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Ambrosia artemisiifolia L. - in Switzerland: concerted action to prevent further spreading

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Summary Common ragweed (Ambrosia artemisiifolia L.) was described in Switzerland already in the end of the 19 th century. Ragweed remained hidden until changing conditions triggered its spread. The invasion of this neophyte in Switzerland is still in a stage, where an effective low cost control should be feasible. A survey of the Swiss agricultural research station, Agroscope Changins-Wädenswil (ACW), former RAC Changins, showed for 2005 a clear trend: Beside a few known foci in arable fields, ragweed grows mainly in private garden sites all over the country. Ragweed follows human activities, and it was observed that its seeds are found in bird grain mixtures. Seeds also enter the regions along the French and Italian borders by agricultural machines and excavated material from building sites. The fact that ragweed endangers public health was one reason to follow more carefully its beginning invasion. The spread of ragweed from private house gardens via compost or via professional gardening as pathways to the fields seems to be very easy. Therefore it was necessary to act rapidly to start an effective campaign in 2005. The information on how to eradicate ragweed went to all municipalities in Switzerland and met increasing interest. This year, the aim was to eradicate ragweed in house gardens, to reduce seed production and to make ragweed known to the population. The campaign will continue in 2006.
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1
Revision 2007:
Station fédérale de recherches en production végétale, Agroscope Changins-
Wädenswil (ACW), CH 1260 Nyon 1, Switzerland
Ambrosia artemisiifolia L. – in Switzerland: concerted action to
prevent further spreading
CHRISTIAN BOHREN
Summary
Common ragweed (Ambrosia artemisiifolia L.) was described in Switzerland
already in the end of the 19
th
century. Ragweed remained hidden until changing
conditions triggered its spread. The invasion of this neophyte in Switzerland is
still in a stage, where an effective low cost control should be feasible. A survey of
the Swiss agricultural research station, Agroscope Changins–Wädenswil (ACW),
former RAC Changins, showed for 2005 a clear trend: Beside a few known foci in
arable fields, ragweed grows mainly in private garden sites all over the country.
Ragweed follows human activities, and it was observed that its seeds are found in
bird grain mixtures. Seeds also enter the regions along the French and Italian
borders by agricultural machines and excavated material from building sites.
The fact that ragweed endangers public health was one reason to follow more
carefully its beginning invasion. The spread of ragweed from private house
gardens via compost or via professional gardening as pathways to the fields seems
to be very easy. Therefore it was necessary to act rapidly to start an effective
campaign in 2005. The information on how to eradicate ragweed went to all
municipalities in Switzerland and met increasing interest. This year, the aim was
to eradicate ragweed in house gardens, to reduce seed production and to make
ragweed known to the population. The campaign will continue in 2006.
Keywords : Invasive Plants, Common Ragweed, Ambrosia, neophytes, public
health
Introduction
Common ragweed (Ambrosia artemisiifolia L.) presently causes growing
concerns in Switzerland. Described first in the 1880s and present sporadically in
the country as a neophyte, ragweed begun spreading intensively during the last
decade. Besides being a weed in arable fields, the plant produces pollen with a
high allergenic potential, that can potentially induce severe health problems in the
population. This situation requires a strong control strategy involving not only
farmers but also staff in charge of managing natural areas, road sides, building-
and gravel industries.
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In Europe ragweed has been known since the 1860s, in France as well as in
Germany. Around 1950 ragweed began to spread in the region of Lyon (France).
In the sixties and seventies it became an increasing problem of public health in
France and today around 140 000 people are affected in the region Rhône-Alpes.
12,1 % of the population around Lyon is allergic (ARVALIS, 2005). In Hungary 90
% of the land area is infested, whereas in former Yugoslavia ragweed is widely
distributed mostly on fallow land as a consequence of war. The Po Valley in
northern Italy is nearly completely colonized (AFEDA, 2005)
This paper presents briefly the historical and current distribution of ragweed in
Switzerland, some information about the presence of pollen in the air with related
medical aspects and, finally, the latest information about the control campaign in
Switzerland.
Figure 1: Distribution of Ambrosia artemisiifolia L. before 1982 in Switzerland
A neophyte in Switzerland
HEGI (1908) reported sporadic findings of ragweed in Geneva, Basel, Zurich
and Berne in the late 19
th
century on fallow ground, along road banks, and in
gravel pits. JAQUET (1925) described it as a sporadic species, growing in the
region of Fribourg. But ragweed remained hidden. The map set up by the Centre
of the Swiss Floristic Network (CRSF/ZDSF 2004) shows that three foci of
ragweed were found before 1994, and about 85 after 1994. Currently, colonization
of Switzerland by ragweed is described as “at the onset of an invasion”
(CORDILLOT 2004) and therefore the costs to control it may be still low. But the
canton of Ticino, on the southern side of the alps, is already heavily infested.
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In the canton of Geneva and in the neighbouring region of the canton of Vaud,
ragweed is present on agricultural fields, along road banks, and in recreational
areas. Other cases – small foci with high infestation rate – have been reported for
a long time in Basel, Ticino, Geneva and recently in Zurich. Ragweed seeds
reached the Geneva region via agricultural machines such as combine harvesters.
Machines for soil treatment are also routinely exchanged between the French
region of Lyon and the Swiss Bassin Lémanique. Excavated material from
building sites is very often been transported between France and Geneva, likewise
between Italy and the canton of Tessin.
Figure 2: Distribution of Ambrosia artemisiifolia L. in 2002 in Switzerland.
= observations before 1994, = observations after 1994.
These examples show how ragweed benefits from human activities to spread.
Thus, it is not amazing to find ragweed in many private house gardens, or flower
pots in urban and recreational areas. It is also present along traffic routes, growing
often directly along the asphalt. Heavily infested areas are found in gravel pits
where several hectares can be left untouched for a couple of years. Smaller foci
are also known to be present on building sites.
A few reasons may account for ragweed spreading nowadays at a much faster
rate:
with globalisation, there is more travel, and transportation of goods is
more intensive; ragweed seeds directly benefit from these to spread
further;
more environmentally-friendly agricultural practises led to less
intensive crop management, in particular against weeds;
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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global warming may help ragweed to grow and spread at faster rates in
the northern hemisphere;
imported bird seed mixtures, that are distributed nationwide.
Figure 3: Distribution of Ambrosia artemisiifolia L. registered in 2005 by the
Swiss Agricultural Research Station Agroscope Changins–Wädenswil (ACW).
Einzelpflanzen = single plants.
Pollen counts
Ragweed produces pollen in large quantities from August to September which
is often transported by wind over far distances. The pollen of Ambrosia has a high
potential to provoke hay fever and in some cases asthmatic reactions.
Concentrations between 6 and 10 pollen grains per m
3
air represent a moderate
load and more than 10 pollens per m
3
a high load. By comparison, more than 49
pollen per m
3
air represent a high load for grass pollen, which is the main allergen
for hay fever in Switzerland.
The airborne pollen is collected with a volumetric pollen trap and analysed by
light microscopy. In 1969 R.M. Leuschner initiated the pollen measurement in
Switzerland with the first pollen trap in Basel. Since 1993 MeteoSwiss runs the
national pollen monitoring network with 14 measuring stations. The Ambrosia
pollen counts increased in the region of Geneva in the eighties and nineties. Most
of the pollen is transported by wind from neighbouring regions, as shown by the
correlated increase of pollen in Lyon (CLOT et al. 2002). The highest levels of
Ambrosia pollen in Switzerland are detected in Ticino. In 2004 11 days of high
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load were measured in Lugano and Locarno and in Geneva 9 days, whereas in
Zurich no high concentrations of pollen were detected (CLOT et al. 2005).
Medical aspects
If invasion by Ambrosia is left uncontrolled, increase of allergies could heavily
augment the estimated costs of 260 million Swiss Francs for allergy and asthma
(MÜLLER et al, 2000) Experiences from France and North America show that
around 10 % of the population is sensitive to ambrosia pollen (DRASS 2000). A
quarter of them may develop heavy asthmatic reactions. So far, ragweed allergy
with evidence of sensitisation in Geneva remains low with possibly 4 to 5
potential cases in 2004 (TARAMARCAZ et al. 2005). Only 8 of 18 polled medical
practitioners have encountered 1 or 2 patients allergic to ragweed during the 2004
ragweed pollinisation period.
An estimated 100 million CHF is spent in Switzerland to cover overall costs
for treatment of allergic rhinitis (MÜLLER et al, 2000). But numerous sensitive
persons may not consult a doctor. Two third of the patients in Geneva – a town
hosting numerous international organisations – were sensitised outside of
Switzerland (HAUSER, 2004). In the St.Gall Rhine valley in eastern Switzerland
10.6 % of 15 year old students showed sensitivity to pollen of ragweed (GASSNER
2005), amongst other pollen.
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Photo 2: Common ragweed (A. artemisiifolia L.) forms different types of
flowers, probably as a result of stress.
Seed spread and distribution
French observations clearly show that bird seed mixtures contaminated with
Ambrosia seed are an important pathway (CHAUVEL et al. 2004); up to 2500
grains were found in one kg. Another important source for spread is the feed for
small animals such as rabbits and hamsters. It can contain fertile ambrosia seeds,
which can directly reach the field. Seeds are also found in imported sunflower and
sorghum. In most cases it is technically impossible to separate ragweed grains
because weight and size could be similar to other seeds like sorghum. Grain
importers and feed producers should bear the responsibility and sterilise the grains
used for feed.
Seeds of Ambrosia are not airborne, normally they fall on the ground. Spread
of ragweed is greatly favoured by human activities.
Ragweed has a higher spread potential than most indigenous annual
dicotyledonous weed species and most indigenous grass weeds in Central Europe.
Among neophytes, only South African ragwort (Senecio inaequidens DC.),
Canadian horseweed (Conyza canadensis L.) and Japanese knotweed (Reynoutria
japonica HOUTT.) show higher spread potentials (WEBER et al. 2005).
Ragweed is easily mistaken with mugwort species Artemisia vulgaris L. and
Artemisia verlotiorum LAMOTTE.
Distribution of Ambrosia registered in different periods
The first Swiss distribution map set up by the Swiss Web Flora (Fig. 1) shows
some foci of Ambrosia registered before 1982 in the region of Basel, but in the
rest of the country only a few places were infested.
The map established by the Centre of the Swiss Floristic Network shows a
wider distribution of Ambrosia in Switzerland twenty years later in 2002. Mainly
in the western and southern part of the country large areas are infested with
Ambrosia, whereas smaller foci are reported from the rest of the country.
The map of 2005 is based on the survey of the Swiss Agricultural Research
Station Agroscope Changins–Wädenswil (ACW) . It does not show earlier
observations. Single plant foci were found mostly in house gardens following
announcement by their owners and verified by official experts. The high number
of Ambrosia single plant foci reported 2005 in the canton of Zurich (top centre of
the map, north) is the result of a regional publication of the Swiss house owners
association (HEV) in July. It was the time when Ambrosia was grown high
enough, to be recognised by the eyes of a layperson.
Control in agriculture
Control of ragweed with herbicides is difficult in some crops like sugar beet
and peas, and is nearly impossible in sunflowers as both ragweed and sunflower
belong to the same botanical family.
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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Since 2003 ACW has been performing efficacy trials with many herbicides
registered in Switzerland. Table 1 shows the efficacy of the herbicides tested.
Knowledge about mechanical control of ragweed could be very important for road
services, as the use of herbicides along roads is highly restricted. Since 2004, we
have been monitoring mowing trials where we count the seed production of
ragweed after a series of various dates of cutting (BOHREN et al. 2005). Our first
observations show that a cut in the first half of September can stop the seed
production, but cannot prevent the production of pollen. It may be very difficult to
inhibit coevally pollen production and seed production.
Ragweed, germinated in cereals, rests in a small stage until the crop is
harvested; coming to the light, it starts to reproduce. The flowering time is
obviously day length dependant and is similar for all plants: it starts from end of
July. Insufficient mechanical or chemical control allows ragweed to sprout
quickly from the base of the stem.
Table 1: Trial site La Petite Grave: Efficacy of various herbicides 2003 –
2007
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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La Petite Grave
application of products in field trials of small plots (4 replications); application time according to label for crop
efficacy in %
X= registered in CH
vegetables and others
product
dosage
active ingredient
efficacy 2003
efficacy 2004
efficacy 2005
efficacy 2006/7
mean (estimated)
faba bean
set aside
peas
cereals
potatoes
corn
beetroot
soya
grassland
sugar beet
Atrazin 2 l/ha Atrazin 500 g/l 100 100 X
Lontrel 1 l/ha Clopyralid 100 g/l 100 100 X X
ecol.
comp.
Banvel 4 S 0.5 l/ha Dicamba 480 g/l 100 100 X X X
Basta 5 l/ha Glufosinate 200 g/l 100
Roundup 3 l/ha Glyphosate 360 g/l 100
Afalon 3 kg/ha Linuron 47.50% 100 100 X X div.
Sencor 1 kg/ha Metribuzin 70% 97 100 100 X tomatoes
Gardo Gold 4 l/ha
Terbuthylazin, S-
Metolachlor
187.5 +
312.5
g/l
100 x
Venzar 2.5 kg/ha Lenacil 80% 99 99 X X leek
Arelon 3 l/ha Isoproturon 500 g/l 96 96 X
Golaprex 4 l/ha
Orbencarb,
Metribuzin
803.4 +
66.9 g/l
96 96 X X X X
carottes/
tulips
Topper 3.5 l/ha Ioxynil 240 g/l 95 95
chicorée
etc
MCPB 4 l/ha MCPB 400 g/l 85 100 95 X X X X berries
Equip 2 l/ha Foramsulfuron 22.5 g/l 94 94 X
Callisto 1.5 l/ha Mesotrion 100 g/l 92 92 X
Tomigan 1 l/ha Fluroxypyr
259 g/l
(~180
g/l
acide)
80 85 X
Basagran 3 l/ha Bentazon 81 40 75 X X X X X X flax
Terano 1 kg/ha
Flufenacet,
Metosulam
70 70 65 75 X
Concert 60 g/ha
Metsulfuron,
Thifensulfuron
75
Lanray 5 l/ha Orbencarb, Linuron 88 40 75 X X X X
Rasantan 1 kg/ha
Bromoxynil, DFF,
Amidosulfuron
65 65 X
Orkan 3 l/ha MCPP, Ioxynil, DFF 65 65 X
Primus 0.15 l/ha Florasulam 40 60 X X
Goltix compact 4 kg/ha Metamitrone 50 60 X X
Equip+ Terano 2l+1kg/ha
Foramsulfuron +
Flufenacet/Metosulam
50+ 55 X
Maister 150 g/ha
Foramsulfuron,
Iodosulfuron
65 38 50 X
Bolero 1 l/ha Imazamox 40 50 X
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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Refine extra 40 g/ha
Thifensulfuron,
Tribenuron
35 50 X
Goltix triple 2 kg/ha 2x
Metamitron,
Ethofumesate,
Phenmedipham
15 15 X X
Ally Class 50 g/ha
Metsuflufron,
Carfentrazon
15 15 X
Debut 60 g/ha Triflusulfuron 7 25 15 X X
Lotus 0.25 l/ha Cinidon-ethyl 10 10 X X
Titus 40 g/ha Rimsulfuron 5 0 10 X
Dual-Gold 2 l/ha S-Metolachlor 0 10 X X X
Aurora 40 g/ha Carfentrazon 5 5 X
Tramat flow 2.6 l/ha Ethofumesat 5 5 X X
Bandur 5 l/ha Aclonifen 0 0+ 0 X X X
herbicides applied in
autumn in cereals
Arelon, Herold,
Malibu,Fenikan,
Herbaflex, Lanray,
Banaril, Stomp,
Boxer, Concert
0 0 X
Racer 3 l/ha Flurochloridon 0 0 x
Stomp 4 l/ha Pendimethalin 0 0 0 0 X X X X
Boxer 5 l/ha Prosulfocarb 0 0+ 0 X X
Express 40 g/ha Tribenuron 0 0 X
Trifluralin 3.5 l/ha Trifluralin 0 0 X
all registered a.s. in winter oil seed rape applied in autumn 0 0
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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Concerted action
Several factors have to be respected to launch an effective control of ragweed.
On one hand it might not be sufficient for public health to apply control strategies
in agriculture for ragweed as for any other weed, because we do not know
anything about a limit of tolerance which guarantees that the amount of ragweed
pollen will not rise above the high load limit of >10 grains per m
3
air. On the
other hand it might not be sufficient to apply control strategies along roadsides or
in natural reserves to prevent ragweed becoming a weed in agricultural areas.
The danger of ragweed pollen to human health requires a concerted action of
several disciplines:
In cantons of Ticino, Neuchâtel, and Geneva, “Ambrosia Groups” were
created to discuss control strategies. The initiators of such groups often
belong to agricultural services, meteorology agencies and medical
services. Members of the “Ambrosia Group” in Geneva studied in-
depth the dissemination routes of ragweed seeds. Botanists,
environmentalists, road services, medical and agricultural services take
part. Meanwhile the group in Geneva is officially registered by the
cantonal government. Within this group, the Swiss federal research
station ACW, was appointed to work out control strategies for
agriculture (DELABAYS et al. 2005).
The Swiss Agency for the Environment, Forests and Landscape has
organised multidisciplinary workshops to learn more about ragweed.
Cantonal offices have also organised workshops to instruct the
personnel working with road services and environmental agencies.
In 2005 the Federal Departement for Economic Affairs adapted the
ordinance on animal feedstuff with the restriction that all type of
feedstuff put into circulation must be free from ragweed seeds. 2006 the
Federal Council amended the ordinance on plant protection and
declared A.artemisiifolia subject to official control (BUND, 2006).
Agricultural advisory services are now forced to control every focus of
contamination in the fields because of the invasive behaviour of
ragweed.
Meteorologists are well equipped to measure pollen in the air, and they
edit periodically a pollen report (METEOSWISS) for allergic persons
which is also broadcasted by the radio stations.
Medical services study more about the allergic symptoms intensively in
order to treat future patients properly.
Road services support the information campaign in 2006 finacially.
Information campaign 2005
Experiences from France and elsewhere show that once ragweed is in the
fields, it can no longer be fully controlled. Consequently we must control ragweed
in this stage of early spread, to stop it infesting our fields.
The question in 2005 was, where and how ragweed is located in Switzerland.
To answer this question, ACW published in spring an article on ragweed in the
house-owners journal (BOHREN, 2005). The possibility was also offered to send
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suspect plants to ACW for determination. We have registered in 2005 mostly
single plant foci in house gardens throughout the country. But we have also
registered the infestation of 6 agricultural plots and 22 public facilities with
several hundreds of plants. A massive infestation was discovered in a gravel pit in
the region of Basel.
The echo of the campaign 2005 with more than 120 new foci detected, showed,
that people are very vigilant. A flyer – edited in three different languages – with a
description of the plant and its danger has been printed and sent to all
municipalities. 130,000 copies were distributed within 2 weeks.
Several institutions do continuously edit data sheets and leaflets on ragweed to
inform their clientele. Individual measures often do not solve the real problem.
Private house gardeners are often good observers, and they decide clearly to
tolerate or not a certain plant species in their garden. People sensitive to hay fever
and other allergies will even control public areas. Readers of the house-owners
journal sending plants to our research stations frequently wrote in their
accompanying letter how happy they are to do something good for their health.
The elimination of many single plant foci may help to reduce the number of
seeds produced and may therefore slow down the spreading of ragweed.
The very successful campaign of 2005 will be continued in 2006, aiming at
maintaining fields in Switzerland free of ragweed as long as possible..
Agricultural institutions must be active with the objective to keep ragweed away
from our fields.
References
AFEDA, 17ème colloque pluridisciplinaire de l’AFEDA, 25 novembre 2005 Parc des
Oiseaux, Villars-les-Dombes. Chantal Déchamp, editeur AFEDA, Saint Priest
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Lyon St.-Exupéry, Arvalis – Institut du végétal, Paris
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OHREN C., Neophyten-Invasion stoppen. Der Schweizerische
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dissemination d’Ambrosia artemisiifolia L. via les semences de tournesol. XII
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CLOT B., D. SCHNEITER, PH. TERCIER, R. GEHRIG, A. PEETERS, M. THIBAUDON,
2002: Ambrosia pollen in Switzerland: Local production or transport?. Allergie et
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malherbologiques. Revue Suisse Agric., 37 (1), 17 – 24.
DRASS, 2000. Etude sur la place de l’allergie due à l’ambroisie parmi les pollinoises
en Rhône-Alpes. Rapport d’étude, DRASS Rhône-Alpes, Lyon, 49p.
GASSNER M.: Ambrosia in der Ostschweiz. Personal information, Grabs 2005.
HAUSER C. : personal information. Service of Allergology and Immunology,
University Hospital of Geneva, 2004.
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Berücksichtigung von Deutschland, Österreich und der Schweiz. Lehmann,
München.
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cultivées dans le canton de Fribourg. Mém. Soc. Fribourg. Sci. Nat., Bot. 3,
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Further information : Christian Bohren, Agroscope Changins–Wädenswil (ACW),
P.O.Box 1012, CH 1260 Nyon, 1;
christian.bohren@rac.admin.ch
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Photo 3: Common ragweed (A. artemisiifolia L.) growing on a building site
near Geneva, Switzerland
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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Photo 1: Common ragweed (A. artemisiifolia L.) grown in an agricultural field
near Geneva, Switzerland.
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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HRISTIAN BOHREN AGROSCOPE ACW, NYON SWITZERLAND, 2007
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WITH REFERENCE TO: Bohren C., Common ragweed (Ambrosia artemisiifolia L.) in
Switzerland: development of a nationwide concerted action,
Aus: Journal of Plant Diseases and Protection - Zeitschrift für
Pflanzenkrankheiten und Pflanzenschutz, Sonderheft XX, in Vorbereitung (2006),
ISSN 1861-4051, Eugen Ulmer KG, Stuttgart
Ambrosia artemisiifolia L. – in Switzerland: concerted action to prevent further spreading
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HRISTIAN BOHREN AGROSCOPE ACW, NYON SWITZERLAND, 2007
... To install effective and adequate control measures it is necessary to know the relevance of the different routes that the species uses, to enter new growing sites. Spread of A. artemisiifolia seeds within excavated material is an important pathway for the species to reach new locations (Bohren 2005(Bohren , 2007, and thus this is investigated in this study. The aims of this part are, to learn more about: ...
... Spread with excavated material is also relevant in Switzerland. Transportation of soil and gravel between neighbouring countries is a common practice in parts of Europe, particularly between Switzerland, France and Italy, where construction materials and substrates near borders are exchanged across borders, which may lead to the establishment of ragweed on new sites (Bohren 2007, Buttenschøn et al. 2010. Bohren (2007) describes that machines for soil treatment are routinely exchanged between French regions of Lyon and the Swiss Basin Lemanique. ...
... Transportation of soil and gravel between neighbouring countries is a common practice in parts of Europe, particularly between Switzerland, France and Italy, where construction materials and substrates near borders are exchanged across borders, which may lead to the establishment of ragweed on new sites (Bohren 2007, Buttenschøn et al. 2010. Bohren (2007) describes that machines for soil treatment are routinely exchanged between French regions of Lyon and the Swiss Basin Lemanique. Also, Essl et al. (2009) mention the transportation of soil as an important pathway for the spread of A. artemisiifolia in Austria. ...
... According to the density results, one and two mowings at 3-4 leaf stage cause population regeneration and weak management of western ragweed, which was consistent with the results of many studies (Gao et al., 2009). The regrowth of western ragweed after cutting has been previously well confirmed (Barbour & Meade, 1981;Barnett et al., 2013;Bohren, 2006). Mowing the above-ground plants if done at the right time reduces the biomass allocated to the underground parts and reduces the potential for regrowth in plants (Darby et al., 2008). ...
Article
Western ragweed (Ambrosia psilostachya) is an invasive species in spring‐sown crops that can also cause allergic rhinitis and asthma due to its allergenic pollen. In order to evaluate the chemical and mechanical control of western ragweed, two separate experiments were conducted in 2019 and 2020. Chemical treatments included non‐treated plots, the combination of glyphosate and 2,4‐D, glyphosate + ammonium sulfate, bentazon, imazethapyr + surfactant, picloram, 2,4‐D, and mechanical treatments included: once mowing at 3–4 leaf stage, once mowing before male flowers' emergence, once mowing early female flowering stage, two mowings at 3–4 leaf stage, two mowings before male flowers' emergence. Results of these studies indicated that in both years, picloram at 0.96 kg ai ha−1 and the combination of 2,4‐D and glyphosate at 1.23 + 0.72 kg ai ha−1 provided more than 90% control of western ragweed and reduced plant height, dry weight, and density. The application of imazethapyr and bentazon, respectively, at the rates of 0.1 and 0.96 kg ai ha−1 did not cause visual damage. The mowing shortly before flowering was the most effective mechanical treatment for western ragweed control. In order to the efficient management of the western ragweed, we suggest that the mowing treatments if appropriately timed and application of glyphosate plus 2, 4‐D at 1.23 + 0.72 kg ai ha−1, and picloram at 0.96 kg ai ha−1 can prevent western ragweed from spreading by suppressing growth and reducing seed production.
... The control of ragweed is technically feasible and must be supported by the community: experiences in Germany and other countries show that legal regulations specific for ragweed are necessary for ragweed control (4,(46)(47)(48)(49) to join health agricultural and environmental advantages. ...
Article
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Background and aim: Airborne ragweed pollen is one of the agents of respiratory allergies in our changing environment. The monitoring of pollen is essential to manage pollen allergy and to improve its forecasting methods. Moreover, the control and fight against ragweed plants is important. Aim of this study is to understand the scenario of the studies on ragweed over time. Methods: We searched PubMed and Scopus for articles published until July 2022 reporting the words "ragweed". Articles written in all languages were included. Results: Scopus was the database with the highest number of published papers. Among the papers on ragweed, the papers citing the word "allergy" were 59.4% in PubMed and 37,6% in Scopus. The subject areas more addressed were medicine, immunology, genetics/molecular biology, but agricultural/biological sciences too and, interestingly, other subjects like social sciences, art, humanistic, etc.). Among the top 40 institutions supporting research, 8 were European, 4 Asian, 1 Russian and 21 were American, the other 6 were pharmaceutical companies. Conclusions: This study shows a picture of the ragweed studies and some related subjects over time. A gap between the number of biomedical and not biomedical issues was evident. There is a need for greater involvement of institutions into support of knowledge and fight ragweed. The results will provide a useful tool to identify future goals in a global approach of ragweed related issues.
... Ambrosia artemisiifolia (common ragweed) originated in the Sonoran region of North America and is a C 3 plant. As a malignant and invasive weed, it poses a serious threat to human health, agricultural production, and biodiversity (Vincent et al., 1992;Fumanal et al., 2005Fumanal et al., , 2007Bohren, 2006;Bonini and Ceriotti, 2019). Ophraella communa LeSage (Coleoptera: Chrysomelidae) is derived from North America and its larvae and adults feeds on common ragweed leaves. ...
Article
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Increase in atmospheric CO2 directly affects the insect physiology and behavior, and indirectly affects the herbivorous insects by affecting their hosts. The increase in atmospheric CO2 is accompanied by an increase in temperature and heat waves. Ophraella communa LeSage is a natural enemy of Ambrosia artemisiifolia (common ragweed). The development and reproduction of this beetle is weakened upon eating common ragweed grown under stress conditions. As female behavior and physiology alter after mating, the reproductive tract of males is likely to modulate reproduction and development in this species. Herein, the transcriptional profiles of testes and accessory glands from male O. communa individuals feeding on common ragweed under conditions of high CO2 concentration and heat waves and that grown under ambient CO2 concentration were compared. Differentially expressed genes (DEGs) were identified between the same tissues from beetles fed on common ragweed grown under different stress conditions. There were 3, 2, 3, 1and 5 genes related to decomposition and transport of macromolecular substances, host location, stress response, reproduction, and poisonous food-utilization. No expected response was observed in the male reproductive tract, but some of the identified DEGs might control the development of the population. The results presented here should be helpful in guiding future studies on deciphering the indirect response of other organs to high CO2 concentration and heat waves, as well as the functions of seminal fluid proteins in O. communa.
... conservation values (AHCV) such as sites exhibiting exceptional botanical richness, assemblage of rare, and threatened and/or endemic plant species. While some countries have already established procedures for the management of IAPs (e.g., USA, Switzerland; Bohren, 2006;Van Driesche, Blossey, Hoddle, Lyon, & Reardon, 2002), many other countries are still in the process of evaluating the threats and risks caused by IAPs. ...
Article
Full-text available
Invasive alien plants (IAP) are a threat to biodiversity worldwide. Understanding and anticipating invasions allow for more efficient management. In this regard, predicting potential invasion risks by IAPs is essential to support conservation planning into areas of high conservation value (AHCV) such as sites exhibiting exceptional botanical richness, assemblage of rare, and threatened and/or endemic plant species. Here, we identified AHCV in Georgia, a country showing high plant richness, and assessed the susceptibility of these areas to colonization by IAPs under present and future climatic conditions. We used actual protected areas and areas of high plant endemism (identified using occurrences of 114 Georgian endemic plant species) as proxies for AHCV. Then, we assessed present and future potential distribution of 27 IAPs using species distribution models under four climate change scenarios and stacked single‐species potential distribution into a consensus map representing IAPs richness. We evaluated present and future invasion risks in AHCV using IAPs richness as a metric of susceptibility. We show that the actual protected areas cover only 9.4% of the areas of high plant endemism in Georgia. IAPs are presently located at lower elevations around the large urban centers and in western Georgia. We predict a shift of IAPs toward eastern Georgia and higher altitudes and an increased susceptibility of AHCV to IAPs under future climate change. Our study provides a good baseline for decision makers and stakeholders on where and how resources should be invested in the most efficient way to protect Georgia's high plant richness from IAPs.
... conservation values (AHCV) such as sites exhibiting exceptional botanical richness, assemblage of rare, and threatened and/or endemic plant species. While some countries have already established procedures for the management of IAPs (e.g., USA, Switzerland; Bohren, 2006;Van Driesche, Blossey, Hoddle, Lyon, & Reardon, 2002), many other countries are still in the process of evaluating the threats and risks caused by IAPs. ...
Article
Full-text available
Invasive alien plants (IAP) are a threat to biodiversity worldwide. Understanding and anticipating invasions allow for more efficient management. In this regard, predicting potential invasion risks by IAPs is essential to support conservation planning into areas of high conservation value (AHCV) such as sites exhibiting exceptional botanical richness, assemblage of rare, and threatened and/or endemic plant species. Here, we identified AHCV in Georgia, a country showing high plant richness, and assessed the susceptibility of these areas to colonization by IAPs under present and future climatic conditions. We used actual protected areas and areas of high plant endemism (identified using occurrences of 114 Georgian endemic plant species) as proxies for AHCV. Then, we assessed present and future potential distribution of 27 IAPs using species distribution models under four climate change scenarios and stacked single‐species potential distribution into a consensus map representing IAPs richness. We evaluated present and future invasion risks in AHCV using IAPs richness as a metric of susceptibility. We show that the actual protected areas cover only 9.4% of the areas of high plant endemism in Georgia. IAPs are presently located at lower elevations around the large urban centers and in western Georgia. We predict a shift of IAPs toward eastern Georgia and higher altitudes and an increased susceptibility of AHCV to IAPs under future climate change. Our study provides a good baseline for decision makers and stakeholders on where and how resources should be invested in the most efficient way to protect Georgia's high plant richness from IAPs.
... Hier finden sich verantwortliche Berufs-und Behördenvertreter zu gemeinsamen Treffen. Im Kanton Genf sind Vertreter der Medizin, Biometeorologie, Landwirtschaft, Naturschutz, Straßenunterhalt (national, kantonal, kommunal), Eisenbahnen, Baubranche sowie Kantons-und Gemeindebehörden dabei (Bohren et al., 2006). In diesen Gruppen lernt man einander kennen und merkt, wo den anderen der Schuh drückt; gemeinsame Aktionen entstehen hier. ...
Article
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The dicotyledonous summer annual common ragweed (Ambrosia artemisiifolia L.) is on the one hand a noxious arable weed and on the other hand an invasive neophyte with a great potential to spread. Various possibilities are known for control of common ragweed in agricultural fields with mechanical and chemical methods. Limits are set in sunflowers because sunflower and ragweed are botanically related. Because no weed control action results in 100% efficacy, common ragweed can propagate quickly in untreated corners of the field or in other disturbed soils. The legal obligation of reporting and control – introduced in Switzerland a couple of years ago – allowed the development of specific distribution maps and enhanced the quality of control measures. Facts and figures from the Canton of Geneva prove that the ragweed invasion has been stopped, but the species is not eradicated. The results of Geneva represent the results of good ragweed control in the whole country. Beside agriculture, traffic infrastructure, building sites, gravel pits and urban park and garden areas are sensible to ragweed invasion. This is why the formation of “Ambrosia Groups” helps to exchange experiences and to understand factors provoking the invasion. The responsibility of individuals helps to improve control efficiency even if financial funds are small. A sustainable control success depends on the efficiency to hamper seed production. The reduction of pollen quantity in the air in a long term is part of the earnings for the control effort. Actually, the publicity of common ragweed is fed by specialist information and its distribution in the media. It would be an interesting task to develop in our fast moving era an awareness level comparable to that of the stinging nettle.
Chapter
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In this chapter, we present general knowledge about five very common invasive alien species: Common ragweed (Ambrosia artemisiifolia L.), Jersalem Artichoke (Helianthus tuberosus L.), Japanese knotweed (Reynoutria japonica Houtt), Tree‐of‐Heaven (Ailanthus altissima [Mill.] Swingle), and Black locust (Robinia pseudoacacia L.). Based on the our own fieldwork and available literature, we prepared data distribution maps of invasive alien species in Bosnia and Herzegovina. It is very important to note that from an ecological point of view the species listed have a strong negative environmental, health, social, and economic impact. Due to the strong impacts on biodiversity, it is necessary to establish a permanent monitoring system, create a database of impacted habitats, and initiate actions to eradicate or control high‐risk invasive species in places where they have become established.
Chapter
This chapter provides an overview of the status of invasive alien species in Switzerland, the associated challenges and the ongoing work concerning invasive alien species from a national perspective. Despite regional differences, the number of invasive alien species is generally increasing in Switzerland. To contain the spread of invasive alien species with the potential to cause damage and prevent new introductions, a national strategy that defined 29 measures was adopted in 2016 by the Swiss Federal Council. This chapter presents the Swiss Invasive Alien Species Strategy and the three priority measures that are the focus of current work: strengthening national coordination of all actors responsible for implementing the national strategy measures, harmonizing the legal basis concerning invasive alien species, and establishing an expert group to continuously update the knowledge bases required to implement the strategy. Finally, it presents some case studies that illustrate different approaches to preventing and controlling specific invasive alien species.
Technical Report
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Uniwersytet Śląski w Katowicach, Wydział Biologii i Ochrony Środowiska. Ekspertyza na zlecenie Generalnego Dyrektora Ochrony Środowiska, pp. 178.
Article
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The purpose of this article is to alert physicians for the environmental and health threats of Ambrosia artemisiifolia (common ragweed) in Switzerland. Switzerland borders several heavily ragweed colonised areas. Up to 12% of the population suffers from allergies (hay fever, asthma) to ragweed pollen in these areas. Switzerland is beginning to be invaded by this plant. Currently, the ragweed pollen counts are still low but can reach local peaks that induce symptoms in allergic individuals. Ragweed allergy, however, is still rare in Switzerland. Because the amount of ragweed pollen was increasing in the last few years, identification and surveillance of ragweed plant foci was started. Colonisation is currently systematically monitored in Geneva and southern Tessin. Major accumulation of ragweed foci have been detected in the canton of Geneva, the western shore of the lake of Geneva belonging to the canton of Vaud, and in the southern part of the canton of Tessin, aside from minor foci registered all over Switzerland. The routes of ragweed invasion are presented and discussed. Current measures of ragweed containment and needs for the future are presented. The urge for these measures at an early stage of ragweed spread is underlined by the impracticability of eradication in highly colonised areas. The costs of preventing ragweed spread in Switzerland are likely to be several magnitudes lower than the treatment of a significant percentage of the Swiss population for ragweed pollen allergy. Because areas can change from low to heavy ragweed colonisation within a few years, the current window of opportunity to prevent further colonisation by ragweed should not be missed.
Article
A Europe-wide survey was conducted by sending questionnaires to weed scientists in order to evaluate currently troublesome weeds and those which may cause problems in the future. Recipients were asked to list species that are spreading and cause problems in agroecosystems, and to rate these according to three scores (degree of weediness, degree of spread potential, and degree of control success), with three levels for each score (low, medium and high). In total, 281 species were reported from 26 European countries. Most of them were annuals (48%), followed by perennials (34%) and biennials (14%). There were significant differences in weed scores among these life forms. Weed scores were unrelated to each other, implying that they have different meanings with respect to the biology of the species. Weed scores did not correlate with European range size, implying that they indicate the weediness of the species independently of the geographical distribution and can be used to prioritize weed species for management.
Common ragweed (Ambrosia artemisiifolia L.) in Switzerland: development of a nationwide concerted action
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