|

J. S. Gray, Department of Environmental Resource Management,
University College Dublin, Ireland.
Abstract
Ticks of the Ixodes ricinus (persulcatus) species complex are vectors
for several zoonotic diseases including, babesiosis, ehrlichiosis, Lyme
borreliosis and tick-borne encephalitis. An understanding of the biology
of the vectors is fundamental to prevention and control of these diseases,
and in addition to summarising established knowledge, this review
addresses recent work on seasonal activity, host specificity, inter- and
intraspecific variations in biology and factors affecting distribution and
abundance.
Taxonomy
Ticks, which are related to spiders, are divided into two families, the
Argasidae (soft ticks), and the Ixodidae (hard ticks). The two families
differ in their morphology, feeding habitats and details of life cycles.
All feed on the blood of vertebrates, but whereas the soft ticks
(argasids) take relatively small frequent blood meals of short duration
(minutes to hours), the hard ticks (ixodids) take just one very large
blood meal at each instar (larva, nymph, adult female) and remain feeding
at the same site for several days. Although members of both families can
inflict direct damage, their main significance is as vectors of disease.
The argasids generally occur in the immediate vicinity of their hosts e.g.
burrows, nests etc (i.e. are endophilic) and visit their host(s) at
frequent intervals to feed. Although a few soft tick species transmit
important diseases such as human relapsing fever and African swine fever,
they are far surpassed in veterinary and medical importance by the
ixodids. The ixodids are considered to be globally the most important
ectoparasites of livestock and are also vectors of many zoonotic diseases.
Some ixodids have an endophilic habit, but the majority of important
species are exophilic and when hungry they are found in the open, usually
on the tips of vegetation from where they ambush passing hosts. The
ixodids may be further classified as prostriate or metastriate, based
primarily on morphological detail, but life cycle differences include the
ability of the males of some prostriate species to undergo spermatogenesis
and to mate without taking a prior blood meal. The majority of important
ixodid species are metastriate, but the single prostriate genus
Ixodes
includes species that acquired added notoriety in the latter part of the
20th century as the vectors of several northern hemisphere zoonoses, such
as Lyme borreliosis (LB), ehrlichiosis, babesiosis and tick-borne
encephalitis (TBE) (Table 1). This review will focus primarily on the main
vectors of these diseases, which are ticks of the Ixodes ricinus
(persulcatus) species complex.
Distribution and life cycles
The Ixodes ticks responsible for the transmission of Lyme borreliosis
and other zoonoses are distributed throughout temperate regions of the
northern hemisphere (Table 1). This distribution does not, however,
entirely coincide with the occurrence of the diseases they transmit. For
example, even the most widely distributed zoonosis, Lyme borreliosis, does
not occur in the southern states of the USA or in southern parts of
Europe. Other diseases such as tick-borne encephalitis and murine
babesiosis are even more restricted in their distribution, which may be
due to the complexities of transmission dynamics in different areas and/or
to variations in pathogenicity of the agents themselves.
Table 1. Zoonotic pathogens transmitted by ticks of the
Ixodes ricinus species complex.
|
Tick species |
Geographical area |
Pathogens |
|
Ixodes pacificus |
western North America |
Borrelia burgdorferi s.l. Ehrlichia ? |
|
Ixodes persulcatus |
Russia, temperate Asia |
Borrelia burgdorferi s.l.
Ehrlichia?
TBE virus |
|
Ixodes ricinus |
Europe |
Babesia divergens
Babesia microti?
Borrelia burgdorferi s.l.
Ehrlichia (phagocytophila?)
TBE virus |
|
Ixodes scapularis |
eastern North America |
Babesia microti
Borrelia burgdorferi s.l.
Ehrlichia (phagocytophila?)
Powassan virus |
|
The basic life cycles of the four tick species primarily involved in
the transmission of these zoonoses are very similar and, unless otherwise
stated, the following account refers to the European tick, Ixodes
ricinus.
The three instars, larva, nymph and adult, each climb the vegetation in
order to attach to a passing host. Once on the host the tick crawls to a
feeding predilection site where it slits the skin with scalpel-like
mouthparts (chelicerae) and inserts a barbed proboscis (hypostome) that
together with cement secreted by the salivary glands, anchors the tick
firmly in place. The tick remains in place for several days (larva, 2–3
days; nymph, 4–5 days; adult female, 7–9 days) during which time
active growth of gut and cuticle occurs in order to accommodate the
enormous blood meal, most of which will be acquired in the final 24 hours
of engorgement. The adult male rarely feeds and never engorges. The tick
does not neatly pierce blood vessels but creates a feeding pool by
secreting vasoactive mediators and immunomodulators (Grubhoffer, 1999)
that keep the blood flowing and suppress host attempts to resist the
process. During feeding the blood meal is concentrated by the extraction
of water which is then secreted back into the host by specialised salivary
gland cells and is an important means by which tick-borne pathogens invade
their hosts. Once fully engorged the tick withdraws its hypostome and
tumbles to the ground where it begins digesting the blood meal and
developing to the next instar. The digestive process consists of
pinocytosis (microphagocytosis) and endocytosis of blood components by
cells lining the gut, followed by intracellular digestion rather than
intralumenal enzymic digestion as occurs in most other haematophagous
arthropods. The lack of digestive enzymes in the tick gut favours the
survival of ingested microorganisms and may explain why ticks transmit a
greater variety of pathogens than any other group of arthropods
(Sonenshine, 1991). Digestion is slow, and development of the new instar
takes several months in the temperate regions inhabited by these ticks.
The newly moulted (or hatched) unfed tick may remain quiescent for a time
but will eventually ascend the vegetation to quest for another blood meal.
In I. ricinus a full year may separate the active feeding periods of
successive instars.
Tick habitats
The free-living stages of these Ixodes ticks are very sensitive to
desiccation and cannot survive relative humidities of less than 80% for
any length of time. This requirement restricts the ticks to habitats in
which humidity at the base of vegetation rarely falls below 85% RH, even
at the height of summer. Unfed ticks and those that have recently engorged
can acquire water from humid air by ingestion of hygroscopic material
secreted by the salivary glands (Kahl & Knülle, 1988). This
capability enables the unfed stages to make host-seeking excursions into
the upper vegetation where they can lie in wait for hosts for several days
before having to descend to the vegetation base in order to rehydrate.
Ticks may occur in open areas where there is high rainfall and dense
vegetation, such as rough hill-land in the UK and Ireland, and where the
main hosts for all instars are usually sheep, cattle or deer. More typical
habitats for I. ricinus and other members of the species complex
throughout their ranges are deciduous and mixed woodlands, that generally
provide the conditions for the free-living phases of the life-cycle and
usually also harbour a diverse array of tick hosts.
Host specificity
The three instars tend to occur in different proportions on different
hosts. In most regions larvae feed most readily on rodents, nymphs on
birds and medium-sized mammals, and adults on large hosts, such as deer.
The different instars quest at different heights in the vegetation (Gigon,
1985, Mejlon & Jaenson, 1997), apparently in response to desiccation
stress (Randolph & Storey, 1999). This stratified occurrence in the
vegetation probably makes a major contribution to instar host specificity,
but attachment and feeding preferences are also likely to play a part
(Nilsson & Lundquist, 1978). As a result of the wide variety of hosts
present in woodland, ticks in this habitat may serve as vectors of several
pathogens, some of which cause human disease. All instars of I. ricinus
bite humans, but the few studies on this aspect indicate that nymphs are
involved more often than either larvae or adult females (Table 2).
Table 2. Proportions of Ixodes ricinus instars infesting
humans.
|
Country |
Data source |
Total ticks |
Percent larvae |
Percent nymphs |
Percent adult females |
Reference |
|
UK |
Local clinic |
481 |
14.8 |
82.1 |
3.1 |
Robertson et al, 2000 |
|
SW Germany |
General practitioners |
556
|
2.9 |
55.6 |
43.9 |
Maiwald et al, 1998 |
|
Germany (throughout) |
General practitioners, paediatricians,
patients |
2,967 |
7.9 |
70.2 |
21.9 |
Liebisch & Liebisch, 1996 |
The relative abundance and distribution of nymphs are partly
responsible for these statistics, but it is also probable that nymphs are
more likely to attach to human skin than are larvae or adult females.
However, it is interesting to note that the data from south-west Germany
show a much greater proportion of bites caused by adult females than in
the UK study. This may be due to sampling bias (general practitioner data
compared with data from an on-site clinic in a recreation area), but it is
also possible that differences exist in the aggressiveness of different I.
ricinus populations to humans. Epidemiological evidence suggests that
nymphs of I. scapularis and I. pacificus are also the instar most
responsible for human tick bites (Clover & Lane 1995; Falco et al,
1999). Thus nymphs are apparently responsible for most cases of zoonotic
disease that these three species transmit (LB, ehrlichiosis, TBE, murine
babesiosis). In contrast I. persulcatus nymphs rarely bite humans, and
where I. persulcatus transmits LB and TBE most cases are caused by adult
females (Korenberg, 1994).
Regulation of seasonal activity
In order to acquire a host, ticks climb to vantage points in the
vegetation and are particularly vulnerable to desiccation during this
phase of their life cycle. They can rehydrate by descending to the humid
base of the vegetation, but this costs energy and most species appear to
time their host-seeking activity to avoid dry or cold periods of the year.
In the majority of habitats host-seeking activity is most intense in
spring and early summer, with relatively little activity in mid-summer. In
some areas a second, usually lower peak of activity, occurs in autumn.
This basic pattern is subject to considerable variation, even within local
areas, due to the influence of host availability and macro- and
microclimate effects (Gray, 1991). For diseases such as bovine babesiosis
that can be easily diagnosed and recorded, the seasonal nature of disease
transmission by I. ricinus is readily apparent (Fig. 1.).

Appreciable experimental and field evidence is now available to suggest
that ticks make use of diapause mechanisms to regulate these periods of
host-seeking activity (Belozerov, 1982). The use of diapause can be viewed
as a "strategic" approach by ticks responding to appropriate
seasonal cues to ensure that host-seeking activity occurs at favourable
times of the year. For example, in I. ricinus a behavioural diapause,
manifesting as quiescence of newly moulted unfed stages, occurs in ticks
conditioned in the previous instar by a long-day photoperiod, and this
tends to delay questing until the spring of the following year. Another
form of diapause, arrested development (morphogenetic diapause), occurs in
eggs, engorged larvae and engorged nymphs and is stimulated by decreasing
day length perceived by unfed and feeding ticks that acquire hosts in
autumn. This morphogenetic diapause prevents ticks from commencing
development in early winter and delays the appearance of the unfed
questing stages until after mid-summer. In areas where a significant
proportion of the tick population utilizes both forms of diapause, two
separate cohorts occur, one feeding in spring and the other (usually
smaller) in autumn, with significant interchange occurring between the two
(Gray, 1991). Similar diapause mechanisms have been identified in the
related species I. scapularis (Yuval & Spielman, 1990) and I. persulcatus (Belozerov, 1982) though there are also minor differences.
I.
persulcatus displays a more strongly developed behavioural diapause
(Kheisin et al, 1955 cited by Balashov, 1972) suggesting that this species
is adapted to long harsh winters. In contrast behavioural diapause appears
to be entirely absent in I. scapularis, indicating a southern origin for
this species, as originally suggested by McEnroe (1984) and supported by
recent work on genetic diversity (Norris et al, 1996). Most aspects of the
seasonal activity of I. ricinus can also be explained by
"tactical" responses of ticks to such ambient conditions as
temperature and humidity (van Es et al, 1999; Jensen, 2000; Perret et al,
2000). Such responses constitute the "fine-tuning" of seasonal
activity regulation and may be the dominant regulatory process in some
tick populations. However, in the absence of studies on development under
natural or quasi-natural conditions regulation of seasonal activity by
underlying diapause mechanisms cannot be ruled out.
Population variations
It is probable that populations of I. ricinus differ in their
propensity to undergo diapause, which may explain variations in results
obtained by investigators of this topic. Such differences particularly
apply to behavioural diapause, which although well documented in some
metastriate ticks (Sonenshine, 1993) appears to be less obvious in I.
ricinus, and may, in some regions, be more of a temperature-induced
quiescence. There may be regional differences in other aspects of the
biology of I. ricinus and although few studies have been conducted so far,
there are some indications that differences exist that may affect disease
transmission. For example, it is possible that there are regional
differences in the readiness of adult female I. ricinus to bite humans
(referred to above). There are also data suggesting that a greater
proportion of the nymphal I. ricinus population feeds on wood mice
(Apodemus sylvaticus) in some European regions than in others (Table 3).
Table 3. Regional differences in I. ricinus larva/nymph
ratios on wood mice (Apodemus sylvaticus)
|
Country |
Mouse numbers |
Mean larvae per mouse |
Larva: nymph ratio |
Percent Bb infection in mice |
Percent Bb infection in questing nymphs |
Reference |
|
Netherlands |
106 |
3.4 |
5 : 1 |
38
|
12.7 |
de Boer et al, 1993 |
|
Switzerland |
60 |
6.0 |
20 : 1 |
44 |
23.8 |
Humair et al, 1999 |
|
Germany |
78 |
4.5 |
147 : 1 |
27.3 (serology) |
10.8 |
Kurtenbach et al, 1995 |
|
Ireland |
306 |
2.1 |
649 : 1 |
3.5 |
12.2 |
Gray et al, 1999 |
These differences in nymphal infestations may be partly due to habitat
characteristics such as air humidity, which affects the questing height of
larvae and nymphs (Randolph & Storey, 2000). However, though they were
abundant at ground level, nymphs were rarely found on rodents in several
Irish woodland habitats (Gray et al, 1999). Since rodents are regarded as
important reservoir hosts of several zoonotic pathogens, such differences
in nymphal infestations could have profound implications for disease
transmission and it is interesting to note in Table 3 that the larva:nymph
ratios are inversely related to the proportion of B. burgdorferi-infected
wood mice in the same biotopes. These data indicate that nymphs are
primarily responsible for transmitting B. burgdorferi s.l. to rodents and
differences in nymphal infestations of these reservoir hosts may influence
the regional prevalence of the pathogen. For example, infrequent nymphal
infestation of rodents has been suggested as a possible reason for the low
prevalence of B. afzelii in parts of Ireland (Gray et al, 2000).
Variations in susceptibility of different tick populations to tick-borne
pathogens may also occur. For example, in a study on the susceptibility to
B. afzelii of larvae derived from Spanish, Irish and German I. ricinus
females it was apparent that the Spanish ticks were more susceptible
(though B. afzelii does not occur in Spain) than either German or Irish
I. ricinus (Estrada-Peña et al, 1998). Surprisingly, the German ticks were
the least susceptible to this German B. afzelii strain, which was from the
same region. Regional differences in the epidemiology of tick-borne
diseases are often explained in terms of pathogen behaviour, but these
studies suggest that more attention should be given to variations in tick
populations. Few attempts have been made to determine intraspecific
taxonomic markers in ticks. However, a recent study on cuticular
hydrocarbons, which can be useful markers for insect taxonomy, showed the
existence of at least 10 distinct I. ricinus groups and a geographical
pattern in their distribution (Estrada-Peña et al, 1996). This is in
general agreement with an unpublished study of genetic variation of I.
ricinus based on analysis of 16S mitochondrial rDNA (Ames et al), which
concluded that there is significant intraspecific diversity in I. ricinus
from different countries, but that genetic variation within countries is
negligible. A similar study on the population genetics of I. scapularis
in
the USA (Norris et al, 1996) suggested that this species occurs as two
clades and their conclusions also support the view (cited above, McEnroe,
1984) that I. scapularis arose in the south. Further research is necessary
on the comparative biology of tick populations discriminated by phenotypic
and DNA criteria.
Tick abundance
Identification of the factors that determine tick abundance and
quantification of their importance is necessary if there is to be any
understanding of spatial and temporal differences in questing tick
population densities. Tick abundance in any particular habitat is
determined by factors such as vegetation cover, climate and weather, which
affect the survival and development of the free-living phases, and by the
success of host acquisition and feeding by the parasitic phases. The
free-living phases are highly dependent on the year-round availability of
a humid microclimate and adequate temperatures for development. The
optimal habitats in these respects are deciduous woodlands in temperate
climates, and such woodlands usually harbour diverse and numerous hosts so
that the immature tick instars are rarely limited in their feeding
opportunities. However, the adult ticks require large mammals such as deer
to feed successfully and produce the next generation, and there are now
ample data to suggest that the availability of such hosts has a major
impact on the population density of ticks within tick-permissive habitats
(Wilson et al, 1984, 1990; Gray et al, 1992; Deblinger et al, 1993). Where
the habitat is especially favourable for the free-living phases of the
tick life cycle, relatively small numbers of deer can maintain very large
tick populations (Robertson et al, 2000). An understanding of the factors
that determine the density of tick populations has predictive value for
the effects of such phenomena as climate change. In a recent study in
Sweden the northward expansion and increased density of I. ricinus between
the 1980s and 1990s, resulting in increased incidence of TBE, was examined
by Lindgren et al. (2000) and they concluded that these changes were
related to warmer winter temperatures. Such a temperature rise could boost
tick densities and distribution in several different ways, including
longer periods for tick development, increased vegetation growth thus
extending tick-permissive habitats, increased host acquisition
opportunities in autumn and winter, and better wintering of the main host
for adult ticks, the roe deer (Capreolus capreolus). Additionally, roe
deer populations in Sweden are thought to have increased in the mid-1980s
as a result of reduced predation following a scabies outbreak in the fox
population. This study illustrates the complex dynamics underlying
tick-transmitted zoonoses and the value of developing good mathematical
models for their analysis. It is increasingly evident that a sound
knowledge of the biological processes involved in the transmission of
these diseases is vital for an understanding of their eco-epidemiology and
the full exploitation of predictive models.
References
-
Balashov YS. 1972. Blood sucking ticks (Ixodoidea) - vectors
of diseases of man and animals. Translation 500, Medical Zoology
Department USNMR Unit 3, Cairo, Egypt.
-
Belozerov VN. 1982. Diapause and biological rhythms in ticks.
In: Physiology of ticks, F. D. Obenchain and R. Galun (eds) pp
469-500, Pergamon Press, Oxford.
-
Clover JR; Lane RS. 1995. Evidence implicating nymphal Ixodes
pacificus (Acari: Ixodidae) in the epidemiology of Lyme disease in
California. Am J Trop Med Hyg 53: 237-240.
-
Deblinger RD, Wilson ML, Rimmer DW, Spielman A. 1993. Reduced
abundance of immature Ixodes dammini (Acari: Ixodidae) following
incremental removal of deer. J Med Entomol 30: 44-50
-
de Boer R, Hovius KE, Nohlmans MKE, Gray JS. 1993. The
woodmouse (Apodemus sylvaticus) as a reservoir of tick-transmitted
spirochaetes (Borrelia burgdorferi) in the Netherlands. Zent bl
Bakteriol, 279: 404-416.
-
Estrada-Peña A, Daniel M, Frandsen F, Gern L., Gettinby G, Gray
JS, Jaenson TGT, Jongejan F, Kahl O, Korenberg E, Mehl R, Nuttall. P. 1998.
Ixodes ricinus strains in Europe Zbl Bakt-Int J Med M 287: 185-189
-
Estrada-Peña A, Gray JS, Kahl O. 1996. Variability in
cuticular hydrocarbons and phenotypic discrimination of Ixodes ricinus
populations (Acarina: Ixodidae) from Europe. Exp Appl. Acarol 20:
457-467.
-
Falco RC, McKenna DF, Daniels TJ, et al. 1999. Temporal
relation between Ixodes scapularis abundance and risk for Lyme disease
associated with erythema migrans. Am J Epidemiol: 149: 771-776.
-
Gigon F. 1985. Biologie d'Ixodes ricinusL. sur le Plateau
Suisse - une contribution à l'écologie de ce vecteur. PhD
dissertation, Université de Neuchâtel
-
Gray JS. 1991. The development and seasonal activity of the
tick, Ixodes ricinus: a vector of Lyme borreliosis. Rev Med Vet
Entomol 79: 323-333.
-
Gray JS, Kahl O, Janetzki C, Stein J. 1992. Studies on the
ecology of Lyme disease in a deer forest in County Galway, Ireland. J
Med Entomol 29: 915-920.
-
Gray J S, Kirstein F, Robertson JN, Stein J, Kahl O. 1999.
Borrelia burgdorferi s.l. in Ixodes ricinus ticks and rodents in a
recreational park in south-western Ireland. Exp Appl Acarol 23:
717-729.
-
Gray JS, Robertson JN, Key S. 2000. Limited role of rodents
as reservoirs of Borrelia burgdorferi sensu lato in Ireland. Eur J
Epidemiol 16: 101-103.
-
Gray JS, Fitzgerald E, Strickland KL. 1983. Prevalence of
clinical babesiosis in an area in north Co. Meath, Ireland. Vet Rec 3:
537-539.
-
Humair PF, Rais O, Gern L 1999. Transmission of Borrelia
afzelii from Apodemus mice and Clethrionomys voles to Ixodes ricinus
ticks: differential transmission pattern and overwintering
maintenance. Parasitology 118: 33-42
-
Jensen PM. 2000. Host seeking activity of Ixodes ricinus
ticks based on daily consecutive flagging samples Exp Appl Acarol 24:
695-708.
-
Kahl O, Knülle W. 1988. Water vapour uptake from
subsaturated atmosphere by engorged immature ixodid ticks. Exp Appl
Acarol 4: 73-88.
-
Korenberg, E.I. 1994 Comparative ecology and epidemiology of Lyme
disease and tick-borne encephalitis in the former Soviet Union.
Parasitology Today, 10: 157-160.
-
Kurtenbach K, Kampen H, Dizij A, et al. 1995 Infestation of
rodents with larval Ixodes-ricinus (Acari, Ixodidae) is an important
factor in the transmission cycle of Borrelia burgdorferi sl in German
woodlands. J Med Entomol. 32: 807-817.
-
Liebisch A, Liebisch G. 1996. Hard ticks (Ixodidae) biting
humans in Germany and their infection with Borrelia burgdorferi. In:
Mitchell R, Horn DJ, Needham GR, Welbourne C (eds) Acarology IX Vol 1
: Proceedings , 1996; The Ohio Biological Survey: 465-468
-
Lindgren E, Tälleklint L, Polfeldt T. 2000. Impact of
climatic change on the northern latitude limit and population density
of the disease-transmitting European tick Ixodes ricinus. Environ
Health Persp 108: 119-123.
-
Maiwald M, Oehme R, March O, et al. 1998. Transmission risk
of Borrelia burgdorferi sensu lato from Ixodes ricinus ticks to humans
in southwest Germany. Epidemiol Infect 121: 103-108
-
McEnroe WD. 1984. Winter survival and spring breeding by the
fall tick, Ixodes dammini, in Massachussetts (Acarina: Ixodidae)
Acarologia, XXV: 223-229.
-
Mejlon HA, Jaenson TGT. 1997. Questing behaviour of Ixodes
ricinus ticks (Acari: Ixodidae) Exp Appl Acarol 21: 747-754.
-
Nilsson A, Lundquist L. (1978). Host selection and movements
of Ixodes ricinus (Acari) larvae on small mammals. Oikos 31: 313-322.
Norris DE, Klompen JSH, Black WC. 1999. Comparison of the
mitochondrial 12S and 16S ribosomal DNA genes in resolving
phylogenetic relationships among hard ticks (Acari : Ixodidae) Ann
Entomol Soc Am 92: 117-129.
-
Perret JL, Guigoz E, Rais O, Gern, L. 2000. Influence of
saturation deficit and temperature on Ixodes ricinus tick questing
activity in a Lyme borreliosis-endemic area (Switzerland) Parasitol
Res 86: 554-557.
-
Randolph SE, Storey K. 1999. Impact of microclimate on
immature tick-rodent host interactions (Acari: Ixodidae): implications
for parasite transmission. J Med Entomol 36: 741-8.
-
Robertson JN, Gray JS, Stewart P. 2000. Tick bite and Lyme
borreliosis risk at a recreational site in England. Eur J Epidemiol
16: 647-652.
-
Sonenshine DE. 1991. Biology of ticks. Vol 1. Oxford
University Press.
-
Sonenshine DE. 1993. Biology of ticks. Vol 2. Oxford
University Press.
-
van Es RP, Gettinby G, Hillerton JE. 1999. Models of temporal
variation in questing activity in individuals of Ixodes ricinus (Acari
: Ixodidae) Exp Appl Acarol 23: 977-986.
-
Wilson ML, Levine JF, Spielman A. 1984. Effect of deer
reduction on abundance of the deer tick (Ixodes dammini). Yale J Biol
Med 57: 697-705.
-
Wilson ML, Litwin TS, Gavin TA, Capkanis MC, Maclean DC, Spielman
A. 1990. Host-dependent differences in feeding and reproduction of
Ixodes dammini (Acari: Ixodidae). J Med Entomol 27: 945-54.
-
Yuval B, Spielman A. 1990. Duration and regulation of the
developmental cycle of Ixodes dammini (Acari: Ixodidae). J Med Entomol
27: 196-201
Part of the proceedings of the symposium Current
Research on Tick-Borne Infections, Kalmar, Sweden, March 28–30, 2001. ©
2001, J. S. Gray, Department of Environmental Resource Management,
University College Dublin, Ireland.
|
Feedback And Comments
|
Please enter a comment or feedback.
|
|
|
CRTBI - Extended Abstracts
Bunikis J et al.: Structure and Function of the Surface Proteins of Borrelia Spirochetes
Dambrauskienè V et al.: Epidemiology of Tick-Born Encephalitis and it's Clinical Manifestations in
Panevèzys City County
Egenvall A et al.: A serosurvey of granulocytic Ehrlicha spp. and Borrelia burgdorferi sensu lato
in 2018 Swedish horses
Gray J S et al.: The biology of Ixodes ticks, with special reference to Ixodes ricinus
Guillaume B et al.: Human Granulocytic Ehrlichia Infection in Belgium
Haglund M et al.: Tick-borne encephalitis (TBE) - an overview
Larsen K et al.: Tick species and arthropod-transmitted infections from Danish cats and dogs
Lundkvist Å et al.: Characterization of Tick-borne enchephalitis virus from Latvia – evidence for co-circulation of three distinct subtypes
Malmgren L et al.: A field trial of the effectiveness of 65% permetrin spot-on and 9.7% fipronil spot-on against ticks (Ixodes ricinus) on dogs
Massung R F et al.: Genetic Variants of Ehrlichia phagocytophila in the United States
Nilsson I et al.: Serological evidence of Lyme arthritis in Egypt
Nyman D et al.: Ticks have preferences in choosing human hosts
Ornstein K et al.: Quantification of spirochete burden in Borrelia burgdorferi infected ticks fed on OspA immunized mice by 16S rRNA RT real-time PCR
Randolph S et al.: Epidemiological consequences of tick ecology
Skarpaas T et al.: Tick-borne encephalitis in Norway
Soutschek E et al.: A defined mixture of recombinant antigens from several Borrelia genospecies improves serodiagnosis of Lyme disease
von Stedingk L V et al.: Recent research on human babesiosis – the Scandinavian perspective
Stuen S et al.: Granulocytic Ehrlichia infection in domestic and wild ruminants in Norway
Widhe M et al.: Cytokines in Lyme Borreliosis: in vivo levels of TGF-b1, TNF-a and IL-6 in serum and cerebrospinal fluid from patients with neuroborreliosis or erythema migrans in relation to clinical outcome |