PM 9/32 (1) Solanum carolinense

Q3 Agricultural and Biological Sciences
EPPO Bulletin Pub Date : 2024-11-09 DOI:10.1111/epp.13048
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It is a common weed in many crops and pastures and affects crop yield and quality (Follak, <span>2020</span>; Van Wychen, <span>2020</span>), it is considered toxic to livestock (Bassett &amp; Munro, <span>1986</span>) and a host to many crop diseases and pests (Wahlert et al., <span>2015</span>).</p><p>In the EPPO region, <i>S. carolinense</i> occurs in different habitats including banks of major rivers (e.g. the Waal; Dirkse et al., <span>2007</span>), ruderal habitats (e.g. roadsides, port areas; Pérez et al., <span>2020</span>), pastures and crop fields (Follak, <span>2020</span>; Klingenhagen et al., <span>2012</span>). The spread of <i>S. carolinense</i> is largely driven by human activities. Propagules of <i>S. carolinense</i> can be spread by agricultural machinery with contaminated soil attached both within fields and from field-to-field. Additionally, management and/or construction works in habitats that act as corridors for spread (e.g. roadsides) may facilitate the spread of the species (Follak, <span>2020</span>; Wehtje et al., <span>1987</span>). The establishment of <i>S. carolinense</i> by root fragments is assumed to be very successful, as the species can grow vegetatively from very small fragments (Ilnicki &amp; Fertig, <span>1962</span>; Miyazaki, <span>2008</span>).</p><p>In 2022, <i>S. carolinense</i> was added to the EPPO A2 List of pests recommended for regulation as quarantine pests (EPPO, <span>2022a</span>). The species is regulated by a number of EPPO countries (EPPO, <span>2022b</span>), such as Azerbaijan, Kazakhstan, Jordan, Russia, Ukraine and Uzbekistan (all A1 List) as well as in Belarus and Israel (Quarantine pest) and Georgia (A2 List).</p><p>Further information on the biology, distribution and economic importance of <i>Solanum carolinense</i> can be found in Wahlert et al. (<span>2015</span>) and EPPO (<span>2022b</span>).</p><p>EPPO member countries at risk are advised to prepare monitoring activities and a contingency plan for the eradication and containment of this pest.</p><p>Regional cooperation is important, and it is recommended that countries should communicate with their neighbours to exchange views on the best programme to implement, in order to achieve the regional goal of preventing further spread of the pest.</p><p>For the efficient implementation of monitoring and control at a national level, cooperation between the relevant public bodies (e.g. NPPOs, Ministries of Environment, Ministries in charge of transport, water management), as well as with other interested bodies (associations) should be established.</p><p>Staff of organizations in charge of the monitoring of the species should be trained to recognize the plant at all stages in its lifecycle, even when present as small populations. This may include staff of NPPOs, botanists, agronomists, farmers, nature conservation managers, municipal authorities and road and rail maintenance workers. As this plant has the potential to grow in a range of habitats, citizen science projects may be implemented to encourage landholders and other citizens to report sightings of <i>S. carolinense</i>.</p><p>Regular surveys (see ISPM 6: <i>Surveillance</i>; FAO, <span>2018</span>) are necessary to determine the geographical distribution of the plant and its prevalence. Monitoring can concentrate on areas that are climatically suitable and most vulnerable to colonization. It should be carried out in likely places of introduction of <i>S. carolinense</i>, such as disturbed habitat complexes and arable land. 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引用次数: 0

Abstract

Specific scope: This Standard describes the control procedures aiming to monitor, contain, and eradicate Solanum carolinense.

Specific approval and amendment: First approved in 2024–09.

Solanum carolinense (Solanaceae) is a perennial herb native to North America (Wahlert et al., 2015). The species has several weedy attributes (e.g., reproduces vegetatively, rapid growth, prolific seed production, grows in a variety of biotic and abiotic conditions) (Bassett & Munro, 1986). The species was introduced into the EPPO region most likely in the middle of the 20th century.

Solanum carolinense is regarded to be a major agricultural problem. It is a common weed in many crops and pastures and affects crop yield and quality (Follak, 2020; Van Wychen, 2020), it is considered toxic to livestock (Bassett & Munro, 1986) and a host to many crop diseases and pests (Wahlert et al., 2015).

In the EPPO region, S. carolinense occurs in different habitats including banks of major rivers (e.g. the Waal; Dirkse et al., 2007), ruderal habitats (e.g. roadsides, port areas; Pérez et al., 2020), pastures and crop fields (Follak, 2020; Klingenhagen et al., 2012). The spread of S. carolinense is largely driven by human activities. Propagules of S. carolinense can be spread by agricultural machinery with contaminated soil attached both within fields and from field-to-field. Additionally, management and/or construction works in habitats that act as corridors for spread (e.g. roadsides) may facilitate the spread of the species (Follak, 2020; Wehtje et al., 1987). The establishment of S. carolinense by root fragments is assumed to be very successful, as the species can grow vegetatively from very small fragments (Ilnicki & Fertig, 1962; Miyazaki, 2008).

In 2022, S. carolinense was added to the EPPO A2 List of pests recommended for regulation as quarantine pests (EPPO, 2022a). The species is regulated by a number of EPPO countries (EPPO, 2022b), such as Azerbaijan, Kazakhstan, Jordan, Russia, Ukraine and Uzbekistan (all A1 List) as well as in Belarus and Israel (Quarantine pest) and Georgia (A2 List).

Further information on the biology, distribution and economic importance of Solanum carolinense can be found in Wahlert et al. (2015) and EPPO (2022b).

EPPO member countries at risk are advised to prepare monitoring activities and a contingency plan for the eradication and containment of this pest.

Regional cooperation is important, and it is recommended that countries should communicate with their neighbours to exchange views on the best programme to implement, in order to achieve the regional goal of preventing further spread of the pest.

For the efficient implementation of monitoring and control at a national level, cooperation between the relevant public bodies (e.g. NPPOs, Ministries of Environment, Ministries in charge of transport, water management), as well as with other interested bodies (associations) should be established.

Staff of organizations in charge of the monitoring of the species should be trained to recognize the plant at all stages in its lifecycle, even when present as small populations. This may include staff of NPPOs, botanists, agronomists, farmers, nature conservation managers, municipal authorities and road and rail maintenance workers. As this plant has the potential to grow in a range of habitats, citizen science projects may be implemented to encourage landholders and other citizens to report sightings of S. carolinense.

Regular surveys (see ISPM 6: Surveillance; FAO, 2018) are necessary to determine the geographical distribution of the plant and its prevalence. Monitoring can concentrate on areas that are climatically suitable and most vulnerable to colonization. It should be carried out in likely places of introduction of S. carolinense, such as disturbed habitat complexes and arable land. High risk places of introduction include, summer crops, such as maize and soybean and surroundings of grain and fodder warehouses, oil mills, grain processing factories and fodder industry factories where potentially contaminated plant material is stored or processed.

Any eradication programme for S. carolinense in the case of recently detected populations is based on the delimitation of the infested area within the country and the application of measures to both eradicate and prevent further spread of the pest. The feasibility of eradication depends on the size and designation of the infested area, the density of the population and the accumulated seed bank, and accessibility of the site. Eradication may only be feasible in the initial stages of infestation.

Measures are described in Appendix 1.

The containment programme for S. carolinense in the case of established populations is based on the application of measures to prevent further spread of the species in country or between neighbouring countries.

Measures are described in Appendix 2.

Regional cooperation is essential to promote phytosanitary measures and information exchange in identification and management methods. NPPOs can provide land managers and stakeholders with identification guides and facilitate regional cooperation including information on site-specific studies of the plant, control techniques and management. Professionals (e.g. administration, foresters) should be informed about the threat to natural and managed land, and about preventive measures. Integrated management, involving different sorts of land managers and various management measures will be more effective and efficient.

Abstract Image

具体范围:本标准描述了监控、控制和根除茄草的控制程序。具体批准修改:2024-09年度首次批准。茄科(Solanum carolinense)是一种原产于北美的多年生草本植物(Wahlert et al., 2015)。该物种有几个杂草的属性(例如,无性繁殖,快速生长,多产的种子生产,在各种生物和非生物条件下生长)(Bassett &amp;Munro, 1986)。该物种很可能在20世纪中期被引入EPPO地区。茄草被认为是一个主要的农业问题。它是许多作物和牧场中常见的杂草,影响作物产量和品质(Follak, 2020;Van Wychen, 2020),它被认为对牲畜有毒(Bassett &amp;Munro, 1986)和许多作物病虫害的宿主(Wahlert et al., 2015)。在EPPO地区,S. carolinense出现在不同的栖息地,包括主要河流的河岸(如瓦尔河;Dirkse et al., 2007)、野生栖息地(如路边、港口区;psamurez et al., 2020),牧场和农田(Follak, 2020;Klingenhagen et al., 2012)。carolinense的传播主要是由人类活动驱动的。卡洛林的繁殖体可以通过附着污染土壤的农业机械在田间和田间传播。此外,作为传播通道的栖息地(如路边)的管理和/或建筑工程可能促进该物种的传播(Follak, 2020;Wehtje et al., 1987)。通过根片段建立carolinense被认为是非常成功的,因为该物种可以从非常小的片段营养生长(Ilnicki &amp;多数时候,1962;宫崎骏,2008)。2022年,卡罗来纳角虫被列入EPPO A2检疫性有害生物名录(EPPO, 2022a)。该物种受到许多EPPO国家(EPPO, 2022b)的管制,例如阿塞拜疆,哈萨克斯坦,约旦,俄罗斯,乌克兰和乌兹别克斯坦(均为A1清单)以及白俄罗斯和以色列(检疫害虫)和格鲁吉亚(A2清单)。关于茄草的生物学、分布和经济重要性的更多信息可以在Wahlert et al.(2015)和EPPO (2022b)中找到。建议有风险的植保组织成员国制定监测活动和应急计划,以根除和控制这种有害生物。区域合作是重要的,建议各国与邻国沟通,就最好的执行方案交换意见,以实现防止这种有害生物进一步蔓延的区域目标。为了在国家一级有效地执行监测和控制,应在有关公共机构(例如国家方案组织、环境部、负责运输和水管理的各部)之间以及与其他有关机构(协会)之间建立合作。负责监测该物种的组织的工作人员应接受培训,以便在其生命周期的所有阶段识别该植物,即使是小种群。这可能包括国家专业机构的工作人员、植物学家、农学家、农民、自然养护管理人员、市政当局以及公路和铁路维修工人。由于这种植物有可能在各种栖息地生长,公民科学项目可能会实施,以鼓励土地所有者和其他公民报告南卡罗来纳的目击事件。定期调查(见ISPM 6:监测;粮农组织,2018年),以确定该植物的地理分布及其流行程度。监测可以集中在气候适宜和最易受殖民化影响的地区。它应该在可能引进卡罗来纳草的地方进行,如受干扰的生境复群和耕地。引入的高风险地点包括夏季作物,如玉米和大豆,以及谷物和饲料仓库、油厂、粮食加工厂和饲料工业工厂周围,这些工厂储存或加工可能受污染的植物材料。对于最近发现的卡罗来纳角虫种群,任何根除方案都是基于在国内划定受侵染地区,并采取措施根除和防止这种害虫的进一步传播。根除的可行性取决于侵染区域的大小和名称、种群密度和积累的种子库以及场地的可达性。根除可能只在侵扰的最初阶段可行。措施见附录1。在已建立种群的情况下,对卡罗来纳红丝虫病的控制方案是基于采取措施防止该物种在国内或邻国之间进一步传播。措施见附录2。 区域合作对于促进植物检疫措施以及识别和管理方法方面的信息交流至关重要。npppo可以向土地管理者和利益相关者提供识别指南,并促进区域合作,包括关于工厂具体地点研究、控制技术和管理的信息。专业人员(例如行政部门、林务人员)应了解对自然和管理土地的威胁以及预防措施。综合管理,涉及不同类型的土地管理者和各种管理措施将更有效和高效。
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来源期刊
EPPO Bulletin
EPPO Bulletin Agricultural and Biological Sciences-Horticulture
CiteScore
1.80
自引率
0.00%
发文量
70
期刊介绍: As the official publication of the European and Mediterranean Plant Protection Organization, the EPPO Bulletin publishes research findings on all aspects of plant protection, but particularly those of immediate concern to government plant protection services. Papers are published in English and French, with summaries also in Russian.
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