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Bioecological notes on Xylosandrus compactus (Eichhoff) (Coleoptera Curculionidae Scolytinae), a species recently recorded into Italy

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  • C.R.E.A.-ABP Consiglio per la Ricerca in agricoltura e l'analisi dell'economia agraria (CREA) Centro di ricerca per l' AgroBiologia e Pedologia (ABP) Florence (italy)

Abstract and Figures

Intense trade flows favour the accidental diffusion of alien plant and animal species harmful to agricultural crops and forest ecosystems in many parts of the world. Particularly prone to such introductions are lignicolous species of woodboring beetles that attack living plants and can develop in lumber or crating wood, such as many species belonging to the subfamilies Scolytinae and Platypodinae (Coleoptera: Curculionidae). Investigations of marked witherings of laurel twigs (Laurus nobilis L.) carried out from autumn 2010 in an area of the Versilia coast (Lucca) revealed that the Black twig borer, Xylosandrus compactus (Eichhoff), was involved in this pathological expression. This species was recently recorded for the first time in Italy on ornamental plants in some localities in the Naples's province. Here we report its essential external morphological features, with useful characters for its distinction from X. germanus (Blandford), a morphologically similar species, as well as its essential bioecological features, with special reference to what has been observed in the abovementioned area of Tuscany. This should facilitate the rapid identification and verification of new outbreaks and, where possible, the timely implementation of control strategies.
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REDIA, XCV, 2012: 67-77
(*) Consiglio per la ricerca e la sperimentazione in agricoltura, Research Centre for Agrobiology and Pedology, Via Lanciola n. 12/A,
50125 Firenze, Italy; e-mail: fabrizio.pennacchio@entecra.it.
(**) Via M. Buonarroti, 54 - Lido di Camaiore (Lucca), Italy.
Pennacchio F., Santini L., Francardi V. – Bioecological notes on Xylosandrus compactus (Eichhoff) (Coleoptera
Curculionidae Scolytinae), a species recently recorded into Italy.
Intense trade flows favour the accidental diffusion of alien plant and animal species harmful to agricultural crops
and forest ecosystems in many parts of the world. Particularly prone to such introductions are lignicolous species of wood-
boring beetles that attack living plants and can develop in lumber or crating wood, such as many species belonging to the
subfamilies Scolytinae and Platypodinae (Coleoptera: Curculionidae). Investigations of marked witherings of laurel twigs
(Laurus nobilis L.) carried out from autumn 2010 in an area of the Versilia coast (Lucca) revealed that the Black twig borer,
Xylosandrus compactus (Eichhoff), was involved in this pathological expression. This species was recently recorded for the
first time in Italy on ornamental plants in some localities in the Naples’s province. Here we report its essential external
morphological features, with useful characters for its distinction from X. germanus (Blandford), a morphologically similar
species, as well as its essential bioecological features, with special reference to what has been observed in the above-
mentioned area of Tuscany. This should facilitate the rapid identification and verification of new outbreaks and, where
possible, the timely implementation of control strategies.
KEY WORDS: Black twig borer, insect pest introduction, Laurus nobilis.
FABRIZIO PENNACCHIO (*) - LUCIANO SANTINI (**) - VALERIA FRANCARDI (*)
BIOECOLOGICAL NOTES ON XYLOSANDRUS COMPACTUS (EICHHOFF)
(COLEOPTERA CURCULIONIDAE SCOLYTINAE), A SPECIES RECENTLY
RECORDED INTO ITALY (1)
INTRODUCTION
The intense flow of goods affecting today’s global
market, in particular the intense trade in products from the
Far East, has led to an increase in accidental introductions
of plant and animal species harmful to crops and forest
ecosystems in various parts of the world (PELLIZZARI and
DALLA MONTÀ, 1997; HAACK, 2003, 2006). Particularly
prone to such introductions are wood-boring beetles that
complete their development in the inner parts of trunks,
branches and twigs of living plants and in lumber or
crating wood. These include lignicolous or xylomy -
cetophagous species belonging to the subfamilies
Scolytinae and Platypodinae (Coleoptera Curculionidae)
more than corticicolous or phloeophagous species which
are generally more easy to control through simple
debarking of the material. Moreover, during phytosanitary
inspections of imported lumber in ports, airports, freight
terminals, etc., it is more difficult to identify material
infested by lignicolous or xylomy cetophagous beetles than
that colonized by corticicolous beetles (HAACK, 2003;
RABAGLIA et al., 2006; KIRKENDALL and FACCOLI, 2010). In
North America, 22 of the 45 wood-boring species present
were introduced from different parts of the world
(RABAGLIA et al., 2006, 2009, 2010; OKINS and THOMAS,
2009). In Europe, 12 of the 19 species of bark beetles of
more or less recent introduction, including the two
– Received 31 October 2012 Accepted 10 November 2012 Published 4 December 2012
1 This study was carried out as part of the Project “Strateco-
Phitosanitary Emergences: Containment Strategies” D.M
30290/7303/09.
spermophagous species Coccotrypes dactyliperda (Fabricius)
and Dactylotrypes longicollis (Wollaston), are
xylomycetophagous (KIRKENDALL and FACCOLI, 2010). In
recent years, several species of exotic bark beetles (largely
lignicolous ones) have been identified in Italy, such as
Gnathotrichus materiarius (Fitch) (FACCOLI, 1998), Xylo -
sandrus germanus (Blandford) (ZANDIGIACOMO et al., 1998;
STERGULC et al., 1999), X. crassiusculus (Motschul sky)
(PENNACCHIO et al., 2003), Monarthrum mali (Fitch)
(KIRKENDALL et al., 2008), Ambrosiophilus atratus
(Eichhoff) (FACCOLI, 2008), Ambrosiodmus rubricollis
(Eichhoff) (FACCOLI et al., 2009) and Megaplatypus mutatus
(Chapuis) (TREMBLAY et al., 2000). To these we must add
two phloeophagous species: Phloeosinus armatus Raitter
(COVASSI, 1991) and Phloeotribus liminaris (Harris)
(PENNACCHIO et al., 2004).
Still in progress investigation of the causes of marked
and widespread witherings of the more or less thin
branches of laurel (Laurus nobilis L.) carried out from
autumn 2010 in a relatively small area of the Versilia coast
included in the municipalities of Lido di Camaiore,
Pietrasanta, Forte dei Marmi (Province of Lucca) and, only
for few isolated locations, in those of Montignoso and
Massa (Province of Massa-Carrara) revealed that the black
twig borer X. compactus (Eichhoff) was involved to some
extent in the aforementioned unusual phytopathology. This
species was recently recorded for the first time in Italy, by
the Phytopathological Laboratory of the Phytosanitary
Service of the Campania Region, on ornamental plants in
some localities of the province of Naples, such as Gussone
Park in Portici and the park of Capodimonte (FITOLAB,
2011a, 2011b). Shortly thereafter, it was recorded by us for
the province of Lucca (FRANCARDI et al., 2012).
In the present note, we report the essential features of
the external morphology and biology of X. compactus on
the basis of previous literature data and our investigations
carried out in the above-mentioned area of Tuscany in
2010-2012. This should facilitate the rapid identification
and verification of new outbreaks and, where possible,
allow for the adequate planning and timely implemen -
tation of control measures.
SPECIMENS EXAMINED
Many females and a male were found within the maternal
galleries in different localities in the municipalities of Lido
di Camaiore, Marina di Pietrasanta and Forte dei Marmi
(Lucca) between October 2010 and October 2012.
DISTRIBUTION
The native distribution area of X. compactus is probably
tropical and subtropical Southeast Asia (India, Sri Lanka,
Indochina, China, Indonesian Archipelago, Micronesia,
Philippines, Japan), from where it has been introduced
into many parts of the world. To date, its presence is
established for much of Africa, where it is widespread,
probably introduced several centuries ago during the first
trading missions. The species is recorded from Mauritania,
Sierra Leone, Liberia, Ivory Coast, Ghana, Nigeria, Came -
roon, Equatorial Guinea, Gabon, Republic of Congo,
Democratic Republic of Congo, Uganda, Kenya, Tanzania,
South Africa, as well as from the Indian Ocean islands
(Madagascar, Seychelles, Mauritius, Comoros, Reunion).
In North America, to which it was probably introduced in
the first half of the 20th century, it is now widespread in the
south-eastern states of the USA (Florida, Georgia,
Louisiana, Mississippi, Texas, North and South Carolina).
In Latin America, it is present in Brazil, Peru and the
Caribbean islands (Cuba and the Antilles). It is also
recorded from New Caledonia, New Zealand, Hawaii,
Samoa and Fiji (SCHEDL, 1962; BEAVER, 1976; WOOD
1977, 1980, 1982; SAMUELSON, 1981; CHAPIN and OLIVER,
1986; DEYRUP and ATKINSON, 1987; WOOD and BRIGHT,
1992; DELGADO and COUTURIER, 2010, 2012).
ADULT MORPHOLOGY
FEMALE – Body stout, cylindrical, dark brown or black,
shiny, with a length between 1.4 and 1.9 mm, length/width
ratio 2.1. Antennae with funicle consisting of 5 articles and
club obliquely truncated. Pronotum with length/width
ratio 0.94-0.95. Anterior margin armed with 6-10, most
commonly 6-8, rather coarse denticles. Elytra 1.2 times as
long as wide. Elytral slope with regularly arcuate profile,
striae with short but distinct rows of setolae, interstriae
with clearly longer rows of setolae (Fig. I, 1 and 2; Fig. II, 1
and 2).
MALE – very rare, apterous and haploid, much smaller
than the female (0.8-1.1 mm), twice as long as wide.
Pronotum narrowly rounded, flattened or slightly concave
in the median part, anteriorly lacking projecting denticles.
Spicules barely appreciable, almost obsolete. Elytral striae
and interstriae with irregular spotting.
Morphologically, X. compactus presents marked simila -
rities to X. germanus (Blandford). Nevertheless, it can be
distinguished from the latter by its smaller size (the
females of X. germanus measure 2.0-2.3 mm); by the
presence of rows of setolae on both the striae and the
interstriae of the elytral slope (in X. germanus the setolae
along the striae are obsolete or completely absent) and by
the flat interstriae (in X. germanus they are weakly convex)
(Fig. I, 3).
BIOLOGICAL NOTES
Like all representatives of the tribe Xyleborini, X.
compac tus is a xylomycetophagous bark beetle (WOOD,
1982). Its preimaginal development occurs in the pith
tissue of thin twigs of 1-2 years and of the current year
with a diameter between 2.5 and 12 mm; its feeding is
almost exclusively on an ambrosia-type fungus.
The adult female digs the maternal galleries, normally on
the side of the twig facing the ground or in any case on the
less exposed side, starting from an entrance hole of ca. 0.8
mm diameter around which, as also observed by DIXON et
al. (2003), there may be a small amount of loose frass that
tends to disperse in a short time. During the early
excavation phases, the female proceeds orthogonally to the
major axis of the twig, crossing the cortical tissue, the
phloem and xylem, until she reaches the pith. Within the
pith, she digs and later expands (proceeding in the
direction of the twig’s major axis) the true maternal gallery,
the one reserved for larval development, whose diameter
generally corresponds to that of the pith (Fig. III, 1 and 2).
This gallery extends partly beneath but mainly above the
entrance tunnel (see Figs. IV and V). In this micro-envi -
ronment, the female releases the spores of the symbiotic
ambrosia fungus carried by her in a special structure of the
pronotum called the mycangium (LHOSTE and ROCHE,
1959). After the fungal mycelium has began to develop,
the female will release a more or less large group of eggs.
According to ENTWISTLE (1964), unfertilized females and
those that have exhausted the sperm reserve lay eggs that
only produce haploid males by means of facultative
arrhenotokous parthenogenesis.
Egg hatching, occurring 4-6 days after deposition, is
followed by three larval stages and the pupal stage. The
entire cycle lasts from 27 to 40 days depen ding on the
physical and chemical conditions of the host tree and the
climatic conditions (BRADER, 1964; HARA and BRADSLEY,
1979). Throughout this developmental period, the mother
remains with her brood.
The newly emerged adults, whose sex ratio is strongly
biased in favour of females, are initially light brown. With
progressive consolidation of the integumental structures
and maturation of the gonads, the colour turns into a
definitive intense dark brown in 4-5 days (see Fig. III, 3).
Mating can occur from this moment on, taking place
inside the maternal gallery before the young females leave
the twig and disperse. In view of the above-mentioned
values, taken from the literature and based on regular
surveys carried out in Versilia on laurel plants in the period
2010-2012, it is reasonable to assume that, in this area of
recent introduction, the species can complete at least two
generations and the more or less protracted beginning of a
third between the end of April and late November.
Moreover, in this area, the species normally overwinters as
adults, sheltered and inactive inside the maternal galleries
in more or less numerous groups. When young females
leave the maternal gallery and disperse, their active flight is
certainly supported by the wind. Nevertheless, it seems
likely that when they develop on a particularly receptive
68 F. PENNACCHIO ET AL. REDIA, Vol. XCV, 2012
BIOECOLOGICAL NOTES ON XYLOSANDRUS COMPACTUS (EICHHOFF)… 69
host plant (which we found to be laurel in our study area)
they largely tend not to disperse in the air but rather to
remain on the original or nearby host plants and to dig
their own egg galleries in them. This could explain the
massive attacks during a single season which progressively
affect the same plant or the same laurel hedge, as well as
the relative slowness with which outbreaks expand, even
in areas such as Versilia where laurel is very widespread.
X. compactus is a primary phytophaguos which, like
many other xylomycetophagous bark beetles, is largely
poly phagous. Hence, it can cause severe phytosanitary
problems in areas of recent introduction. At present, more
than 220 host plants, belonging to 62 families, are known.
In the presumed native tropical regions and in those of
new introduction, the development of X. compactus occurs
at the expense of economically important plants such as
coffee, tea, mango, avocado, cacao and lychee. Several
other species of economic, ecological and ornamental
importance can be attacked, including those belonging to
the genera Acacia, Acer, Azalea, Celtis, Cornus, Eucalyptus,
Ficus, Hibiscus, Khaya, Liquidambar, Magnolia, Malus,
Ostrya, Platanus, Swietenia and Vitis (NGOAN et al., 1976;
WOOD, 1982; DIXON and WOODRUFF, 1982; MESHRAM et
al., 1993; INTACHAT and KIRTON, 1997; DAEHLER and
DUDLEY, 2002; MATSUMOTO, 2002). Other recorded host
plants in the same environments include perennial
herbaceous species belonging to the families
Orchideaceae, Araceae and Zingiberaceae (HARA and
BRADSLEY, 1979; HARA and SEWAKE, 1990). Additional
lists of host plants for this bark beetle are reported in
Fig. I – Scanning electron microscope (SEM) photos. 1. Xylosandrus compactus (Eichhoff) adult female:
overall appearance. 2. X. compactus: detail of elitral declivity. 3. Xylosandrus germanus (Blandford): detail of
elitral declivity (photo C. Benvenuti).
SCHEDL (1962), BRADER (1964), SAMUELSON (1981), and
WOOD and BRIGHT (1992).
In Italy, X. compactus attacks have been recorded on
laurel, holm oak and viburnum in Campania (cf.
FITOLAB, 2011a). To this can be added the host plants we
recently recorded in Versilia where, in addition to the
greatly preferred laurel, X. compactus also attacks and
develops on many other trees and shrubs such as cherry
laurel, pitto sporum, spindle, strawberry tree, hazelnut,
holm oak, English oak, maple, alder, beech, elm, lime,
sweetgum, tulip tree, magnolia, common dogwood,
pomegranate, azalea, rhododendron, camellia, gardenia,
lemon and olive.
However, despite such a large number of potential
hosts, it seems that only a few of them have the particular
physical and chemical characteristics to support the
development of large X. compactus populations. According
to BRADER (1964), we can state on the basis of our findings
that the different hosts of this bark beetle share the
following characters: small diameter of the woody twigs in
which the maternal gallery is dug, absence of pubescence
of the outer surface of the twigs and no emission of gum,
latex or other liquids from the wound produced by the
bark beetle when digging the gallery.
DAMAGES
In many areas of new introduction, X. compactus has
shown marked aggressiveness towards plants in apparently
good vegetative conditions, often leading to significant
economic losses (LAVABRE, 1958, 1959; SAMUELSON, 1981;
RAMESH 1987; EGONYU et al., 2009). Among the many
described cases, it should be noted that very intense attacks
on even young plants of Castanea sp. were observed in
China (Yan et al., 2001), while in Hawaii (ZIEGLER, 2001,
2002) there have been X. compactus attacks against rare
native species threatened with extinction (Colubrina
oppositifolia and Caesalpinia kavaien sis); hence, this beetle
is now a serious threat to the survival and biodiversity of
the natural ecosystems of these islands.
The attacks cause the desiccation of a more or less con -
spi cuous part of the thinner branches of the canopy, with
consequent physiological damage for the entire plant. As a
70 F. PENNACCHIO ET AL. REDIA, Vol. XCV, 2012
Fig. II – Xylosandrus compactus (Eichhoff). 1. Overall appearance of an adult female. 2.
Group of adults in a maternal gallery (photo P. Giannotti).
result production losses may occur in both agricul tural
and forest ecosystems, as well as significant aesthetic
damage of many ornamental plants (Fig. VI, 1 and 2)
(NELSON and DAVIS, 1972; RAMESH, 1987; WATERHOUSE,
1997; DELGADO and COUTURIER, 2010, 2012).
In laurel (in which the symptoms of the attack are always
particularly evident) and in all other host plants examined
by us, the damage appeared within 7-10 days, according to
the following successive stages. A blackish colouration
appeared rapidly on the outer surface of the twig in the
area closely adjacent to the entrance tunnel. Within a few
days, the blackening of the external tissues involved not
only a short inferior tract but also the entire part of the twig
superior to the entrance hole with contemporary rapid
necrosis and desiccation of the same sprig (Fig. VI, 1).
Most Authors attribute the damage caused by X.
compactus to the mechanical action of digging the maternal
galleries by the females in the tissues of living twigs and
shortly thereafter to the presumed pathogenicity of the
symbiotic ambrosia fungi brought in by the bark beetle.
There is no complete agreement on the identity of these
fungi: some Authors argue that it is Fusarium solani
(Mart.) Sacc (NGOAN et al., 1976; HARA and BEARDSLEY,
1979; DAEHLER and DUDLEY, 2002; BAMBARA, 2003;
DIXON et al., 2003), while others report it to be
Ambrosiella xylebori Brader (BRADER, 1964; BHAT and
SREEDHARAN, 1988) or Ambrosiella macrospora (Fr.-
Grossman) Batra (MUTHAPPA and VENKATASUBBAIAH,
1981). Other Authors considered this last fungus
fundamental for the larval feeding but not pathogenic for
the plant (FRANCKE-GROSSMAN, 1952). In any case, it
cannot be excluded that the pathogenicity of the ambrosia
fungus is supported by that of other parasitic fungi (agents
of anthracnose) that penetrate into the tissues through the
wound produced by the bark beetle (BRADER, 1964).
With regard to this issue, preliminary results have been
recently obtained at the Micology lab of the Department
of Agriculture, Food and Environment of the University of
Pisa. Tissues of Laurus nobilis, Acer pseudoplatanus and
Magnolia grandiflora with gellery systems, preovipositional
females and mature larvae of X. compactus, plated on
Potato Dextrose Agar gave rise to colonies of at least six
different sporulating fungi and two mycelia sterilia.
Among the sporulating fungi, Verticillium and Pestalo -
tiopsis have been recorded, and these two genera include
pathogenic species able to induce symptoms (tracheo -
mycoses and twig blight)similar to those observed in field
samples (VANNACCI, 2012, pers. comm.).
BIOECOLOGICAL NOTES ON XYLOSANDRUS COMPACTUS (EICHHOFF)… 71
Fig. III – Xylosandrus compactus (Eichhoff). 1. Group of larvae and pupae in the maternal
gallery. 2. Pupa. 3. Newly emerged adult (photo P. Giannotti).
CONTROL STRATEGIES
Since X. compactus spends much of its life cycle well
protected inside the maternal galleries dug in the most
internal tissues of the host twigs, the application of control
strategies based on synthetic chemical insecticides
normally encounters considerable difficulties, beyond the
limitations due to environmental, ecological and regulatory
concerns. Indeed, results of previous trials from which to
draw useful information to plan rapid, effective control
interventions are scarce and often contradictory (MAN -
GOLD et al., 1977; MIZELL et al., 1998).
Anyway rational approach to the use of insecticides is to
use molecules able to ensure a good contact action and
with good residual power to kill newly emerged females
when they move in the crown of the host plant in search of
suitable points in which to dig their galleries (see:
MANGOLD et al., 1977; YAN et al., 2001; BAMBARA, 2003).
However, to make this type of intervention more effective,
it seems essential to conduct careful monitoring, which can
be carried out with multifunnel traps baited with ethanol
(BURBANO et al., 2012). This can be very useful not only
for rapid assessment of the spread of the insect into new
settlement areas but also to precisely identify the periods
of flight of the females in order to plan the place and
timing of interventions to contain the species (ABREU et al.,
1997, 2012; OLIVER and MANNION, 2001). Although the
use of systemic insecticides might appear to be an effective
technique against such well protected insects, there are
still many doubts about their true usefulness (PEÑA et al.,
2011). This is primarily because the location of the
preimaginal stages and adults means that they are sepa -
rated from the surrounding tissues of the host plant by a
more or less substantial layer of mycelium of the symbiotic
fungus on which they feed, and there is no certainty that it
can incorporate lethal doses of the administered active
principle. Moreover, these forms of the bark beetle are
located, from the beginning of their development, inside
tissues whose normal function might be compromised and
have begun to wither. This withering adversely affects the
72 F. PENNACCHIO ET AL. REDIA, Vol. XCV, 2012
Fig. IV – Xylosandrus compactus (Eichhoff). 1. Laurel twigs (Laurus sp.) with the entrance
hole leading to a maternal gallery. 2. Section showing the development of the same gallery
(photo P. Giannotti).
translocation of the active principle from the sites of
application and absorption.
Furthermore it can not be excluded that the damage can
be determined by the combined presence of exceptional
or abnormal climatic and/or edaphic conditions resonsable
to induce latent suffering in plants. For this reason all
cultivation practices that promote vigor of plants (above all,
land ploughing, balanced fertilization startegies and
emergency irrigation) can be still useful integrative
interventions, not only in order to mitigate the attacks of
this species, but also to promote a good vegetative recovery
of heavely attacked plants (DIXON e WOODRUFF, 1982;
BAMBARA, 2003).
Literature reports suggest a generally low importance
of natural enemies in limiting X. compactus populations,
especially in areas of new introduction. Studies con duc -
ted in Indonesia by LEPELLEY (1968) on the activity of
some parasitoids showed an inconstant efficacy. Howe ver,
some positive results were reported by KEUCHENIUS (1931)
for the island of Sumatra regarding the effects of a
eulophid wasp (Tetrastichus sp.) and a bethylid wasp. With
regard to our Tuscan study area, a larva of X. compactus
with a closely associated larva of a parasitoid was isolated
from a laurel twig from Marina di Pietrasanta in
September 2011. After 12 days, the parasitoid larva
produced a female of the braconid wasp Heterospilus
leptostoma Fischer. This species, not previously recorded
for Italy, belongs to the subfamily Doryctinae, whose
members are known as idiobiotic ectoparasitoids of
endophytic larvae of Lepidoptera, Hymenoptera Ten -
tredinidae and Coleoptera, especially bark beetles (SHAW,
1997; WHARTON et al., 1997) (Fig. VII, 1 and 2). Despite
the faunistic importance of this parasitoids, our exiguous
finding not allow us to make any conclusion of an applied
nature.
CONCLUSIONS
The results of our investigation indicate that wherever
X. compactus has been accidentally introduced it has
become a serious phytosanitary problem in a relatively
BIOECOLOGICAL NOTES ON XYLOSANDRUS COMPACTUS (EICHHOFF)… 73
Fig. V – Xylosandrus compactus (Eichhoff). 1. Olive twigs (Olea sp.) with the entrance hole
leading to a maternal gallery. 2. Development of these galleries (photo P. Giannotti).
short time because of the variety of plants it can attack. The
effects can be negative and economically disastrous for
agricultural and forestry production, especially in the
nursery sector and in the international and inland plant
trade. This is even more worrying on account of the
objective difficulty in adequately controlling the species
with the currently available materials and techniques and
the almost complete absence of previous studies to help
plan truly effective and environmentally friendly contain -
ment measures. Therefore, it is necessary to conduct
further, more extensive studies on the bioecology of this
species and the development of effective techniques to
monitor its infestations.
ACKNOWLEDGEMENTS
The Authors would like to thank Prof. Giovanni Vannac -
ci of the Section Patologia Vegetale of the Department of
Scienze Agrarie, Ambientali e Agroalimentari of the
University of Pisa, well as Dr. Augusto Loni and Mr. Paolo
Giannotti of the Section Entomologia Agraria of the same
Department, respectively for the identification of the
complex of fungi associated in dieback of twigs attacked by
bark beetle, for identification of the parasitoid Heterospilus
leptostoma Fischer and for the realization of most of the
photographs. The Authors are also grateful to the Technical
Assistant Claudia Benvenuti of the CRA ABP of Florence
for the realization of the SEM images and Dr. Alberto
Inghilesi of the Department of di Biologia evoluzionistica
“Leo Pardi” of the University of Florence, for providing
some specimens of X. germanus for comparative
morphological observa tions. We wish to thank the Plant
Protection Service of Tuscany, seat of Pisa, for reporting
some sites infested by X. compactus and provided some
samples for its determination, and Mr. Mario Pardini of the
“Agraria Pardini Giuseppe s.r.l.” of Lido di Camaiore for
the continued cooperation provided during the data
collection in the field.
74 F. PENNACCHIO ET AL. REDIA, Vol. XCV, 2012
Fig. VI – Xylosandrus compactus (Eichhoff). Evident signs of an attack. 1. On a laurel hedge.
2. On the crown of a lime tree (photo L. Santini).
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BIOECOLOGICAL NOTES ON XYLOSANDRUS COMPACTUS (EICHHOFF)… 77
... Argentario on bay laurel, carob (Ceratonia siliqua L.), mastic (Pistacia lentiscus L.), buckthorn (Rhamnus alaternus L.), and butcher's broom (Ruscus aculeatus L.), unpublished data). Populations of X. compactus were also found along the Italian Adriatic coast in a nursery in the Marche Region (Grottammare (Ascoli Piceno) and surroundings) on Olea europaea (Pennacchio et al., 2012, Vitale et al., 2022. The aforementioned reports, together with several other recent ones reporting the range expansion of X. compactus in Italy and other invaded European and/or Mediterranean countries, confirm the beetle ability to attack and develop on plants growing both in anthropized environments, including gardens and parks (urban and peri-urban), and in natural or semi-natural ones, infesting forest trees (i.e., Quercus sp.) and understory shrubs, such as bay laurel, buckthorn, mastic, and butcher's broom (Gugliuzzo et al., 2019a;Leza et al., 2020;Riba-Flinch et al., 2021;Hizal et al., 2023). ...
... Branches and apical twigs of L. nobilis and R. alaternus showing symptoms described by Francardi et al. (2012;2017) and Pennacchio et al. (2012) were found in 2020 in five different localities: three in Tuscany (Villa Salviati, 43°46'08"N -10°19'29"E, Pisa province; Monte Argentario-La Cacciarella, 42°26'23"N -11°06'13"E, Grosseto province; Porto Azzurro-Island of Elba, 42°46'28"N -10°24'35"E, Livorno province), one in Latium (Circeo National Park, 41°23'52"N -12°54'59"E, Latina province), and one in Sicily (Ragusa province, 36°55'07"N -14°43'15"E). These were sites of first recovery or with an abundant presence of the insect. ...
... Branches and apical twigs of L. nobilis and R. alaternus showing symptoms described by Francardi et al. (2012;2017) and Pennacchio et al. (2012) were found in 2020 in five different localities: three in Tuscany (Villa Salviati, 43°46'08"N -10°19'29"E, Pisa province; Monte Argentario-La Cacciarella, 42°26'23"N -11°06'13"E, Grosseto province; Porto Azzurro-Island of Elba, 42°46'28"N -10°24'35"E, Livorno province), one in Latium (Circeo National Park, 41°23'52"N -12°54'59"E, Latina province), and one in Sicily (Ragusa province, 36°55'07"N -14°43'15"E). These were sites of first recovery or with an abundant presence of the insect. ...
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In 2020, surveys were carried out in different locations of Tuscany, Latium, and Sicily (Italy) to detect the presence of Xylosandrus compactus (Heichhoff) and to evaluate the fungal community associated with infestations by this invasive ambrosia beetle. In particular, we aimed to investigate the potential co-occurrence of phytopathogenic species that may pose a risk of spreading within the Mediterranean. Surveys were carried out in five localities where bay laurel (Laurus nobilis L.) plants showed signs of infestation by X. compactus. For the first time in Italy, in one of these surveyed localities, the ambrosia beetle was also consistently found attacking Rhamnus alaternus L., and samples from this host plant were included in the study. We were not interested in the already investigated nutritional mutualists consistently associated with the ambrosia beetle but focused on the potential occurrence of other fungal species inhabiting the body of adult beetles collected from infested galleries. Differences in fungal communities and/or variations in beetle-fungus species-specific associations among locations, as well as among the two host plants investigated are also highlighted. Thirty beetle adults were collected from each sampling site up to a total of 180 individuals including those from R. alaternus. In total, 31 different fungal genera were isolated. Fungal isolates belonging to the genera Geosmithia, Fusarium, Alternaria, Aureobasidium, Cladosporium, and Penicillium were shared by different regions. Differences in the fungal community composition, as well as in the occurrence of some isolated fungal genera, such as potential phytopathogenic ones (i.e., Fusarium, Geosmithia, Thyridium) and/or potential antagonists (i.e., Clonostachys, Aureobasidium, Trichoderma), alongside with opportunistic and/or commensals, were observed among sites and between the two hosts. Moreover, one entomopathogenic fungal species (i.e., Metarhizium brunneum) was found and isolated from beetle individuals infesting R. alaternus. The presence of X. compactus in the Mediterranean maquis of the Island of Elba is reported for the first time. Key Words: ambrosia beetle; black twig borer; Rhamnus alaternus; Geosmithia sp.; Laurus nobilis; Metarhizium sp.; fungal community.
... Among them, Xylosandrus compactus (Eichhoff, 1876) causes damage to shrubs and trees in forests, ornamental gardens, and parks (Garonna et al. 2012;Vannini et al. 2017;Leza et al. 2020). This species harms thin twigs, causing them to wither and die (Pennacchio et al. 2012;Vannini et al. 2017;Gugliuzzo et al. 2019a) while also serving as a vector for various fungal pathogens (Bateman et al. 2016;Vannini et al. 2017;Morales-Rodríguez et al. 2021). In exceptional cases, it can even infest tree trunks with a diameter of up to 80 cm (Gugliuzzo et al. 2019b). ...
... X. compactus is originally from Southeast Asia (Wood 1982) and was first observed in Europe in Italy in 2010 (Pennacchio et al. 2012), followed by detections in France in 2015 (Chapin et al. 2016), Spain in 2019 (Leza et al. 2020), Greece in 2019 (Spanou et al. 2019), Turkey in 2021 (Hizal et al. 2023), Malta in 2021 (EPPO 2021), Slovenia in 2023 (Hauptman et al. 2024), the European part of Russia in 2023 (Karpun et al. 2024), Switzerland in 2023 (Blaser et al. 2024), and Croatia in 2023 (Pernek et al. 2025). ...
... Montenegro hosts Mediterranean biotopes similar to those along the Italian coast, where the species is already established. Consequently, there is a high likelihood that Montenegro could experience similar damage, particularly to shrubs, as observed in Italy (Pennacchio et al. 2012;Vannini et al. 2017;Gugliuzzo et al. 2019a). ...
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Key message The ambrosia beetle Xylosandrus compactus (Eichhoff, 1876), originally from Southeast Asia, was first found in Europe in 2010, specifically in Italy. Since then, X. compactus has rapidly spread across southern Europe, including France, Spain, Greece, Turkey, Malta, Slovenia, Russia, Croatia, and Switzerland, gradually moving northward through lower-elevation areas. In 2023, a single female was found near the village of Kameno in Montenegro. This female was sifted through leaf litter in rocky terrain within a deciduous forest mainly populated by oak and hornbeam trees, located 2.5 km from the international port of Herceg Novi.
... Ante la detección de síntomas sospechosos o bien de señales de posibles daños en brotes y/o ramaje (marchitamiento anormal de hojas, seca de brotes, presencia de exudados u orificios) se tomaron muestras para una inspección más detallada, en campo y posteriormente en laboratorio. Sólo para Xylosandrus, los insectos adultos recogidos fueron conservados en etanol-70º para su estudio e identificación, utilizando las claves dicotómicas y los detalles que se incluyen en los trabajos de Garonna et al. (2012) y Pennacchio et al. (2012). ...
... Las preferencias que se han observado en este trabajo coinciden con las observaciones realizadas por otros autores en Italia (Francardi et al., 2012;Gugliuzzo et al., 2019), Francia (Barnouin et al., 2020), Grecia (Spanou et al., 2019) y Turquía Hizal et al., 2023). ...
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Resumen: Después de la primera cita de Xylosandrus compactus (Eichhoff, 1876) (Coleoptera: Curculionidae: Scolytinae) para la península ibérica en Banyoles (Girona) en 2020 y sobre Laurus nobilis ornamentales, a finales del 2022 se reportan ataques en 25 municipios de 6 comarcas de las provincias de Girona y Barcelona. La lista de plantas afectadas en Cataluña asciende ya a un total de 38 especies de 30 géneros, con una gran preferencia para Laurus nobilis y Ceratonia siliqua, seguido de Cercis siliquastrum, Magnolia grandiflora y Arbutus unedo. Aunque la mayoría de estos ataques han sido sobre brotes anuales, también se han observado daños sobre ramaje de calibre diverso y tronco. Cabe destacar la presencia de ataques de X. compactus sobre especies forestales y sobre vegetación de ribera y de barrancos, y que podrían comportar daños significativos y consecuencias ecológicas sobre el laurel, el cual también está sufriendo ataques de tigre (Stephanitis lauri Rietchel, 2014 [Hemiptera: Tingidae]), cochinilla (Protopulvinaria pyriformis [Cockerell, 1894] [Hemiptera: Coccidae]) y psila (Trioza alacris Flor, 1861 [Hemiptera: Triozidae]). Abstract: After the first record of Xylosandrus compactus (Eichhoff, 1876) (Coleoptera: Curculionidae: Scolytinae) for the Iberian Peninsula in Banyoles (Girona province) in 2020 with attacks on ornamental Laurus nobilis, at the end of 2022 attacks in 25 municipalities in 6 regions of the provinces of Girona and Barcelona are reported. The list of affected host plants in Catalonia amounts to a total of 38 species from 30 genera, with a high preference for Laurus nobilis and Ceratonia siliqua, followed by Cercis siliquastrum, Magnolia grandiflora and Arbutus unedo. Although most of these attacks have been on annual shoots, damages on branches of various diameters and trunks have also been observed. It is worth noting the presence of attacks by X. compactus on forest species and vegetation from riparian and ravines habitats; it could cause significant damage and ecological consequences for the bay laurel, which is also suffering attacks and damages from lace bug (Stephanitis lauri Rietchel, 2014 [Hemiptera: Tingidae]), soft scale (Protopulvinaria pyriformis [Cockerell, 1894] [Hemiptera: Coccidae]) and psyllid (Trioza alacris Flor, 1861 [Hemiptera: Triozidae]).
... Most ambrosia and bark beetles are native to temperate and subtropical forests, so they represent the greatest danger for southern Europe due to a similar climate; hence, damage is most concentrated here (Pennacchio et al., 2004(Pennacchio et al., , 2012Alfaro et al., 2007;Francardi et al., 2017;Leza et al., 2020). In the more northern countries of Europe, only damage by the ambrosia beetle Xylosandrus germanus Blandford, 1894 has been recorded (Maksymov, 1987;Graf and Manser, 2000;Galko et al., 2019). ...
... The MaxEnt algorithm can be used to model the spread of invasive species around the world. For the invasive ambrosia beetle Xylosandrus compactus Eichhoff, 1876, which occurs in southern Europe (Pennacchio et al., 2012;Barnouin et al., 2020;Leza et al., 2020;Riba-Flinch et al., 2021), with the continuation of average climatic values from 1970 to 2000, X. compactus is predicted to find suitable ecological conditions for development in southern Moravia (which is the warmest region of the Czech Republic) by 2050 (Urvois et al., 2021). ...
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Invasive bark beetles pose a threat to native biodiversity and to functional ecosystems and the economic productivity of forests, parks, and orchards. In the Czech Republic, there are six species of invasive ambrosia and bark beetles with a stable natural population, and it can be assumed that other invasive species that will be found. In the Czech Republic, there are no guidelines or methods for the early detection of invasive ambrosia and bark beetles. We propose monitoring at a total of 24 locations considering the following: (i) monitoring approaches used in other countries; (ii) identified entrance gates of invasive ambrosia and bark beetles found in the Czech Republic; (iii) presumed invasive species that occur in surrounding countries and are expanding their range; (iv) substances attractive to all the above mentioned species; (v) commonly available traps; and (vi) minimization of operating costs. Most of the chosen locations are located on the state borders and in river valleys, which are probably the entrance gates to the Czech Republic for invasive ambrosia and bark beetles. In addition, two large timber warehouses where international trade takes place, all international airports and three botanical gardens with tropical greenhouses were selected. Three Theysohn or Ecotrap impact traps should be installed every year at all locations. Traps should be baited with ethanol and exposed from mid-April to the end of July and should be checked every 2 weeks.
... As reported by several authors, the tunnelling activity in the wood, which disrupts the transport of water and nutrients, along with the introduction of ambrosia fungi presumed to be pathogenic to the host trees, likely contributes to the severe stem blight or even death of the plants (Ngoan et al. 1976;Paine et al. 1997;Bosso et al. 2012;Pennacchio et al. 2012;Greco and Wright 2015). In 2011, X. compactus was first recorded for Europe in urban parks of the Campania region in Italy. ...
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... Most of the major damage, e.g., the killing of healthy trees or the infestation of stressed trees, that are consequently killed, caused by invasive bark beetles is reported from southern Europe (Pennacchio et al. 2012, Montecchio and Faccoli 2014, Daubree 2016, Faccoli et al. 2016, Francardi et al. 2017, Leza et al. 2020. Only trees infested by invasive bark beetles have been reported from Central Europe, and this includes only colonizing downed wood by the ambrosia bark beetle, Xylosandrus germanus, in Switzerland and Slovakia (Maksymov 1987, Galko et al. 2019). ...
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