiulus sabulosus L., a close relative of O. moreleti, breeding in autumn, consistent with the peak breeding period observed here. This is contrary to Blower and Miller (1977) who observed female Cylindroiulus nitidus (Verhoeff) to have either laid or be laying eggs in May (Northern hemisphere -spring), which is opposite to the autumn laying period observed in our study. ...
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• The Portuguese millipede, Ommatoiulus moreleti (Lucas, 1860), is increasingly a pest of grains crops in Australian agricultural ecosystems. With the rapid uptake of minimum‐tillage practices, habitat quality has been enhanced for several species of soil dwelling invertebrates, in particular O. moreleti. • To understand the population dynamics of O. moreleti in Australian grains crops, populations were sampled at multiple sites for more than 2 years using pitfall traps and cardboard roll traps. Specimens were dissected to investigate reproductive status and developmental stage. • Millipede trapping rates varied between sites and across the year, and tended to be lower when soil water content (m³/m³) was high. Both sexes were active year round, however females were relatively more abundant when ground temperatures were higher. • Males in a copulatory state and females with mature eggs were collected year round although females lacking mature eggs were more common when ground temperatures were higher and the soil was drier, and female egg load was higher under cooler conditions. Females at a stadium 9 or later carried mature eggs and copulatory males tended to be from stadium 8 or later. Different developmental stages could be recovered at all times of the year. • These findings indicate persistent populations of O. moreleti across fields throughout the year, with a key breeding period in autumn but likely opportunistic breeding all year. Control of millipedes will need to focus on increasing the impact of biological agents, decreasing suitable habitat for millipede breeding and intensive control at susceptible crop periods.
... In arthropods, stressors can cause many alterations of all of the organelles and structures in the cells that form the midgut epithelium, and eventually they can severely damage the entire epithelium (Rost-Roszkowska et al. 2008, 2016bWilczek et al. 2014;Fontanetti et al. 2015;Karpeta-Kaczmarek et al. 2016). Therefore, the midgut is treated as a model organ for studies on how the external environment can affect the entire organism with special emphasis on the effects of the stressors that originate from the soil in terrestrial ecosystems (Fontanetti and Godoy 2007;David and Coulis 2015). Changes in the tissues/organs of animals, which are treated as bio-indicators, are at the center of analyses in the environmental sciences (Karpeta-Kaczmarek et al. 2016). ...
... Changes in the tissues/organs of animals, which are treated as bio-indicators, are at the center of analyses in the environmental sciences (Karpeta-Kaczmarek et al. 2016). Millipedes are considered to be bio-indicators in assessments of soil pollution because by living in the soil, they play an important role in the aeration, humification, and enrichment of the soil and they are very sensitive to all changes of the environment (Hopkin et al. 1985;Godoy and Fontanetti 2010;Nogarol and Fontanetti 2010;David and Coulis 2015). ...
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The midgut of millipedes is composed of a simple epithelium that rests on a basal lamina, which is surrounded by visceral muscles and hepatic cells. As the material for our studies, we chose Telodeinopus aoutii (Demange, 1971) (Kenyan millipede) (Diplopoda, Spirostreptida), which lives in the rain forests of Central Africa. This commonly reared species is easy to obtain from local breeders and easy to culture in the laboratory. During our studies, we used transmission and scanning electron microscopes and light and fluorescent microscopes. The midgut epithelium of the species examined here shares similarities to the structure of the millipedes analyzed to date. The midgut epithelium is composed of three types of cells-digestive, secretory, and regenerative cells. Evidence of three types of secretion have been observed in the midgut epithelium: merocrine, apocrine, and microapocrine secretion. The regenerative cells of the midgut epithelium in millipedes fulfill the role of midgut stem cells because of their main functions: self-renewal (the ability to divide mitotically and to maintain in an undifferentiated state) and potency (ability to differentiate into digestive cells). We also confirmed that spot desmosomes are common intercellular junctions between the regenerative and digestive cells in millipedes.
... Beetles, dipterans, and other insects usually moult through their 3-5 instar larvae stages (Klausnitzer and Zwick, 1997). Studies devoted to the size distribution of the instar larvae of insects or myriapods are usually published by taxonomists who describe their differences and development throughout the life cycle (David and Coulis, 2015;Ferreira et al., 2018). There are seemingly no published reports on the estimated abundance of soil macrofaunal taxa, including the separation of instar larval stages. ...
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The soil macrofauna, including animals between 1–2 mm and 20–30 mm in size, uses soil differently from the mesofauna, which lives in cavities, or microfauna that inhabits water films. In some ecosystems, the macrofauna accounts for most of the total soil animal biomass and substantially contributes to soil food-web functioning. Additionally, the macrofauna can be among the most diverse groups in the soil environment. A few macrofaunal taxa (e.g. earthworms and termites) are considered to be ecosystem engineers attracting research focus, while studies on most other soil macrofauna remain scattered and uneven. An analysis of 80 publications conducted for this study showed inconsistent definitions of soil macrofauna by specialists. Further, a comparison of taxa listed among the soil macrofauna and mesofauna deduced that researchers allocate soil animals to either group by higher-level taxonomic categories and not by size. The main challenge in soil macrofaunal surveys is the extremely high diversity of species from widely different taxa, which require highly specialised taxonomists to identify them to species level. The abovementioned publication analysis showed that small taxa, mainly insects, are often not surveyed. In addition, animals of the same species at different ontogenetic stages that coinhabit the soil are not analysed separately. This tendency leads to an underestimation of the abundance and biomass of early larval stages. Hence, the soil macrofauna is seldom included in analyses of soil ecosystem functioning and modelling. Synchronised and unified studies across biomes could draw more attention to this size group and increase research focus and output from soil ecologists and other scientists.
... Based on the number of these body segments it is possible to determine the post-embryonic development stage of the species (Blower 1985). This is considered an important characteristic as there is little to no variation in the development patterns of these taxa (Enghoff et al. 1993), thus allowing aspects of their phenology to be evaluated (David et al. 2003, Youngsteadt 2009, David and Coulis 2015. ...
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Studies that address biodiversity and its supporting mechanisms in different ecosystems are fundamental to understanding the relationships between species and the prevailing environmental conditions within each habitat type. This study presents information on the phenology of Promestosoma boggianii (Silvestri, 1898) and its association with seasonal flood and dry events in a floodplain of Mato Grosso's northern Pantanal region, Brazil. Sampling was carried out in three areas located between the Bento Gomes and Cuiabá rivers, on the Porto Cercado Road, Poconé-MT. Each sample area was composed of two treatments: (I) floodable habitats and (NI) non-floodable habitats. Three quadrats (10 x 10 m) were established within each treatment, with sampling carried out using pitfall traps and mini-Winkler extractors during the dry season, rising water , high water and receding water phases for the duration of two hydrological cycles within the Pantanal (2010/2011 and 2011/2012). A total of 295 P. boggianii individuals were sampled at different stages of development (except stages I and II), distributed between the rising water (209 ind., 70.8%), dry (76 ind., 25.8%) and receding water (10 ind., 3.4%) seasons. No specimens were sampled during the high water season. The higher abundances recorded between the dry and rising water seasons, primarily at early stages of development, indicate that P. boggianii is characterized as a univoltine species in these habitats. The data demonstrate that individuals of P. boggianii were more abundant in floodable habitats. In addition, the results show that the life cycle of this diplopod is sinchronized to the seasonal nature of this floodable environment, as a strategy to survive the extreme conditions of terrestrial and aquatic phases Brazil's northern Pantanal region.
... In this study, we focused on the two most abundant shrub species Q. coccifera and C. albidus. The saprophagous macrofauna community is dominated by the julid millipede O. sabulosus aimatopodus, a Mediterranean subspecies of O. sabulosus with no dorsal yellow bands and that has a phenology adapted to the Mediterranean climate (David and Coulis 2015). Its population density and biomass, which vary seasonally and annually, were estimated at 164 ± 37 individuals m -2 and 9.2 ± 2 g (live mass) m -2 , respectively, in the spring of 2010. ...
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In many terrestrial ecosystems, large amounts of leaf litter are consumed by macroarthropods. Most of it is deposited as faeces that are easily transferred into deeper soil layers. However, the decomposition of this large pool of organic matter remains poorly studied. We addressed the question of how leaf litter transformation into macroarthropod faeces, and their burial in the soil, affect organic matter decomposition in a Mediterranean dry shrubland. We compared mass loss of intact leaf litter of two dominant shrub species (Quercus coccifera, Cistus albidus) with that of leaf litter-specific faeces from the abundant millipede Ommatoiulus sabulosus. Leaf litter and faeces were exposed in the field for 1 year, either on the soil surface or buried at 5 cm soil depth. Chemical and physical quality of faeces differed strongly from that of leaf litter, but distinctively between the two shrub species. On the soil surface, faeces decomposed faster than intact leaf litter in Quercus, but at similar rates in Cistus. When buried in the soil, faeces and leaf litter decomposed at similar rates in either species, but significantly faster compared to the soil surface, most likely because of higher moisture within the soil enhancing microbial activity. The combined effects of leaf litter transformation into faeces and their subsequent burial in the topsoil led to a 1.5-fold increase in the annual mass loss. These direct and indirect macroarthropod effects on ecosystem-scale decomposition are likely more widespread than currently acknowledged, and may play a particularly important role in drought-influenced ecosystems.
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A comprehensive revision of the species of the genus Ommatoiulus in Andalusia, southern Spain, is carried out for the first time, revealing the presence of a total of 19 species, among which are one new record for the country, one for continental Spain, two new records for Andalusia and 10 species new to science: Ommatoiulus baenai, O. baileyi, O. hoffmani, O. jaenensis, O. kimei, O. pseudoflagellatus, O. recueroi, O. reipi, O. sabinarensis, O. schubarti n.spp. The following taxa are synonymised: Schizophyllum hoplites Verhoeff, 1910, S. diplurum appendiculatum Brolemann, 1925, and Ommatoiulus diplurus mauriesi Hoffman, 1975, are regarded as junior synonyms of Ommatoiulus diplurus (Attems, 1903), n.syn. Schizophyllum dorsovittatum estrellanum Verhoeff, 1910, and S. calatravanum Brolemann, 1920, are junior synonyms of Ommatoiulus dorsovittatus (Verhoeff, 1893), n.syn. Schizophyllum nivale Schubart, 1959, is a junior synonym of Omnmatoiulus ilicis (Brölemann, 1896), n.syn. Full descriptions and diagnostic notes are provided for all the species with accounts on their distributions, habitats, and notes discussing their taxonomy. A dichotomous identification key, based on gonopod structures, is presented to facilitate species identification. In the discussion section, the general patterns of species distribution are underlined, showing a clear tendency to 'endemism' for the majority of species and to polymorphism for species with broader distribution ranges, especially O. diplurus. A disjunct distribution Andalusia/Pyrenees is registered for O. ilicis. A comprehensive comparison of gonopods is attempted, and three main types of gonopod configuration are delimited, denoting a wide range of structural complexity. The fovea, a cavity in the posterior gonopods, is explored for the first time with scanning electron microscopy, revealing an agglutination of spermatozoa and confirming Verhoeff's original observation dating back nearly 120 years. The constancy of the fovea in all Schizophyllini, combined with its absence in the rest of the julids, provides an additional apomorphy for the tribe.
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Ommatoiulus moreletii, a severe nuisance pest in SE Australia, is widespread in continental Portugal, where it is indigenous, and also on Madeira and the Azores island of Sao Miguel where it is introduced. O. moreletii varied morphologically within continental Portugal. The form found near Lisbon was most similar to that found in Australia and other introduced populations. The life history of O. moreletii near Lisbon was similar to that in Australia, but certain aspects (breeding season, age distribution) varied in other areas of Portugal. The fecundity of O. moreletii was higher in Portugal than in Australia, due to the larger size of Portuguese females.-Author
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This paper provides information on male juvenile to adult maturation moults (= MMJ) in Om- matoiulus sabulosus (L.) in the Maritime Alps and Provence. Five kinds of MMJ variabilities are studied. The no- tions of poor, good and "explosive" MMJ are dealt with.
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The research area includes subalpine meadows, alder communities, dwarf-shrub heaths, lichen heaths and highalpine meadows (1960 m–3090 m a.s.l.). The material consists of 4419 Julidae (31.6% adult) collected by extraction of litter samples (66.4%), in pitfall traps (26.3%) and by handsampling (7.3%). Cylindroiulus meinerti (Verhoeff) only occurred below 2000 m; Leptoiulus saltuvagus (Verhoeff) was mainly found at Alnus viridis sites; Leptoiulus simplex (Verhoeff) had its main distribution in the lichen heath (2200-2300 m); Ommatoiulus sabulosus (L.) was found most frequently in the subalpine meadow and Leptoiulus alemannicus (Verhoeff) occurred up to 2800 m without any altitudinal concentration. Adults of L. saltuvagus showed only one distinct activity peak in September, those of L. simplex were diplochronous (June/September) and O. sabulosus summer stenochronous (July). L. saltuvagus reached maturity in stage IX (only males), X or XI after four or five Years. In their first year of growth the members of a generation reached the third or fourth stage, in the second year the sixth or seventh, in the third year the eighth or ninth. Females could carry full-sized eggs in the autumn of the fourth year in the tenth stage or in the fifth year in stage eleven. Apparently eggs may be laid in spring of the fifth or sixth year. Overwintering density of L saltuvagus in alder litter was found to be 215.6 ± 38.7 inds m−2, the mean biomass 1.16 g m−2(max. 1.88 g m−2). Mean annual production during the growth period of 4-5 months was in the order of 0.85 g m−2 (max. 1.36 g m−2).
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The density and surface activity of the millipedes in a quarter of an acre of a sycamore ash wood are described. Seven species were extracted by Tullgren funnels from samples of soil and litter over five years and were also caught in pitfall traps during a further two years; four other species occurred occasionally in the traps. Each square metre of the site supported 100 individuals over the winter, rising to 300 in the summer. Of these, 85 % belonged to three species, Iulus scandinavius, Polydesmus angustus and P. denticulatus. Male I. scandinavius become adult in either the ninth, tenth or eleventh stadium; females in the tenth and eleventh. Eggs are laid in spring and these take three years to become adults which breed and then die. The majority of Polydesmus spp. in the samples are young belonging to the first six of the eight free-living stadia. The adults fell into the traps in the summer and newly emerged young appear in the samples at this time. They overwinter in their first year mainly as fifth stadia; some might reach maturity (eighth stadia) in the summer following, but it is not certain that they could breed at this time. The pattern of dispersion of lulus is fairly even and is correlated with the distribution of leaf litter but the Polydesmus spp. are highly aggregated. All stadia of lulus fall into the traps but only the last two of Polydesmus. The aggregation of Polydesmus spp. appears to be correlated with the relative inactivity of the younger stadia. The estimates of density of Polydesmus spp. are unreliable because of their aggregation but those of lulus have determinable limits and it is possible to derive rough though meaningful standing crop, production and life-table data. The overwintering standing crop of lulus consists of the survivors of three generations of 5, 2.2 and 1.4% of the original eggs laid; it has a fresh weight of about 1.25 g and a production in the order of 1.5–2.5 g/m2.
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Water loss at increasing temperature in dry air (< 5% r.h.) was measured for the eight stadia of Polydesmus angustus Latzel (Diplopoda, Polydesmida: Polydesmidae). Instantaneous rates of water loss, expressed as percentages of original body water, were calculated at 20, 25 and 30°C. At each temperature, the rate of water loss varied greatly among stadia, decreasing between 15- and 18-fold from stadium I to stadium VII, and then significantly increasing from stadium VII to stadium VIII (adult). In all stadia, the rate of water loss increased with rising temperature, but the temperature effect was much more pronounced in juveniles than in larger stadia. The threshold temperature of heat stupor, which was measured from stadium IV onwards, increased significantly during development, from 35.6°C in stadium IV to 39.5°C in adults. Survival at 20°C and 76% r.h. varied as could be expected from the water loss rates in dry air, survival time increasing from stadium I to stadium VII and then decreasing from stadium VII to the adult stage. The maximum tolerable water loss, estimated for stadia V, VII and adults, did not change significantly among stadia (mean: 47% of the original water content), suggesting that survival times under desiccating conditions depended primarily on the rates of water loss. The relevance of the results in terms of summer survival under natural conditions is discussed, and it is concluded that juvenile mortality could be substantial in the field. This is important for understanding the adaptive value of cohort-splitting in P. angustus.
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A review of the postembryonic development of millipedes (Diplopoda) is given, based mainly on published information. Original observations are, however, also included. Millipedes hatching from the pupoid usually have three pairs of legs; during their postembryonic growth they acquire more segments and more legs. This process is known as anamorphosis. Three types of anamorphosis are recognized. In euanamorphosis, every moult is accompanied by addition of new segments, even after the attainment of sexual maturity. In hemianamorphosis , the addition of new segments goes on until a certain stadium, and further moults take place without addition of segments. In teloanamorphosis , the addition of segments stops at a certain stadium (the adult, and ultimate, stadium) after which no further moults occur. Available information on anamorphosis in each of the millipede orders is reviewed. General patterns are emphasized, but variations are also considered in detail. It is shown that the so-called 'law of anamorphosis' is valid only for the 'ring-forming' millipedes (Merocheta and Juliformia) in which tergites, pleurites, and sternites of each diplosegment are firmly fused into a complete 'ring', and for some other forms (Polyzoniida, Chordeumatida), where there is a constant relationship between rings and legs. The chapter on the order Julida is particularly detailed and includes discussions of patterns in the variation and a section on periodomorphosis. The general chapter on developmental patterns includes inter alia an interpretation of the variations in millipede anamorphosis in terms of the 'biometabolic modi' of Remane. The hypothetical ancestral millipede is shown to have developed by hemianamorphosis. Euanamorphosis was acquired by the ancestral species of Helminthomorpha. Within this clade, Chordeumatida and Merocheta have secondarily become teloanamorphic, whereas some Juliformia seem to have returned to hemianamorphosis. The contrasting principles of elongation and contraction, subject of much debate among diplopodologists, are shown both to have played a role in the course of millipede evolution.
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Ecological changes in the phenology and distribution of plants and animals are occurring in all well-studied marine, freshwater, and terrestrial groups. These observed changes are heavily biased in the directions predicted from global warming and have been linked to local or regional climate change through correlations between climate and biological variation, field and laboratory experiments, and physiological research. Range-restricted species, particularly polar and mountaintop species, show severe range contractions and have been the first groups in which entire species have gone extinct due to recent climate change. Tropical coral reefs and amphibians have been most negatively affected. Predator-prey and plant-insect interactions have been disrupted when interacting species have responded differently to warming. Evolutionary adaptations to warmer conditions have occurred in the interiors of species’ ranges, and resource use and dispersal have evolved rapidly at expanding range margins. Observed genetic shifts modulate local effects of climate change, but there is little evidence that they will mitigate negative effects at the species level.