Category Archives: Ratings

Dwarf Siberian pine beetle | Dryocoetes pini

California Pest Rating  for
Dwarf Siberian Pine Beetle | Dryocoetes pini
Coleoptera: Curculionidae: Scolytinae
Pest Rating: A

 


PEST RATING PROFILE

Initiating Event:

Dryocoetes pini is currently Q-rated.  A permanent pest rating proposal is required to support an official pest rating.

History & Status:

Background: This bark beetle measures approximately 2.5 mm in length.  Adults tunnel through the phloem (inner bark), where eggs are laid.  The larvae feed on the phloem.  This species has been reported to feed on pine (Pinus spp.), larch (Larix spp.), fir (Abies spp.), and spruce (Picea spp.) (European and Mediterranean Plant Protection Organization; Niijima, 1909).  The beetle is apparently not known as a significant pest in its native range (European and Mediterranean Plant Protection Organization).  Dryocoetes species are usually considered “secondary pests” and only attack dead, injured, or otherwise compromised host trees (Vega & Hofstetter, 2014).  At least one species, Dryocoetes confusus Swaine, is a serious pest of fir trees; it is apparently the most destructive member of the genus in North America (CABI,  2017; Hansen, 1996; Vega & Hofstetter, 2014).  The pathogenic fungus Grosmannia dryocoetis is associated with D. confuses (Vega & Hofstetter, 2014).  Similar fungi may also be associated with other Dryocoetes species, including D. pini.

Worldwide Distribution: Dryocoetes pini occurs in the Russian Far East, China, South Korea, and Japan (European and Mediterranean Plant Protection Organization; Park, 2016; Shiraki, 1952).  The species is not known to be present in North America.

Official Control: This species is not known to be under official control anywhere.

California Distribution: This species does not appear to be present in California (Symbiota Collections of Arthropods Network).

California Interceptions: This species is not known to have been intercepted in California.

The risk Dryocoetes pini would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: This species appears to occur primarily in areas with a temperate climate. It is possible that it could thrive in a large portion of California if it was introduced.  The tree genera that this species is known to feed upon occur throughout California.  Therefore, Dryocoetes pini receives a High (3) in this category.

– Low (1) Not likely to establish in California; or likely to establish in very limited areas.

– Medium (2) may be able to establish in a larger but limited part of California.

– High (3) likely to establish a widespread distribution in California.

2) Known Pest Host Range: As stated above, Dryocoetes pini has been reported from several coniferous genera. Therefore, pini receives a Medium (2) in this category.

– Low (1) has a very limited host range.

– Medium (2) has a moderate host range.

– High (3) has a wide host range.

3) Pest Dispersal Potential: Dryocoetes pini is presumably capable of flight. Movement of wood (especially firewood) is a likely pathway for the human-aided dispersal of this species if it was to be introduced.  Reproductive potential is unknown for this species.  Therefore, pini receives a Medium (2) in this category.

– Low (1) does not have high reproductive or dispersal potential.

– Medium (2) has either high reproductive or dispersal potential.

– High (3) has both high reproduction and dispersal potential.

4) Economic Impact: Dryocoetes pini has been reported to be associated with several genera of conifers, including Pinus.  There is a possibility that, if this species was to be introduced to California, it could have a different impact than what is observed in its native range, including killing trees, which could reduce yield of timber.  Significant infestations also have the potential to impact the recreational value of forests.  Therefore, it receives a Low (1) in this category.

Economic Impact:  A

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Economic Impact Score: 1

– Low (1) causes 0 or 1 of these impacts.

– Medium (2) causes 2 of these impacts.

– High (3) causes 3 or more of these impacts.

5) Environmental Impact: Major outbreaks of bark beetles have the potential to kill large numbers of trees, which can have long-lasting impacts. Such impacts could include changes in forest composition, destabilization of soil, and even fire dynamics (Jenkins et al., 2008).  There are rare or threatened conifers in California that could be impacted by the introduction of pini.  Therefore, it receives a High (3) in this category.

Evaluate the environmental impact of the pest on California using the criteria below.

Environmental Impact: A, B

 A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

 B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Environmental Impact Score: 3

– Low (1) causes none of the above to occur.

– Medium (2) causes one of the above to occur.

– High (3) causes two or more of the above to occur.

Consequences of Introduction to California for Dryocoetes pini: Medium (11)

Add up the total score and include it here.

–Low = 5-8 points

–Medium = 9-12 points

–High = 13-15 points

6) Post Entry Distribution and Survey Information: Dryocoetes pini is not known to occur in California.  It receives a Not established (0) in this category.

–Not established (0) Pest never detected in California, or known only from incursions.

–Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

–Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

–High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Final Score:

7) The final score is the consequences of introduction score minus the post entry distribution and survey information score: Medium (11)

Uncertainty:

There is little information available on this species, so it was necessary to draw upon information regarding other species in the genus as well as other bark beetle genera.  There are also no examples of introductions involving this species, so assessment of the impacts of this species requires speculation.

Conclusion and Rating Justification:

Bark beetles can have significant impacts on forests.  One native species in the genus Dryocoetes, D. confusus, is an important pest in western forests.  Even though there is little information on the biology of D. pini, it seems justifiable to use caution and assign it an “A” rating.


References:

CABI.  2017.  Invasive Species Compendium. Wallingford, UK: CAB International. www.cabi.org/isc

European and Mediterranean Plant Protection Organization.  Forest pests on the territories of the former USSR.

https://www.eppo.int/QUARANTINE/special_topics/forestry_project/EPPOforestry_project.pdf

Hansen, E.M.  1996.  Western balsam bark beetle, Dryocoetes confusus Swaine, flight periodicity in northern Utah.  Great Basin Naturalist.  56(4): 348-359.

Jenkins, M.J., Hebertson, E., Page, W., & Jorgensen, C.A.  2008.  Bark beetles, fuels, fires and implications for forest management in the Intermountain West.  Forest Ecology and Management.  254: 16-34.

Niijima, Y.  1909.  Die Scolytiden Hokkaidos unter Berücksichtigung ihrer Bedeutung für Forstschäden.  The Journal of the College of Agriculture, Tohoku Imperial University.  3: 109-179.

Park, S.  2016.  Taxonomic review of Scolytinae and Platypodinae (Coleoptera: Curculionidae) in Korea.  Ph.D. thesis.  Seoul National University.

Shiraki, T.  1952.  Catalogue of injurious insects in Japan.  Preliminary Study Number 71.  General Headquarters, Supreme Commander for the Allied Forces, Economic and Scientific Section, Natural Resources Division.  133 pp.

Symbiota Collections of Arthropods Network.  Accessed March 2, 2018. http://scan1.acis.ufl.edu

Vega, F.E. & Hofstetter, R.W.  2014.  Bark beetles: Biology and ecology of native and invasive species.  Academic Press.  640 pp.


Author:

Kyle Beucke, 1220 N Street, Room 221, Sacramento, CA, 95814, 916-403-6741, plant.health[@]cdfa.ca.gov


Responsible Party:

Jason Leathers, 2800 Gateway Oaks, Sacramento CA 95833, (916) 654-1211, plant.health[@]cdfa.ca.gov


Comment Period:* CLOSED

4/9/18 – 5/24/18


*NOTE:

You must be registered and logged in to post a comment.  If you have registered and have not received the registration confirmation, please contact us at plant.health[@]cdfa.ca.gov.


Comment Format:

♦  Comments should refer to the appropriate California Pest Rating Proposal Form subsection(s) being commented on, as shown below.

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Consequences of Introduction:  1. Climate/Host Interaction: [Your comment that relates to “Climate/Host Interaction” here.]

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♦  Comments may not be posted if they:

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Pest Rating: A

 


Posted by ls 

Pseudocercospora theae

California Pest Rating for
Pseudocercospora theae (Cavara) Deighton 1987
Pest Rating: C

 


PEST RATING PROFILE

Initiating Event: 

On March 6, 2018, the USDA APHIS PPQ requested State Regulatory Officials to review PPQ’s consideration of deregulation of the pathogen, Pseudocercospora theae at US ports of entry.  A ‘Deregulation evaluation of established pests’ report prepared by PERAL was provided for this review.  Therefore, the risk of infestation of P. theae in California is evaluated and a permanent rating is herein proposed.

History & Status:

Background:  Pseudocercospora theae is a fungal plant pathogen in the Mycosphaerellaceae family, that causes leaf spotting known as, bird’s eye spot disease of tea (Camellia spp.). The pathogen has previously been known by its synonyms, Septoria theae and Cecoseptoria theae (Braun et al., 2012; Farr & Rossman, 2018). Holliday (1980) reported that the fungus causes a “very minor” leaf-spotting disease in tea plants.

Pseudocercospora theae has not been reported in California. In the USA, the pathogen has been reported in Florida since about 1955 and disease caused by P. theae has not been reported after 1998.  It is likely that the pathogen is present at non-detectable levels and kept under control by standard disease management practices in nurseries (PPQ, 2018).

Disease cycle: While information on the specific biology of Pseudocercospora theae is limited, it is likely that its disease cycle is like that of other members of the genus.  Generally, Pseudocercospora-infected plants produce conidiophores (specialized hypha) that arise from the plant surface in clusters through stomata and form conidia (asexual spores) successively.  Conidia are easily detached and blown by wind often over long distances.  On landing on surfaces of a plant host, conidia require water or heavy dew to germinate and penetrate the host.  Substomatal stroma (compact mycelial structure) may form from which conidiophores develop.  Development of the pathogen is favored by high temperatures and the disease is most destructive during summer months and warmer climates.  High relative humidity is necessary for conidial germination and plant infection.  The pathogen can overwinter in or on seed and as mycelium (stromata) in old infected leaves (Agrios, 2005).    

Dispersal and spread: Specific information for Pseudocercospora is lacking, however, its mode of dispersal is likely to be like other species of the genus and include air-currents, rain splash/drops, infected plants and propagative material (PPQ, 2018).

Hosts: Camelia sp., C. japonica (Japanese camellia), C. sasanqua (sasanqua camellia), C. sinensis (tea tree; synonyms: Thea assamica, T. sinensis) (Farr & Rossman, 2018).  Although some species of Pseudocercospora are capable of infecting different hosts within a single family (Crous, et al., 2013), there is no evidence that this is true for P. theae (PPQ, 2018).

Symptoms:  Infected host plants exhibit circular leaf spots no greater than 2-3 mm diam., on both sides of a leaf.  The spots are at first purple red, with an indefinite yellow green border and turn white with a narrow purple red ring (Holliday, 1980) with a narrow, raised rim, followed by a dark marginal line or halo (Braun et al., 2012).

Damage Potential: Specific losses due to Pseudocercospora theae have not been reported.  Ornamental plantings of Camellia species may be affected in limited regions of California with sufficient moisture for pathogen infection and development. The climatic suitability of the pathogen encompasses Hardiness Zones 10-13 (PPQ, 2018; Margery et al., 2008).  Nursery production of Camellia species under controlled and conducive conditions for pathogen development would also be of concern in California.  However, P. theae outbreaks in Florida nurseries were successfully controlled by use of proper sanitation practices and fungicide applications (PPQ, 2018), therefore, it is likely that the same will be true for California.  If left uncontrolled, leaf spotting may lead to disease outbreaks under favorable conditions, wherein photosynthetic areas can be reduced, and in severe infections, leaf wilt and drop may be expected.

Worldwide Distribution: Asia: Nepal, Indonesia, India, China, Taiwan, Pakistan, Sri Lanka, Vietnam; Africa: Ethiopia, Malawi, Mauritius, Tanzania, Uganda; Europe: Georgia, Italy, Netherlands Antilles; North America: Florida; South America: Argentina, Brazil, Peru (Braun et al., 2012; EPPO, 2018; Farr & Rossman, 2018).

Official Control: Presently, Pseudocercospora theae is on the ‘Harmful Organism’ list for Colombia (USDA PCIT, 2018).

California Distribution: Pseudocercospora theae has not been reported from California.  The pathogen is not known to be established in California.

California Interceptions:  None reported.

The risk Pseudocercospora theae would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Limited parts of California with adequate moisture, as in coastal regions of the State where Camellia species are grown, are likely to favor establishment of Pseudocercospora theae.

Evaluate if the pest would have suitable hosts and climate to establish in California.

Score: 2

– Low (1) Not likely to establish in California; or likely to establish in very limited areas.

Medium (2) may be able to establish in a larger but limited part of California.

– High (3) likely to establish a widespread distribution in California.

2) Known Pest Host Range: The host range is limited to Camellia [Camelia , C. japonica (Japanese camellia), C. sasanqua (sasanqua camellia), C. sinensis (tea tree)]

Evaluate the host range of the pest. Score:

Low (1) has a very limited host range.

– Medium (2) has a moderate host range.

– High (3) has a wide host range.

3) Pest Dispersal Potential: Reproduction is high and dispersal conidia is through windborne conidia, and rain splash or raindrops. The pathogen is also spread through infected plant propagative material.

Evaluate the natural and artificial dispersal potential of the pest.

Score: 3

– Low (1) does not have high reproductive or dispersal potential.

– Medium (2) has either high reproductive or dispersal potential.

High (3) has both high reproduction and dispersal potential.

4) Economic Impact: Specific losses due to Pseudocercospora theae have not been reported. Ornamental plantings of Camellia species may be affected in limited regions of California with sufficient moisture for pathogen infection and development. Nursery production of Camellia species under controlled and conducive conditions for pathogen development would also be of concern in California.  However, theae outbreaks in Florida nurseries were successfully controlled by use of proper sanitation practices and fungicide applications (PPQ, 2018), therefore, it is likely that the same will be true for California.  Uncontrolled infected plants may lose value, however, with control measures adopted, the impact is expected to be low.

Evaluate the economic impact of the pest to California using the criteria below.

Economic Impact: B

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Low (1) causes 0 or 1 of these impacts.

– Medium (2) causes 2 of these impacts.

– High (3) causes 3 or more of these impacts.

5) Environmental Impact: Home garden plantings of Camellia species may be impacted if the pathogen was to establish under favorable environmental conditions and in the absence of adequate disease control.

Evaluate the environmental impact of the pest on California using the criteria below.

Environment Impact:

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Score the pest for Environmental Impact. Score:

– Low (1) causes none of the above to occur.

Medium (2) causes one of the above to occur.

– High (3) causes two or more of the above to occur.

Consequences of Introduction to California for Pseudocercospora theae: 9

Add up the total score and include it here. (Score)

-Low = 5-8 points

Medium = 9-12 points

-High = 13-15 points

Total points obtained on evaluation of consequences of introduction to California = 9

6) Post Entry Distribution and Survey Information: Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included.

Evaluation is ‘Not established’ in California.

Score: (0)

Not established (0) Pest never detected in California, or known only from incursions.

-Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

-Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

-High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Final Score:

7) The final score is the consequences of introduction score minus the post entry distribution and survey information score: (Score)

Final Score:  Score of Consequences of Introduction – Score of Post Entry Distribution and Survey Information = 9

Uncertainty:

There is very limited information available on the biology of Pseudocercospora theae.

Conclusion and Rating Justification:

Based on the evidence provided above the proposed rating for Pseudocercospora theae is C.


References:

Agrios, G. N.  2005.  Plant Pathology (Fifth Edition).  Elsevier Academic Press, USA.  922 p.

Braun, U., M. Rybak, R. Rybak, and M. G. Cabrera.  2012.  Foliar diseases on tea and mate in Argentina caused by Pseudocercospora species.  Plant Pathology & Quarantine 2 (2): 103-110.  Doi 10.5943/ppq/2/2/2

Crous, P. W., U. Braun, G. C. Hunter, M. J. Wingfield, G. J. M. Verkley, H. -D. Shin, C. Nakashima and J. Z. Groenewald.  2013.  Phylogenetic lineage in Pseudocercospora.  Studies in Mycology 75: 37-114. Published online: 22 May 2012; doi:10.3114/sim0005. Hard copy: June 2013. www.studiesinmycology.org

EPPO.   2018.   Pseudocercospora theae (CERSTH).  PQR database.  Paris, France: European and Mediterranean Plant Protection Organization.  https://gd.eppo.int/

Farr, D.F., & A. Y. Rossman.  2016.  Fungal Databases, Systematic Mycology and Microbiology Laboratory, ARS, USDA.  Retrieved August 1, 2016, from http://nt.ars-grin.gov/fungaldatabases/

Holliday, P.  1980.  Fungus diseases of tropical crops.  Cambridge University Press, New York. 607 pp.

PPQ. 2018.  DEEP report for Pseudocercospora theae (Cavara) Deighton (Mycosphaerellaceae: Capnodiales) – Bird’s eye spot. United States Department of Agriculture, Animal and Plant Health Inspection Service, Plant Protection and Quarantine (PPQ), Raleigh, NC. 4 pp.

USDA PCIT.  2017.  USDA Phytosanitary Certificate Issuance & Tracking System. Retrieved March 21, 2018. 6:36:50 pm CDT.  https://pcit.aphis.usda.gov/PExD/faces/ReportHarmOrgs.jsp.


Responsible Party:

John J. Chitambar, Primary Plant Pathologist/Nematologist, California Department of Food and Agriculture, 3294 Meadowview Road, Sacramento, CA 95832. Phone: 916-262-1110, plant.health[@]cdfa.ca.gov.


*NOTE:

You must be registered and logged in to post a comment.  If you have registered and have not received the registration confirmation, please contact us at plant.health[@]cdfa.ca.gov.


Comment Format:

♦  Comments should refer to the appropriate California Pest Rating Proposal Form subsection(s) being commented on, as shown below.

Example Comment:
Consequences of Introduction:  1. Climate/Host Interaction: [Your comment that relates to “Climate/Host Interaction” here.]

♦  Posted comments will not be able to be viewed immediately.

♦  Comments may not be posted if they:

Contain inappropriate language which is not germane to the pest rating proposal;

Contains defamatory, false, inaccurate, abusive, obscene, pornographic, sexually oriented, threatening, racially offensive, discriminatory or illegal material;

Violates agency regulations prohibiting sexual harassment or other forms of discrimination;

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♦  Comments may be edited prior to posting to ensure they are entirely germane.

♦  Posted comments shall be those which have been approved in content and posted to the website to be viewed, not just submitted.


Pest Rating: C


Posted by ls 

Colletotrichum henanense

California Pest Rating for
Colletotrichum henanense F. Liu & L. Cai 2015
Pest Rating: B

PEST RATING PROFILE

Initiating Event:  

On October 12, 2017, the California Dog Team a shipment of nuts of Castanea sativa (European chestnut) at a parcel distribution facility in Alameda County.  The shipment had originated in Indiana and was destined to a private citizen in Contra Costa County.  A sample of nuts were collected by Alameda County Agricultural officials, and sent to the CDFA Plant Diagnostics Branch for Diagnosis.  Suzanne Latham, CDFA plant pathologist detected the pathogen, Colletotrichum henanense in culture from the nuts. The identity of the associated pathogen was later confirmed by USDA National Identification Services at Beltsville, Maryland, and marked the first domestic detection of C. henanense in the USA.  Consequent to the California detection, all infected plant materials were destroyed. The risk of infestation of C. henanense in California is evaluated and a permanent rating is proposed.

History & Status:

Background:  Colletotrichum henanense is a distinct fungus species belonging to the vastly morphological and physiological variable C. gloeosporioides and is genetically identified from other species of the complex.  The species was originally described in 2015 from tea plants (Camelia sinensis) and Japanese thistle (Cirsium japonicum) in Xinyang, Henan Province, and Beijing, China respectively (Liu et al., 2015).  The pathogen causes anthracnose disease in its host plants.  Camellia species were affected by anthracnose disease in China where the plant species are used as in production of edible oil, processed tea and as ornamentals (Li et al., 2018; Liu et al., 2015).  The pathogen has only been reported from China until its 2017 detection in the California.

Symptoms: Generally, Colletotrichum-infected host plants exhibit symptoms of anthracnose which include dark brown leaf, stem and fruit spots and wilting of leaves which often result in dieback and reduction in plant quality.

HostsCamellia sinensis (tea tree), C. oleifera (tea-oil tree.  Theaceae); Cirsium japonicum (Japanese thistle.  Asteraceae) (De Silva et al., 2017; Li et al., 2018; Liu et al., 2015).  The detection of Colletotrichum henanense in Castanea sativa (European chestnut) is included here (see: Initiating Event).

Symptoms: Colletotrichum henanense causes leaf spot symptoms. Leaf spots or lesions in tea-oil tree are semicircular or half-oval, brown to black with greyish-white centers.  Severely infected leaves wither and drop (Li et al., 2018).

Disease Cycle: It is likely that Colletotrichum henanense has a similar life cycle to that of other Colletotrichum species and survives between crops during winter as mycelium on plant residue in soil, on infected plants, and on seeds.  During active growth, the pathogen produces masses of hyphae (stromata) which bear conidiophores, on the plant surface. Conidia (spores) are produced at the tips of the conidiophores and disseminated by wind, rain, cultivation tools, equipment, and field workers.   Conidia are transmitted to host plants.  Humid, wet, rainy weather is necessary for infection to occur.  These requirements may limit the occurrence of the pathogen in California fields and subsequently, the pathogen may be more of a problem under controlled environments of greenhouses.  Conidia germinate, penetrate host tissue by means of specialized hyphae (appresoria) and invade host tissue.

Transmission: Wind, wind-driven rain, cultivation tools, and human contact.

Damage Potential:  In China, 40% of tea-oil tree yield loss has been suggested (Li et al., 2018).  A 42.5% incidence of anthracnose disease caused by C. henanense was observed in 85 of 200 young tea-oil plants grown in a nursery in Kunming, Yunnan Province, China (Li et al., 2018).  Generally, anthracnose disease can result in reduced plant quality and growth, and marketability.  Nursery productions of Camellia and chestnut are particularly at risk as nursery conditions are often conducive to infection by Colletotrichum species.  In open fields, disease development may be sporadic as it is affected by levels of pathogen inoculum and environmental conditions.

Worldwide Distribution: Asia: China; North America: USA (De Silva et al., 2017; Li et al., 2018; Liu et al., 2015).

Official Control: None reported.

California Distribution Colletotrichum henanense is not established in California (see “Initiating Event”).

California InterceptionsThe risk Colletotrichum henanense would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Like other species of Colletotrichum henanense requires humid, wet, rainy weather for conidia to infect host plants. This environmental requirement and narrow host range may limit the ability of the pathogen to fully establish and spread under dry field conditions.

Evaluate if the pest would have suitable hosts and climate to establish in California.

Score: 2

– Low (1) Not likely to establish in California; or likely to establish in very limited areas.

Medium (2) may be able to establish in a larger but limited part of California.

– High (3) likely to establish a widespread distribution in California.

2) Known Pest Host Range: Presently, the host range is limited to Camellia sinensis, C. oleifera, Cirsium japonicum, and Castanea sativa.

Evaluate the host range of the pest.

Score: 1

Low (1) has a very limited host range.

– Medium (2) has a moderate host range.

– High (3) has a wide host range.

3) Pest Dispersal Potential: Colletotrichum henanense has high reproductive potential and conidia are produced successively.  They are transmitted by wind, wind-driven rain, cultivation tools, and human contact, however, conidial germination and plant infection require long, wet periods.

Evaluate the natural and artificial dispersal potential of the pest.

Score: 3

– Low (1) does not have high reproductive or dispersal potential.

– Medium (2) has either high reproductive or dispersal potential.

High (3) has both high reproduction and dispersal potential.

4) Economic Impact: Anthracnose-infected chestnut and camellia plants may result in lower crop value and market loss.  Nursery productions of Camellia and chestnut are particularly at risk as nursery conditions are often conducive to infection by Colletotrichum  In open fields, disease development may be sporadic as it is affected by levels of pathogen inoculum and environmental conditions. Its economic impact is evaluated as a Medium risk.

Evaluate the economic impact of the pest to California using the criteria below.

Score: B, C

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Economic Impact Score: 2

– Low (1) causes 0 or 1 of these impacts.

Medium (2) causes 2 of these impacts.

– High (3) causes 3 or more of these impacts.

5) Environmental Impact: Chestnut trees cultivated and growing in open environments in California are not expected to be significantly affected by Colletotrichum henanense due to the high moisture conditions required for the development of the pathogen.  However, under humid and moist environments, the pathogen may be more of a problem particularly in ornamental plantings of Camellia in home/urban and private/public settings.

Evaluate the environmental impact of the pest on California using the criteria below.

Environmental Impact: E

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Environmental Impact Score: 2

– Low (1) causes none of the above to occur.

Medium (2) causes one of the above to occur.

– High (3) causes two or more of the above to occur.

Consequences of Introduction to California for Colletotrichum henanense10

Add up the total score and include it here.

-Low = 5-8 points

Medium = 9-12 points

-High = 13-15 points

6) Post Entry Distribution and Survey Information: Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included.

 Evaluation is ‘Not Established’

 Score (0). Colletotrichum henanense is not known to be established in California and is known only from its detected in an intercepted shipment of chestnut.

Not established (0) Pest never detected in California, or known only from incursions.

-Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

-Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

-High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Final Score:

7) The final score is the consequences of introduction score minus the post entry distribution and survey information score: (Score)

Final Score:  Score of Consequences of Introduction – Score of Post Entry Distribution and Survey Information = 10.

Uncertainty:

None.

Conclusion and Rating Justification:

Based on the evidence provided above the proposed rating for the anthracnose pathogen, Colletotrichum henanense, is B.


References:

 De Silva, D. D., P. K. Ades, P. W. Crous and P. W. J. Taylor.  2017.  Colletotrichum species associated with chili anthracnose in Australia.  Plant Pathology 66 (2): 254-267.

Farr, D. F., and A. Y. Rossman. Fungal Databases, U.S. National Fungus Collections, ARS, USDA. Retrieved March 16, 2018, from https://nt.ars-grin.gov/fungaldatabases/

Li, H., G. Y. Zhou, X. Y. Qi and S. Q. Jiang.  2018.  First report of Colletotrichum henanense causing anthracnose on tea-oil trees in China.  Plant Disease “First Look” paper, accepted for publication, posted 01/03/2018. https://doi.org/10.1094/PDIS-08-17-1302-PDN 

Liu, F., Weir, B.S., Damm, U., Crous, P.W., Wang, Y., Liu, B., Wang, M., Zhang, M., and Cai, L. 2015. Unravelling Colletotrichum species associated with Camellia: employing ApMat and GS loci to resolve species in the C. gloeosporioides complex. Persoonia 35: 63-86.


Responsible Party:

John J. Chitambar, Primary Plant Pathologist/Nematologist, California Department of Food and Agriculture, 3294 Meadowview Road, Sacramento, CA 95832. Phone: 916-262-1110, plant.health[@]cdfa.ca.gov.


*NOTE:

You must be registered and logged in to post a comment.  If you have registered and have not received the registration confirmation, please contact us at plant.health[@]cdfa.ca.gov.


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Pest Rating: B


Posted by ls 

Citrus Leaf Blotch Virus

    California Pest Rating for
Citrus leaf blotch virus
Pest Rating: B

PEST RATING PROFILE

Initiating Event:

On February 26, 2018, Dr. G. Vidalakis, University of California, Director, Citrus Clonal Protection Program, informed CDFA of his detection of Citrus leaf blotch virus (CLBV) from a Bearss Lime tree at a residence in Los Angeles County.  Subsequently, an official sample, which comprised a total of 4 subsamples, was collected by the CDFA from the same Bearss Lime tree and sent to the CDFA Plant Pathology Laboratory for diagnosis. On February 27, 2018, Tongyan Tian, CDFA Plant Pathologist, detected Citrus leaf blotch virus from all four subsamples using RT-qPCR and further confirmed the identity of the pathogen by conventional RT-PCR and sequencing. A temporary Q rating was assigned to the pathogen.  The status, risk and consequences of introduction of CLBV to California are assessed and a pest permanent pest rating is proposed herein.

History & Status:

Background: In 1968, Dweet mottle virus (DMV) was initially detected and reported from Riverside, California, during re-indexing of a candidate Cleopatra mandarin variety (C. reticulata) on ‘Dweet’ tangor at the University of California Riverside Citrus Variety Improvement Program, the forerunner of the present Citrus Clonal Protection Program (CCPP).  The candidate mandarin variety had been introduced from Florida into the Program at Riverside.  The virus produced leaf chlorotic blotching symptoms that resembled, but were distinct from, symptoms produced by psorosis virus and Citrus concave gum virus.  It also produced a mild exocortis reaction in Etrog citron.  The parent tree did not show symptoms of damage caused by any known virus and the trunk appeared normal without any signs of stem pitting or bark discoloration, although small fruit, twig dieback and little new growth were apparent.  Since the virus produced symptoms only in ‘Dweet’, it was named Dweet mottle virus (Roistacher & Blue, 1968). However, Dweet mottle virus was not reported from any commercial citrus production sites nor was it observed to produce any economic losses and was detected only once after 1963 in the CCPP indexing program (Krueger et al., 2012).

Then in 1984, at the Citrus Variety Improvement Program in Spain, Navarro and other scientists reported a new graft transmissible disease that caused a bud-union incompatibility between ‘Nagami’ kumquat and ‘Troyer’ citrange rootstock. The ‘Nagami’ kumquat had been introduced from Corsica, France.  In addition to bud-union incompatibility, the presumptive virus involved caused vein clearing in certain citrus species and stem pitting in Etrog citron.  However, after shoot-tip grafting, some plants produced were compatible with Troyer, but still caused stem pitting in Etrog citron, thereby, indicating the involvement of more than one virus (Navarro et al., 1984). Galipienso et al., 2000, gave further evidence of the involvement of more than one virus by demonstrating bud union crease in certain citrus species but not others when propagated on ‘Troyer’ citrange. However, chlorotic blotching in ‘Dweet’ tangor, like those induced by DMV, and stem pitting in Etrog citron were produced by all sources of the virus.  In 2001-02, the causal agent in “Nagami’ kumquat was partially purified and characterized and given the candidate name, Citrus leaf blotch virus (CLBV) (Galipienso et al., 2001; Vives et al., 2001, 2002).  Furthermore, these researchers detected CLBV in different citrus varieties from Japan, New South Wales (Australia), Spain, and Florida, usually associated with abnormal bud union on citrange or citrumelo. Comparison of 14 CLBV isolates from Spain, Japan, USA, France and Australia showed low genetic diversity (Vives et al., 2002).  Low rates of seed transmission were demonstrated in three citrus varieties or hybrids (Guerri et al., 2004).     A few years later, Vives et al., (2005) conducted partial sequence analysis to show that Dweet mottle virus from California had over 96% sequence (high) homology with citrus leaf blotch virus from Spain and therefore, suggested that DMV may be caused by CLBV.  Both viruses induce mottling in ‘Dweet’ tangor and stem pitting in ‘Etrog’ citron and that, besides CLBV, a different pathogen causing bud-union crease and vein clearing may be present in ‘Nagami’ kumquat sources but not in DMV from California source.  This was further demonstrated by Vives et al., (2008a) by the development of full-genome cDNA clones of CLBV that caused systemic infection in agro-inoculated herbaceous and citrus host plants and induced chlorotic blotching in ‘Dweet’ tangor and stem pitting in Etrog citron, but not vein clearing in Pineapple sweet orange or bud union crease on trifoliate rootstocks.  Then in 2010, Hajeri and other researchers at the University of California, Riverside, and the USDA ARS National Clonal Germplasm Repository for Citrus and Dates (NCGRCD), Riverside, determined the complete nucleotide sequence of DMV and with phylogenetic analysis showed that DMV is an isolate of CLBV, and not a distinct species, within the genus Citrivirus.

In California, the seed transmissibility of citrus leaf blotch virus caused concern to the citrus nursery industry.  Consequently, Kreuger et al. (2012) reported that all citrus trees at CCPP and NCGRCD were tested for the presence of the virus using RT-PCR with local DMV positives and a CLBV positive from Florida as positive controls. The virus was not detected in the tested trees.  Furthermore, they failed to detect it during surveys of field trees exhibiting bud union abnormalities for the presence of specific pathogens and therefore, while the overall status of CLBV in California is presently unknown, they believe that this virus if present at all, is only at a low incidence.  This is because the close identity of CLBV and DMV has likely prevented CLBV from becoming introduced into California.  All introductions of new citrus germplasm are indexed into ‘Dweet’ tangor as well as other indicator species at CCPP and NCGRCD. Reaction of CLBV in ‘Dweet’ tangor would enable detection of this virus, even if the actual identity of the virus was not known at the time of indexing. Detection of positives or even misidentifications would have been eliminated by thermal therapy or shoot-tip grafting before release (Kreuger et al., 2005, 2012).

Citrus leaf blotch virus has been reported in China, Corsica (France), Cuba, Italy, Japan, New South Wales (Australia), New Zealand, Spain, Florida, Arkansas, Oregon, and California (USA).  In Arkansas and Oregon, the virus was found in peony plants showing stunting and gnarled irregularities, however, since the virus was found in both symptomatic and asymptomatic material, it could not be associated with the disease and its role in peony health is currently unknown.  Nonetheless, CLBV may easily move between propagation cycles via mechanical and seed transmission of clonally propagated peony plants (Gress et al., 2017).

Citrus leaf blotch virus not only causes symptomless infection in most citrus but also, is unevenly distributed within an infected plant, thereby presenting a possible challenge for its detection. In greenhouse studies, Vives et al. (2002) detected CLBV consistently in young leaves of infected ‘Nagami’ kumquat, ‘Owari’ Satsuma, Navelina and Navel oranges, however, detection in old leaves of other citrus species (Eureka lemon, Marsh grapefruit and Nules Clementine) was not consistent, particularly in Pineapple sweet orange.  Detection of the virus in field trees was even less consistent, and not detected in neighbor trees showing similar symptoms possibly due to low titer or uneven distribution of the virus in the plant.

HostsCitrus spp., including C. sinensis, C. limon, C. unshiu, C. paradisi, Poncirus trifoliata, P. trifoliata x C. sinensis (Harper et al., 2008), C. medica (Etrog citrus), C. reticulata x C. sinensis (‘Dweet’ tangor) (Roistacher & Blue, 1968), Fortunella margarita (kumquat “Nagami’) (Navarro et al., 1984), Prunus avium cv. Red-lamp (sweet cherry) (Wang et al., 2016), Actinidia sp. (kiwifruit) (Zhu et al., 2016), Paeonia lactiflora (peony) (Gress et al., 2017).  Experimental hosts include Nicotiana cavicola (Guardo et al., 2009), N. occidentalis and N. benthamiana (Vives et al., 2008b).

Symptoms: Citrus leaf blotch virus causes symptomless infection in most citrus species and cultivars (Vives et al., 2008a).  However, CLBV (and the isolate, DMV) induce chlorotic blotching or mottling in ‘Dweet’ tangor and stem pitting ‘Etrog’ citron. Although CLBV does not induce bud union crease on trifoliate rootstock (Vives et al., 2008a), it has been found to be usually associated with abnormal bud union on citrange or citrumelo rootstock. A different pathogen or interaction of CLBV with a different pathogen is likely the cause of bud union crease and vein clearing symptoms (Vives et al., 2005).

Damage Potential: Citrus leaf blotch virus causes chlorotic leaf blotching in ‘Dweet’ tangor and stem pitting in Etrog citron.  Although it does not induce bud union crease in several citrus species it is usually associated with bud union crease symptoms in citrange and citrumelo rootstocks and therefore, an interaction between CLBV and other agent(s) cannot be ruled out.  There are no reports of yield losses due to CLBV and the virus can cause symptomless infections in most citrus species and cultivars. In California, CLBV (aka DMV) is a regulated pathogen and its distribution is unknown or at best likely to be of low incidence. CLBV (aka DMV) was not reported from any commercial citrus production sites in California nor was it observed to produce any economic losses (Krueger et al., 2012).  However, in certain scion-rootstock combinations using ‘Dweet’ tangor and Etrog citron rootstocks there may be a potential for disease development due to CLBV.

TransmissionCitrus leaf blotch virus is transmitted in citrus by grafting and seed.  CLBV dispersal occurs primarily by propagation of infected buds.  Low rates of seed transmission in at least three citrus species and hybrid, ‘Troyer’ citrange (Citrus sinensis x Poncirus trifoliata), ‘Nagami’ kumquat (Fortunella margarita) and sour orange (C. aurantium), has been demonstrated (Guerri et al., 2004).  Also, CLBV has been mechanically transmitted to Nicotiana cavicola (Guardo et al., 2009), by sap inoculation to N. occidentalis and N. benthamiana (Vives et al., 2008b), and transmitted from citrus to citrus by contaminated knife blades (Roistacher et al., 1980).  The virus is not transmitted by vectors (Galipienso et al., 2000).

Worldwide Distribution: Asia: China, Japan; Europe: Italy, Spain; North America: USA, Cuba; Oceania: New South Wales (Australia), New Zealand (Cao et al., 2017; Gress et al., 2017; Guardo et al., 2007; Harper et al., 2008; Hernández-Rodríguez, 2016; Navarro et al., 1984; Roistacher & Blue, 1968; Vives et al., 2002; Wang et al., 2016).

Official Control: Citrus leaf blotch virus is on the ‘Harmful Organism’ list for Uruguay (USDA PCIT, 2018).  CLBV (aka DMV) is a regulated pathogen in California’s mandatory Citrus Nursery Stock Pest Cleanliness Program (CCR, Title 3, Division 4, Chapter 4, Subchapter 6, Section 3701).

California Distribution: The distribution in California is unknown.  If at all present, it is likely to be only at a low incidence (Kreuger et al., 2005, 2012.  See: ‘Background’).

California Interceptions: No official interceptions have been reported.

The risk Citrus leaf blotch virus would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Although the distribution of Citrus leaf blotch virus in California, is presently unknown and is likely to be only at a low incidence (Kreuger et al., 2012), if not regulated, it may be possible for the pathogen to have a widespread establishment in symptomatic and non-symptomatic infected citrus varieties in commercial citrus-growing regions of the State.

Evaluate if the pest would have suitable hosts and climate to establish in California.  Score: 3

– Low (1) Not likely to establish in California; or likely to establish in very limited areas.

– Medium (2) may be able to establish in a larger but limited part of California.

High (3) likely to establish a widespread distribution in California.

2) Known Pest Host Range: The natural host range is limited primarily to Citrus  Other hosts include sweet cherry and kiwifruit reported from China and peony reported from Arkansas and Oregon. Experimental hosts include, Nicotiana cavicola, N. occidentalis and N. benthamiana.

Evaluate the host range of the pest.

Score: 1

Low (1) has a very limited host range.

– Medium (2) has a moderate host range.

– High (3) has a wide host range.

3) Pest Dispersal Potential: Citrus leaf blotch virus has high reproduction within its plant host, although unevenly distributed within infected plants. It is transmitted by grafting, seed, and mechanically. Its ability for long distance spread through infected seed render it a high rating for dispersal.

Evaluate the natural and artificial dispersal potential of the pest.

Score: 3

– Low (1) does not have high reproductive or dispersal potential.

– Medium (2) has either high reproductive or dispersal potential.

High (3) has both high reproduction and dispersal potential.

4) Economic Impact: Citrus leaf blotch virus is a regulated pathogen under California’s mandatory Citrus Nursery Stock Pest Cleanliness Program.  Under this program any citrus stock found positive for the pathogen would be eliminated before release for commercial planting.  This pathogen causes chlorotic leaf blotching in ‘Dweet’ tangor and stem pitting in Etrog citron.  Although it does not induce bud union crease in several citrus species, it is usually associated with bud union crease symptoms in citrange and citrumelo rootstocks and therefore, an interaction between CLBV and other agent(s) cannot be ruled out.  There are no reports of yield losses due to CLBV and the virus can cause symptomless infections in most citrus species and cultivars. Researchers have stated that CLBV has not been reported from commercial citrus production sites in California nor was it observed to cause any economic losses.  If citrus stock were not regulated, it is likely that in certain scion-rootstock combinations using ‘Dweet’ tangor and Etrog citron rootstocks there may be a potential for disease development due to CLBV. In such a case, it is estimated that CLBV could lower crop yield and value and trigger the loss of markets.

Evaluate the economic impact of the pest to California using the criteria below.

Economic Impact: A, B, C

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Economic Impact Score: 3

– Low (1) causes 0 or 1 of these impacts.

– Medium (2) causes 2 of these impacts.

High (3) causes 3 or more of these impacts.

5) Environmental Impact: No environmental impact is expected, however, if not regulated, CLBV may impact home/urban plantings of citrus host plants.

Evaluate the environmental impact of the pest on California using the criteria below.

Environmental Impact: E

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E.  The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Environmental Impact. Score: 2

– Low (1) causes none of the above to occur.

Medium (2) causes one of the above to occur.

– High (3) causes two or more of the above to occur.

Consequences of Introduction to California for Citrus leaf blotch virus: 12

Add up the total score and include it here. (Score)

-Low = 5-8 points

Medium = 9-12 points

-High = 13-15 points

6) Post Entry Distribution and Survey Information: Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included. (Score)

Evaluation is (0). While the distribution of CLBV in California is currently not known, there is no evidence that it is established within the State.

Not established (0) Pest never detected in California, or known only from incursions.

-Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

-Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

-High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Final Score:

7) The final score is the consequences of introduction score minus the post entry distribution and survey information score: (Score)

Final Score:  Score of Consequences of Introduction – Score of Post Entry Distribution and Survey Information = 12   

Uncertainty:

The in-state distribution of CLBV is not currently known.  Also, the impact of infection related to crop damage and losses is not known.

Conclusion and Rating Justification:

Based on the evidence provided above the proposed rating for Citrus leaf blotch virus is B.


References:

Cao, M. J., Y. -Q. Yu, X. Tian, F. Y. Y. and, R. H. Li and C. Y. Zhou.  2017.  First report of Citrus leaf blotch in lemon in China.  Plant Disease 101: 8.  https://doi.org/10.1094/PDIS-10-16-1500-PDN

Galipienso, L., L. Navarro, J. F. Ballester-Olmos, J. Pina, P. Moreno, and J. Guerri.  2000.  Host range and symptomatology of a graft transmissible pathogen causing bud union crease of citrus on trifoliate rootstocks. Plant Pathology 49: 308–314.

Galipienso, L., M. C. Vives, P. Moreno, R. G. Milne, L. Navarro and J. Guerri.  2001.  Partial characterization of Citrus leaf blotch virus, a new virus from Nagami kumquat.  Archives of Virology 146: 357–368.

Gress, J. C., S. Smith, and I. E. Tzanetakis.  2017.  First report of Citrus leaf blotch virus in peony in the U.S.A. Plant Disease 101: 637. https://doi.org/10.1094/PDIS-08-16-1218-PDN

Guardo, M., G Sorrentino, T. Marletta and A. Carusa.  2007.  First report of Citrus leaf blotch on kumquat in ItalyPlant Disease 91: 104.

Guardo, M., O. Potere, M. A. Castellano, V. Savino and A. Caruso.  2009.  A new herbaceous host for Citrus leaf blotch virus. Journal of Plant Pathology 91: 485-488.

Guardo, M., G. Sorrentino and A. Caruso.  2015.  Characterization and incidence of Citrus leaf blotch virus in Southern Italy.  12th International Citrus Congress – International Society of Citriculture. Acta Horticulturae 1065: 825-83.

Hajeri, S., C. Ramadugu, M. Keremane, G. Vidalakis and R. Lee.  2010.  Nucleotide sequence and genome organization of Dweet mottle virus and its relationship to members of the family Betaflexiviridae.  Arch Virol 15: 1523-1527.  DOI 10.1007/s00705-010-0758-1

Harper, S. J., K. M. Chooi and M. N. Pearson.  2008.  First report of Citrus leaf blotch virus in New Zealand.  Plant Disease 92: 1470.  https://doi.org/10.1094/PDIS-92-10-1470C

Hernàndez-Rodríguez, L., J. M. Pérez-Castro, G. García-García, P. Luis Ramos-González, V. Zamora-Rodríguez, Xenia Ferriol-Marchena, Inés Peña-Bárzaga and L. Batista-Le Riverend.  2016.  Citrus leaf blotch in Cuba: first report and partial molecular characterization.  Tropical Plant Pathology 41: 147. https://doi.org/10.1007/s40858-016-0078-4

Krueger, R. R., J. A. Bash and R. F. Lee.  2005.  Phytosanitary status of California citrus.  International Organization of Citrus Virologists Conference Proceedings (1957-20), 16 (16): 468-472.  https://escholarship.org/uc/item/3667q9qn

Krueger, R. R., J. A. Bash and R. F. Lee.  2012.  Dweet mottle virus and Citrus leaf blotch virus.  http://ucanr.edu/blogs/blogcore/postdetail.cfm?postnum=7112

Navarro, L., J. A. Pina, J. F. Ballester-Olmos, P. Moreno and M. Cambra.  1984.  A new graft transmissible disease found in Nagami kumquat. In: Timmer L. W., and J. A. Dodds (eds) Proceedings of the 9th Conference of the International Organization of Citrus Virologists, IOCV, Riverside, pp 234–240.

Roistacher, C. N., and R. L. Blue.  1968.  A psorosis-like virus causing symptoms only on ‘Dweet’ tangor.  International Organization of Citrus Virologists Conference Proceedings (1957-2010), 4(4): 13-18.

Roistacher, C. N., E. M. Nauer and R. C. Wagner.  1980.  Transmissibility of cachexia, Dweet mottle, psorosis and infectious variegation viruses on knife blades and its prevention.  Proceedings of the 8th Conference of the International Organization of Citrus Virologists, IOCV, Riverside 1980: 225-229.

USDA PCIT.  2018. USDA Phytosanitary Certificate Issuance & Tracking System. Retrieved March 15, 2018. 3:25:54 pm CDT.  https://pcit.aphis.usda.gov/PExD/faces/ReportHarmOrgs.jsp.

Vives, M. C., L. Galipienso, L. Navarro, P. Moreno and J. Guerri.  2001.  The nucleotide sequence and genomic organization of Citrus leaf blotch virus: Candidate type species for a new virus genus.  Virology 287: 225-233.

Vives, M. C., L. Galipienso, L. Navarro, P. Moreno and J. Guerri.  2002.  Citrus leaf blotch virus: a new citrus virus associated with bud union crease on trifoliate rootstocks.  International Organization of Citrus Virologists Conference Proceedings (1957-2010), 15 (15): 205-212.

Vives, M. C., L. Rubio, L. Galipienso, L. Navarro, P. Moreno and J. Guerri.  2002.  Low genetic variation between isolates of Citrus leaf blotch virus from different host species and different geographical origins. Journal of General Virology 83: 2587–2591.

Vives M. C., J. A. Pina, J. Juarez, L. Navarro, P. Moreno and J. Guerri.  2005.  Dweet mottle disease is probably caused by Citrus leaf blotch virus. 16th Conference of the International Organization of Citrus Virologists Conference Proceedings (1957-2010), 15 (16): 251-256.

Vives, M. C., S. Martin, S. Ambros, A. Renovell, L. Navarro, J. A. Pina, P. Moreno, J. and J. Guerri.  2008a.  Development of a full-genome cDNA clone of Citrus leaf blotch virus and infection of citrus plants. Molecular Plant Pathology 9:787–797.

Vives, M. C., P. Moreno, L. Navarro and J. Guerri.  2008b.  Citrus leaf blotch virus.  In: Rao, G. P., A. Myrta and K. Ling (eds).  Characterization, Diagnosis and Management of Plant Viruses, vol. 2. Pp. 55-67.  Studium Press, Houston, TX, USA.

Wang, J., D. Zhu, Y. Tan, X. Zong, H. Wei and Q. Liu.  2016. First report of Citrus leaf blotch virus in sweet cherry.  Plant Disease 100:1027.

Zhu, Chen-xi, Wang, Guo-ping, Zheng, Ya-zhou, Yang, Zuo-kun, Wang, Li-ping, Xu, Wen-xing and N. Hong.  2016.  RT-PCR detection and sequence analysis of coat protein gene of Citrus leaf blotch virus infecting kiwifruit trees.  Acta Phytopathologica Sinica, 46 (1): 11.


Responsible Party:

John J. Chitambar, Primary Plant Pathologist/Nematologist, California Department of Food and Agriculture, 3294 Meadowview Road, Sacramento, CA 95832. Phone: 916-262-1110, plant.health[@]cdfa.ca.gov.


*NOTE:

You must be registered and logged in to post a comment.  If you have registered and have not received the registration confirmation, please contact us at plant.health[@]cdfa.ca.gov.


Comment Format:

♦  Comments should refer to the appropriate California Pest Rating Proposal Form subsection(s) being commented on, as shown below.

Example Comment:
Consequences of Introduction:  1. Climate/Host Interaction: [Your comment that relates to “Climate/Host Interaction” here.]

♦  Posted comments will not be able to be viewed immediately.

♦  Comments may not be posted if they:

Contain inappropriate language which is not germane to the pest rating proposal;

Contains defamatory, false, inaccurate, abusive, obscene, pornographic, sexually oriented, threatening, racially offensive, discriminatory or illegal material;

Violates agency regulations prohibiting sexual harassment or other forms of discrimination;

Violates agency regulations prohibiting workplace violence, including threats.

♦  Comments may be edited prior to posting to ensure they are entirely germane.

♦  Posted comments shall be those which have been approved in content and posted to the website to be viewed, not just submitted.


Pest Rating: B


Posted by ls 

Banded Wood Snail | Cepaea nemoralis

BANDED WOOD SNAIL
California Pest Rating for
Banded Wood Snail  |  Cepaea nemoralis
Gastropoda: Helicidae  
Pest Rating: A

PEST RATING PROFILE
Initiating Event:

Cepaea nemoralis is frequently intercepted by CDFA. A pest rating proposal is required to support its permanent pest rating.

History & Status:

Background: Cepaea nemoralis, known as the banded wood snail, is the most common species of land snail in Europe and has been introduced to North America. This snail is commonly found in urban areas, where it inhabits gardens and abandoned lots. They feed on dead and living plant material, carrion, fungi, moss, and insects1.

          Cepaea nemoralis has a yellow, pink, or brown shell. The shell contains five dark bands. Banded wood snails are hermaphrodites, but cross fertilization occurs (each snail fertilizes the other). They often mate multiple times prior to egg-laying and can store sperm for up to 15 months. Eggs are buried in moist soil, hatching after about three weeks. The snails reach maturity in four years and may live as  long as five to nine years 1, 4.

Worldwide Distribution: Banded wood snails are distributed throughout much of Europe, extending to Poland.  This snail was introduced into North America during the nineteenth century, and it is currently found in Virginia, New York, Ontario, and Massachusetts1, 2.

Official Control: Banded wood snail is listed as a harmful organism in Canada, Israel, Japan, and Taiwan6.

California Distribution: Banded wood snails have never been found in the environment of California.

California Interceptions: Between January 2000 and August 2017, banded wood snails have been intercepted 20 times.  These interceptions include border station inspections and high risk pest exclusion activities.

The risk Cepaea nemoralis (Banded wood snail) would pose to California is evaluated below.

Consequences of Introduction:
  1. Climate/Host Interaction: Banded wood snails can feed on a variety of live and dead plants and dead animals and insects, including remains of ants, beetles, spiders, mites, springtails, and aphids. Banded wood snails may establish in larger, but limited, warm agricultural and metropolitan areas of California. It receives a Medium (2) in this category.

Evaluate if the pest would have suitable hosts and climate to establish in California:

  • Low (1) Not likely to establish in California; or likely to establish in very limited areas.
  •  Medium (2) may be able to establish in a larger but limited part of California.
  • High (3) likely to establish a widespread distribution in California.

2. Known Pest Host Range: Banded wood snails are highly polyphagous and are known to feed on a wide variety of live and dead plants and animals. It receives a High (3) in this category.

Evaluate the host range of the pest.

  • Low (1) has a very limited host range.
  • Medium (2) has a moderate host range.
  • High (3) has a wide host range.

3. Pest Dispersal Potential: Banded wood snails are obligately outcrossing hermaphrodites, with both individuals exchanging sperm during mating, and both individuals able to lay eggs afterward. On average, they lay 30-80 eggs that hatch in 15-20 days. Breeding takes place from April through October. The snail’s foot is used to create a cavity in the soil where the eggs are deposited1, 4. It receives a High (3) in this category.

Evaluate the natural and artificial dispersal potential of the pest.

  • Low (1) does not have high reproductive or dispersal potential.
  • Medium (2) has either high reproductive or dispersal potential.
  • High (3) has both high reproduction and dispersal potential

4. Economic Impact: The banded wood snail is not expected to lower crop yields. It could reduce the value of nursery stock by disfiguring plants with its presence and increase crop production costs in nurseries and orchards. The banded wood snail is a potential vector of Angiostrongylus vasorum, the French heartworm (a disease of wild and domestic canids) 3. It receives a High (3) in this category. Economic Impact: B, C, E: Environmental Score: 3

Evaluate the economic impact of the pest to California using the criteria below.

A. The pest could lower crop yield.
B. The pest could lower crop value (includes increasing crop production costs).
C. The pest could trigger the loss of markets (includes quarantines).
D. The pest could negatively change normal cultural practices.
E. The pest can vector, or is vectored, by another pestiferous organism.
F. The organism is injurious or poisonous to agriculturally important animals.
G. The organism can interfere with the delivery or supply of water for agricultural uses.

  • Low (1) causes 0 or 1 of these impacts.
  • Medium (2) causes 2 of these impacts.
  • High (3) causes 3 or more of these impacts.

5. Environmental Impact: If introduced, the banded wood snail is not expected to lower biodiversity, disrupt natural communities, or change ecosystem processes. It might trigger new chemical treatments in orchards and nurseries and by residents who find infested plants unsightly. It is not expected to significantly impact cultural practices, home/urban gardening, or ornamental plantings. It receives a Medium (2) in this category.

Environmental Impact: A, D:  Environmental Impact: Score: 2

Evaluate the environmental impact of the pest on California using the criteria below.

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.
B. The pest could directly affect threatened or endangered species.
C. The pest could impact threatened or endangered species by disrupting critical habitats.
D. The pest could trigger additional official or private treatment programs.
E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

  • Low (1) causes none of the above to occur.
  • Medium (2) causes one of the above to occur.
  • High (3) causes two or more of the above to occur.
Consequences of Introduction to California for Cepaea nemoralis(Banded wood snails): High (13) 
  • Low = 5-8 points
  • Medium = 9-12 points
  • High = 13-15 points

Post Entry Distribution and Survey Information: The banded wood snail has never been found in the environment in California and receives a Not Established (0) in this category

Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included.

Not established (0) Pest never detected in California, or known only from incursions.
Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).
Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.
 High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Final Score:

The final score is the consequences of introduction score minus the post entry distribution and survey information score: Medium (13)

Uncertainty:

Banded wood snails are commonly intercepted. There have been no formal surveys for this snail in the state. It is therefore possible that it could be present in some locations in California. 

Conclusion and Rating Justification:

Banded wood snail is not known to occur in California and might cause significant economic and environmental impacts if it were to become established here. Currently, an “A” rating is justified.

References:
  1. Animal Diversity Web. Accessed September 7, 2017. http://animaldiversity.org/accounts/Cepaea_nemoralis/

2. Encyclopedia of Life. Accessed September 7, 2017.
http://eol.org/pages/449909/details#overview

3. G.A. Conboy. 2000. Canine Angiostrongylosis (French Heartworm). Accessed September 7, 2017.
http://www.ivis.org/advances/Parasit_Bowman/conboy_angiostrongylosis/ivis.pdf

4. Maggie Whitson. 2005. Journal of the Kentucky Academy of Science, 66(2):82-88. Accessed September 7, 2017. 
http://stoppinginvasives.com/dotAsset/e2bbc1b0-81c5-42b1-b9e4-8123952c6c02.pdf

5. Pest and Damage Record Database, California Department of Food and   Agriculture, Plant Health and Pest Prevention Services.
http://phpps.cdfa.ca.gov/user/frmLogon2.asp

6. USDA phytosanitary Certificate Issuance & Tracking System (PCIT) Phytosanitary Export Database (PExD). Accessed September 7, 2017.
https://pcit.aphis.usda.gov/pcit/


Author:

Javaid Iqbal,  California Department of Food and Agriculture; 1220 N Street, Sacramento, CA 95814; Tel. (916) 403-6695; plant.health[@]cdfa.ca.gov.

Responsible Party:

Jason Leathers; California Department of Food and Agriculture; 1220 N Street, Sacramento, CA 95814; Tel. (916) 654-1211; plant.health[@]cdfa.ca.gov.


Pest Rating: A


Posted by dk

Alligatorweed | Alternanthera philoxeroides

California Pest Rating for
white flower with green leaves
Alligatorweed | Alternanthera philoxeroides
Family:  Amaranthaceae
Pest Rating: A | Proposed Seed Rating: R

PEST RATING PROFILE
Initiating Event:

There was a recent find of alligatorweed in Solano County; this is the first detection in northern California in many years.

History & Status:

Background: Alligatorweed is a perennial herb with horizontal to ascending stems to 1 m long, rooting at the nodes. The flowers are small and borne in small heads with white floral bracts. Like many aquatic emergent, it has distinctive submerged and emersed forms. The submerged form has hollow, floating, emergent and submerged stems. Terrestrial plants have solid stems. Typically, plants grow rooted in soil in shallow water and form dense, interwoven floating mats that extend over the surface of deeper water. Mats can become quite dense and nearly impenetrable. The floating mats can break away and follow currents to colonize new sites. Mats disrupt the natural ecology of a site by reducing light penetration and crowding out native species. Serious infestations can create anoxic, disease-promoting, and mosquito-breeding conditions.

Worldwide Distribution: This weed is found in wet, disturbed areas. It is also a weed of rice and sugar cane fields in tropical and subtropical regions. Native to southern Asia, alligatorweed is now found in tropical and subtropical regions around the world. It is considered an invasive species in Australia, China, New Zealand, and Thailand. Alligatorweed has been introduced throughout the southeastern United States from Virginia to Texas.

Official Control: Alligatorweed has had a CDFA rating of A as a pest in California for decades. The population in Los Angeles County has been managed intermittently over the years by the county, but it still persists.  It has official status as a weed in Alabama, Arizona, Arkansas, California, Florida, South Carolina, and Texas.

California Distribution:  Alligatorweed occurs in several southern California counties. It also has been detected in Contra Costa and Kings Counties, where it is eradicated. There was a recent find of 2 colonies in southern Solano County.

California Interceptions: Alligatorweed has been sent to CDFA by land managers.

The risk Alternanthera philoxeroides (alligatorweed) poses to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Risk is Medium (2), as the plant occurs in wetlands such as the Delta and creeks and rivers, as well as irrigation canals and watering ponds. These habitats are limited but widely distributed in California.

Evaluate if the pest would have suitable hosts and climate to establish in California:

– Low (1) Not likely to establish in California; or likely to establish in very limited areas.

Medium (2) may be able to establish in a larger but limited part of California.

– High (3) likely to establish a widespread distribution in California.

2) Known Pest Host Range: Most plants do not require any one host, but grow wherever ecological conditions are favorable. It receives a High (3) in this category.

Evaluate the host range of the pest.

– Low (1) has a very limited host range.

– Medium (2) has a moderate host range.

High (3) has a wide host range.

3) Pest Dispersal Potential: Risk is Medium (2). Alligatorweed can spread rapidly via water movement and on boats and equipment as stem fragments. It is also grown as an aquarium plant and occasionally discarded into waterways. Seeds evidently are not produced in the United States.

Evaluate the natural and artificial dispersal potential of the pest.

– Low (1) does not have high reproductive or dispersal potential.

Medium (2) has either high reproductive or dispersal potential.

– High (3) has both high reproduction and dispersal potential.

4) Economic Impact: Risk is High (3), as the plant can lower crop yields in rice fields, trigger state or international quarantines, and force changes in cultural practices by blocking canals. It has spread widely in the southeast, and has proven difficult to eradicate both there and in California. Its mats can improve habitat for mosquito larvae, leading to larger mosquito populations.

Evaluate the economic impact of the pest to California using the criteria below.

Economic Impact: A, C, D, E, G

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Economic Impact Score: 3

– Low (1) causes 0 or 1 of these impacts.

– Medium (2) causes 2 of these impacts.

High (3) causes 3 or more of these impacts.

5) Environmental Impact: Risk is High (3) as alligatorweed could further invade the water systems of California, disrupt natural wetland communities and potentially lower biodiversity by invading wetlands. The dense growth impedes water movement, blocks the growth of native plants, and reduces available habitat for water birds and fish. Its invasion in the Delta and its tributaries could degrade habitat of rare species such as Mason’s lilaeopsis (Lilaeopsis masonii), Sacramento River Chinook salmon (Oncorhynchus tshawytscha),  and Giant garter snake (Thamnophis gigas).  Its presence would trigger additional control measures.

Evaluate the environmental impact of the pest on California using the criteria below.

Environmental Impact: A, C, D

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Environmental Impact: Score: 3

– Low (1) causes none of the above to occur.

– Medium (2) causes one of the above to occur.

High (3) causes two or more of the above to occur.

Consequences of Introduction to California for Alternanthera philoxeroides (alligatorweed) : High (13)

-Low = 5-8 points

-Medium = 9-12 points

High = 13-15 points

6) Post Entry Distribution and Survey Information: Alligatorweed currently is known from 3-4 populations in northern and southern California. It receives a Medium (-2) in this category.

Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included:

Score: -2

-Not established (0) Pest never detected in California, or known only from incursions.

-Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

-High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Final Score:

The final score is the consequences of introduction score minus the post entry distribution and survey information score: Medium (11)

Uncertainty:

Uncertainty is low, as alligatorweed has established in wetlands in California and other states. There is some uncertainty as to the actual distribution of this plant in California, as, like some other aquatic weeds, it is likely to be overlooked.

Conclusion and Rating Justification:

Conclusions of the harm(s) associated with this pest to California using all of the evidence presented above:

Proposed Rating: Despite its limited ability to disperse between watersheds, this is a potentially significant weed in California of both natural wetlands and irrigation canals. Because of its potential economic impacts, it deserves an A rating, as it has proven tenacious and is actively spreading.

References:

Baldwin, B. G., D. H. Goldman, D. J. Keil, R. Patterson, T. J. Rosatti, and D. H. Wilken, editors. 2012. The Jepson manual: vascular plants of California, second edition. University of California Press, Berkeley.

Consortium of California Herbaria. Accessed 10/3/2017:  ucjeps.berkeley.edu/consortium/

Florida Dept of Agriculture Weed of the Month: Alternanthera sessilis. Accessed 10/3/2017: http://www.freshfromflorida.com/Divisions-Offices/Plant-Industry/Plant-Industry-Publications/Weed-of-the-Month/April-2011-Alternanthera-Sessilis

Invasive Plant Atlas of the Mid-South. alligatorweed. Accessed 10/3/2017:    https://www.gri.msstate.edu/ipams/species.php?CName=Alligatorweed


Responsible Party:

Dean G. Kelch, Primary Botanist; California Department of Food and Agriculture; 1220 N Street, Sacramento, CA 95814; Tel. (916) 403-6650. plant.health[@]cdfa.ca.gov.


*NOTE:

You must be registered and logged in to post a comment.  If you have registered and have not received the registration confirmation, please contact us at plant.health[@]cdfa.ca.gov.


Pest Rating: A | Proposed Seed Rating: R


Posted by ls

Nutria | Myocastor coypus

California Pest Rating for
Nutria  |  Myocastor coypus
Pest Rating: A

PEST RATING PROFILE
Initiating Event

On March 30, 2017 a suspected Nutria (Myocastor coypus) was turned in to California Department of Fish and Wildlife staff in Merced County. It was confirmed by the local Department of Fish and Wildlife Services trapper.  The animal was found living in a managed wetland (duck hunting club) adjacent to the Grasslands Ecological Area in Merced County.

History & Status

Background

Nutria are large aquatic rodents that may easily be confused with the even larger North American Beaver (Castor Canadensis). Their long rat-like tail is the primary distinguishing characteristic when compared to the large paddle shaped tail of the beaver. Nutria are herbivores that may consume up to 25% of their body-weight per day, in addition they are wasteful feeders focusing on roots and tubers while discarding up to 90% of the plant matter they harvest. They may impact crops and landscape plantings in areas adjacent to water ways, damage water conveyance and storage structures, undermine roads and vector parasites and diseases to humans and livestock. Nutria are primarily nocturnal, though lack of predatory pressure or the influence of human feeding may cause an increase in daytime activity. Nutria are prolific breeders, females may have 2-3 liters per year with an average of 4-5 offspring per liter. Young become sexually active between four and six months of age. Nutria nest in dense vegetation and construct burrows for protection from cold temperatures. Burrows can range from 6-45 meters in length. Nutria have been found to cause significant damage to wetland and riparian habitats and are considered agricultural pests in many parts of the world. In the early 1900’s they were purposefully introduced in many parts of the world to supplement the trapping of furbearing animals for the fur trade. In nature, their populations are primarily limited by harsh winters, commercial trapping and large predators such as alligators or large snakes. Nutria have successfully established in brackish estuarine waters around the United States, however they are not capable of natural immigration in to California with its mountains, deserts and coastline borders.

map for predicted suitable habitat
Figure 1. Geographical extent of predicted suitable nutria habitat (based on 2003 – 2007 mechanistic model) in the contiguous United States compared to the status of nutria populations by state. (Sheffels 2013)

Worldwide Distribution

Native to South America. Nutria are a common invasive species in the Southeastern United States. Blamed for significant impacts and loss of wetlands in the Mississippi Delta as well as the Chesapeake Bay. They are widespread in the Pacific Northwest, including Oregon, Washington and Southern British Columbia. Nutria have been successfully introduced and established in every continent other than Australia and Antarctica (Chesapeake Bay Nutria Eradication Project 2016).

Official Control:

A bounty system has been used in the past in Louisiana. During the 2009-2010 trapping season the state of Louisiana paid a $5 per animal bounty on 445,963 Nutria harvested for a total of $2,229,815 (Coastwide Nutria Control Program).

When necessary USDA – Wildlife Services will control localized populations of Nutria.  In 2002 an eradication program was initiated in the state of Maryland. As of 2016 all known populations had been removed from the Delmarva Peninsula of the Chesapeake Bay in Maryland. Surveillance is currently ongoing to verify eradication (Chesapeake Bay Nutria Eradication Project 2016).

Washington State requires any trapped Nutria to be immediately euthanized and prohibits their movement (Washington Invasive Species Council 2016).

Nutria are Considered an agricultural pest in China. Nutria eradication is underway in Japan. They are known to be responsible for damage to fish ponds in Israel. Nutria are considered a pest in Western Europe but a valuable resource in Eastern Europe where fur has higher value. England initiated a trapping eradication in 1981 and declared eradication in 1989. There are numerous Nutria eradication programs in France. They are considered a pest in Germany due to damage to dams. Nutria are also considered a pest of rice production in Italy. (Carter and Leonard 2002)

California Distribution:

There are historical reports of Nutria from Elizabeth Lake, Stanislaus River and Los Angeles County. The first introduction to the United States occurred at Elizabeth Lake California in 1899 which failed due to breeding failures. The California Department of Food and Agriculture conducted an eradication program for a feral population of Nutria from the Stanislaus River during the 1960’s. Eradication was achieved by 1978 (National Wetlands Research Center 2015).

Recent modeling of Nutria distribution and climate change predict that California is highly suitable for Nutria establishment and spread. The mountainous terrain and disconnected hydrological units are the only barrier between Northern California and the Nutria infested waterways of Southern Oregon (Jarnevich et al. 2017).

California Interceptions:

One adult Nutria was trapped in a managed wetland (duck hunting club) adjacent to the Grasslands Ecological Area in Merced County. There are anecdotal reports of additional Nutria sightings from the duck club caretaker.

Consequences of Introduction

The risk Nutria would pose to California is evaluated below.

Problems associated with high Nutria populations fall into several categories: destruction of marsh habitat, destruction of water control structures such as dykes and levees, destruction of agricultural crops, and the fact that the animals can serve as repositories of a variety of diseases.

1) Climate/Host Interaction: Evaluate if the pest would have suitable hosts and climate to establish in California. Score: 3

Low (1) Not likely to establish in California; or likely to establish in very limited areas.

Medium (2) may be able to establish in a larger but limited part of California.

High (3) likely to establish a widespread distribution in California.

Recent modeling data found that the majority of California could provide suitable habitat for Nutria. High elevations and deserts being the only limiting factors. Nutria could easily move throughout the inland waterways and irrigation networks.

2) Known Pest Host Range: Evaluate the host range of the pest. Score: 2

Low (1) has a very limited host range.

Medium (2) has a moderate host range.

High (3) has a wide host range.

Nutria are an aquatic species. Distribution would be limited to areas adjacent to waterways. Rivers, streams, estuaries and irrigation canals would all be suitable habitat. The interconnected waterways throughout the Sacramento-San Joaquin River and Delta and irrigated lands are all susceptible to Nutria establishment.

3) Pest Dispersal Potential: Evaluate the natural and artificial dispersal potential of the pest. Score: 3

Low (1) does not have high reproductive or dispersal potential.

Medium (2) has either high reproductive or dispersal potential.

High (3) has both high reproduction and dispersal potential.

Nutria could naturally disperse throughout the entire Sacramento-San Joaquin Bay-Delta watershed which covers over 75,000 square miles from Tehachapi to the Cascades Mountain Range. They could also establish around natural and man-made lakes, reservoirs, irrigation canals and other waterbodies.

4) Economic Impact: Evaluate the likely economic impacts of the pest to California using the criteria below. Score: 3

Economic Impact: A, B, E, G

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Economic Impact Score: 3

Low (1) causes 0 or 1 of these impacts.

Medium (2) causes 2 of these impacts.

High (3) causes 3 or more of these impacts.

Nutria have shown to damage rice and orchards/vineyards potentially lowering crop yield and causing losses.  There is also potential for them to disrupt water delivery to crops and spread contaminants impacting food safety.  They are known to vector liver flukes and other parasites to livestock, damage water conveyance and storage infrastructure.

5) Environmental Impact: Evaluate the environmental impact of the pest on California using the criteria below. Score: 3

Environmental Impact: A, B, C, D, E

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Environmental Impact Score: 3

Low (1) causes none of the above to occur.

Medium (2) causes one of the above to occur.

High (3) causes two or more of the above to occur.

Nutria have contributed to massive wetland destruction and land loss. Nutria could feed directly on threatened or endangered wetland and riparian plants. Nutria have created eat-outs completely denuding vast areas of habitat, their burrowing activity also contributes to increased siltation of waterways which can impact fish habitat. Many areas of the United States currently have control and eradication programs targeting Nutria. In addition to being agricultural pests and damaging the environment Nutria have also impacted urban and residential landscaping, transmit parasites to animals and humans and become aggressive towards humans and pets.

Consequences of Introduction to California for Nutria:

Add up the total score and include it here. (14)

Low = 5-8 points

Medium = 9-12 points

High = 13-15 points

6) Post Entry Distribution and Survey Information: Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included. (-1)

Not established (0) Pest never detected in California, or known only from incursions.

Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Nutria have successfully been eradicated from California in an area close to the current location of the detections. There is only one other documented introduction in 1899 which failed to establish. There are no PDR records of other encounters in the State.

Final Score

The final score is the consequences of introduction score minus the post entry distribution and survey information score: (13)

Uncertainty

It is important to separate out uncertainty from risk. Use this section to evaluate any uncertainty associated with the introduction of the pest to California.

The three primary limiting factors of Nutria populations are harsh winters, commercial trapping and large predator populations. California has very mild winters compared to other infested areas of the world. Fur trapping is a very insignificant activity in California due to social as well as regulatory constraints and low fur prices. California does not have large populations of predators nor predators large enough to effectively take Nutria. The Southeastern U.S. has alligators and the portions of Africa that have not been impacted have many different species of large carnivores.

Conclusion and Rating Justification

Proposed rating of A.

Nutria have proven to be a significant agricultural pest in other parts of the world with similar climates and cropping systems to California. Significantly impacted crops include rice, orchards and vineyards. In addition, Nutria are a known vector of ectoparasites and diseases. Livestock are particularly susceptible to liver flukes if exposed to water soiled by Nutria excrement (Menard et al.2000). Nutria have caused extensive damage to waterways, water storage and conveyance as well as adjacent rights-of-way. Of particular concern would be the thousands of miles of earthen canal, dikes and levees comprising much of the Central Valley irrigation infrastructure (Witmer et al. 2012).

Nutria have caused extreme environmental degradation to wetlands around the United States. Their feeding behavior can produce “eat outs” which eliminate the aquatic vegetation which contains wetland and marsh soils. The subsequent erosion is extremely damaging to wetlands. In addition, this erosion combined with their burrowing activity has the potential to damage fish habitat through increased siltation. In the Chesapeake Bay estuary one of the most heavily impacted habitat types is the Spartina sp. complex similar to much of the San Francisco Bay estuary.

Due to the documented negative impacts to agriculture and the environment of Nutria establishment and the high probability of eradication in California, a rating of A is justified.


References

Carter, Jacoby, and Billy P. Leonard. “A Review of the Literature on the Worldwide Distribution, Spread of, and Efforts to Eradicate the Coypu (Myocastor coypus).” Wildlife Society Bulletin (1973-2006), vol. 30, no. 1, 2002, pp. 162–175.  www.jstor.org/stable/3784650

Chesapeake Bay Nutria Eradication Project.  “U.S. Fish and Wildlife Service Species of Concern Fact Sheet: Nutria.” (2016) Aquatic Nuisance Species Task Force.  https://www.fws.gov/chesapeakenutriaproject/

Coastwide Nutria Control Program. “Home. Nutria Control Program” (2007) Louisiana Department of Wildlife and Fisheries.  http://www.nutria.com/site9.php

Jarnevich CS, Young NE, Sheffels TR, Carter J, Sytsma MD, Talbert C “Evaluating simplistic methods to understand current distributions and forecast distribution changes under climate change scenarios: an example with coypu (Myocastor coypus).” (2017) NeoBiota 32: 107-125. https://doi.org/10.3897/neobiota.32.8884

Menard A; M. L’Hostis, G. Leray, S. Marchandeau, M. Pascal, N. Roudot, V. Michel and A. Chauvin “Inventory of Wild Rodents and Lagomorphs as Natural Hosts of Fasciola hepatica on a Farm Located in a Humid Area in Loire Atlantique (France)” (2000), Parasite, 7, 77-82 http://dx.doi.org/10.1051/parasite/2000072077

National Wetlands Research Center. “Worldwide Distribution, Spread of, and Efforts to Eradicate the Nutria (Myocastor coypus).”(2015) United Stated Geological Survey (USGS). https://www.nwrc.usgs.gov/special/nutria/namerica.htm

Pasko, Susan and Anne Marie Eich, “Species of Concern Fact Sheet: Nutria” (2011) Aquatic Nuisance Species Task Force.  https://www.anstaskforce.gov/spoc/nutria.php

Sheffels, Trevor Robert, “Status of Nutria (Myocastor coypus) Populations in the Pacific Northwest and Development of Associated Control and Management Strategies, with an Emphasis on Metropolitan Habitats” (2013).Dissertations and Thesis.Paper 665. http://pdxscholar.library.pdx.edu/cgi/viewcontent.cgi?article=1664&context=open_access_etds

Washington Invasive Species Council. “Stop the Invasion. Nutria, Myocastor coypus” (2016) Washington Department of Fish and Wildlife. http://www.invasivespecies.wa.gov/documents/priorities/NutriaFactSheet.pdf

Witmer, Gary; Sheffels, Trevor R.; and Kendrot, Stephen R., “The Introduction, Impacts, And Management of a Large, Invasive, Aquatic Rodent in The United States” (2012). USDA National Wildlife Research Center – Staff Publications. Paper 1215. http://digitalcommons.unl.edu/icwdm_usdanwrc/1215/


Responsible Party:

David Kratville, Senior Environmental Scientist, California Department of Food and Agriculture, 3294 Meadowview Road, Sacramento, CA 95832. Phone: 916-262-1102, plant.health[@]cdfa.ca.gov.


NOTE:

You must be registered and logged in to post a comment.  If you have registered and have not received the registration confirmation, please contact us at plant.health[@]cdfa.ca.gov.


Pest Rating: A


Posted by ls

Vertebrate Pests

Vertebrate pests are any species of mammal, bird, reptile, amphibian, or fish that causes damage to agricultural, natural, or industrial resources, or to any other resource, and to the public health or safety. Vertebrate pests cause millions of dollars in damage to agricultural crops, transportation infrastructure, water conveyance and restoration lands each year. Vertebrate pests threaten the public health and the environment as vectors of diseases that could be transmitted to humans, livestock and wildlife.


PEST RATINGS:

Nutria |  Myocastor coypus
Pest Rating:  A

Stemphylium solani G. F. Weber 1930

California Pest Rating for
Stemphylium solani G. F. Weber 1930
Pest Rating: A

PEST RATING PROFILE
Initiating Event:

On March 31, 2017, the CDFA Permits and Regulations Program requested a rating for Stemphylium solani.  Therefore, the associated risk and current status of S. solani in California are assessed here and a permanent rating is proposed.

History & Status:

Background:   Stemphylium solani is a fungal pathogen that causes Gray leaf spot disease in tomato, and Stemphylium leaf blight disease in cotton, garlic, and other hosts.  Gray leaf spot in tomato is actually caused by three species of Stemphylium, one being S. solani and the other two species: S. lycopersici (Enjoji) W. Yaman (syn. S. floridanum Hannon & G. F. Weber) and S. botryosum Wallr. f. sp. lycopersici Rotem, Y. Cohen, & I. Wahl.  Gray leaf spot is regarded one of the most destructive diseases of tomato in the southeastern United States and throughout the world wherever warm and humid conditions prevail (Jones & Pernezny, 2014).

Gray leaf spot disease has been reported from several countries worldwide including the United States (see ‘Worldwide Distribution’). In the United States, the disease was first observed in 1924 and by 1928 had spread throughout Florida causing widespread defoliation. Since then, the pathogen has been reported from several states but has never been reported from California.

Disease development:  The disease begins in infested seedbeds and transplant houses or field-transplanted seedlings, usually when the plants are in the first true-leaf stage of growth.  Cotyledons are not severely infected.   The pathogen is spread when infected seedlings are transplanted to fields.  Conidia (asexual spores) can be spread over extensive distances by wind. The teleomorph or sexual stage of S. solani is not known.  The disease is favored by warm temperatures (24-27°C) and high humidity. Spore germination and infection of plant are dependent on the presence of free moisture (dew or rain) (Jones & Pernezny, 2014).  Leaf wetness is considered more important than temperature in establishment of infection (Cerkauskas, 2005).  Stemphylium solani survives as a saprophyte on infected plant debris or on volunteer tomato, pepper, gladiolus, blue lupine, and other wild solanaceous plants.  In the southern state climates, the pathogen remains viable on tomato plants which are grown throughout the year (Jones & Pernezny, 2014).  The pathogen can be seedborne (Koike et al., 2007).

Dispersal and spread: Infected plants, seedlings, and plant debris.  Conidia may be wind-blown over extensive areas or by splashing water (Jones & Pernezny, 2014).

Hosts: Hosts of Stemphylium solani are included primarily in the plant family Solanaceae.  Numerous other plant families are also included with their associated hosts, including Amaryllidaceae (Allium sp.), Asteraceae (Lactuca sp.), and Malvaceae (Gossypium hirsutum).  Hosts include, Aegiceras corniculatum (black mangrove), Allium sativum (garlic), Aster sp. (aster), Basella rubra (Malabar spinach), Capsicum annuum (bell pepper), C. annuum var. annuum (cayenne pepper), C. frutescens (chili pepper), Carthamus sp. (distaff thistles), Cirsium sp. (thistle), Citrus sp. (citrus), Convolvulus arvensis (field bindweed), Cucumis sativus (cucumber), Dactylis glomerata (orchardgrass), Dianthus caryophyllus (carnation), Gossypium hirsutum (upland cotton), Ipomoea reptans (synonym: I. aquatica, swamp morning-glory), Kalanchoe blossfeldiana (flaming katy), Lactuca sativa (lettuce), Lupinus angustifolius (narrowleaf lupine), Lupinus sp. (lupine), Lycopersicon esculentum (synonym: L. lycopersicum, tomato), Lycopersicon sp., Pelargonium zonale (horse-shoe pelargonium), Physalis pubescens (husk tomato), Physalis sp. (groundcherry), Solanum gilo (gilo), S. lycocarpum (wolf apple), S. lycopersicum (garden tomato), S. melongena (aubergine/eggplant), S. melongena var. esculentum, S. pseudocapsicum (Jerusalem cherry), S. tuberosum (potato), Vicia faba (fava bean), Vigna sinensis (synonym: V. unguiculata, cowpea) (CABI, 2017; Farr & Rossman, 2017).

Symptoms:  Gray leaf spots or lesions are almost entirely limited to the leaf blades, but under favorable conditions, lesions may develop on petioles and on the more tender parts of growing stems.  Lesions on stems are linear and parallel to the stem.  Fruit symptoms have not been observed.  In infected tomatoes, symptoms of gray leaf spot are first exhibited as minute brownish-black specks on the lower leaves.  Randomly scattered circular to oblong spots develop on adaxial and abaxial leaf surfaces without being restricted by leaf veins.  The spots may be surrounded by a narrow yellow halo and enlarge to about 2.1 mm in diameter while individual spots on the base of leaves may enlarge to twice that size or more in diameter and occasionally coalesce, thereby, killing large portions of the leaf blade. As the spots enlarge, the centers turn gray, eventually dry, crack, and fall out.  Frequently, at this stage entire leaves conspicuously turn yellow, especially if the infection is severe, and die rapidly, turning brown before dropping from the plants.  Seedbed infections result in marked defoliation without conspicuous yellowing (Jones & Pernezny, 2014; Damicone & Brandenberger, 2015).  In garlic, early symptoms of S. solani infection were observed as white spots (1-3 mm), which enlarged to sunken purple lesions, extending until the leaves withered (Zheng et al., 2008).

Damage Potential:  Gray leaf spot almost entirely affects leaves, and defoliation can be severe reducing available photosynthetic areas of infected plants thereby, resulting in reductions in plant development, quality, and fruit yields.  In China, garlic leaf blight caused by Stemphylium solani affected over 7,000 ha of field production and reduced yields up to 70% (Zheng et al., 2010).  During 1994 and 1995, a severe epidemic of leaf blight of cotton in Brazil resulted in yield losses up to 100% in some commercial fields (Mehta, 1998). Gray leaf spot disease limited tomato production in Venezuela and Malaysia (Cadeño & Carrero, 1997; Nasehi et al., 2012).   In California, processing tomatoes are grown in the warm and dry San Joaquin and Sacramento Valleys while fresh-market tomatoes are grown in the San Joaquin Valley, Central Valley, Central and Southern Coastal regions and the Imperial Valley.  It is less likely that S. solani will be able establish under warm and dry regions of the state’s tomato production acreages, as well as under the possible use of resistant varieties, protectant fungicides and cultural management strategies.  However, for tomato and other host plants under wet and warm climates, the pathogen may be able to establish within those regions.

Worldwide Distribution: Asia: Brunei Darussalam, China, Hong, Kong, Taiwan, Thailand, Korea, Malaysia; Africa: Libya, Mauritius, Senegal, Sudan, Tanzania; Europe: Greece, Spain; North America: Canada, USA (Alabama, Florida, Georgia, Indiana, Louisiana, Maryland, Mississippi, North Carolina, New Jersey, South Carolina, Tennessee, Texas, Virginia); South America: Brazil, Honduras, Venezuela; Central America and Caribbean: Cuba; Oceania: American Samoa (CABI, 2017; Cadeño & Carrero, 1997; Farr & Rossman, 2017).

Official Control: Presently, Stemphylium solani is on the Harmful Organisms list for Peru (USDA-PCIT, 2017).

California Distribution: Stemphylium solani has not been reported from California.

California Interceptions: None reported.

The risk Stemphylium solani would pose to California is evaluated below.

Consequences of Introduction: 

1) Climate/Host Interaction: Although Stemphylium solani has a wide host range that includes several economically important agricultural crops in California as well as wild solanaceous plants, the pathogen is dependent on leaf wetness for plant infection and additionally on warm temperatures for disease development.  The disease is most severe under humid and overcast climate conditions that favor wet foliage mainly due to dew or rain.  These conditions would allow the pathogen to establish in a larger but limited part of California.

Evaluate if the pest would have suitable hosts and climate to establish in California.

Score: 2

– Low (1) Not likely to establish in California; or likely to establish in very limited areas.

Medium (2) may be able to establish in a larger but limited part of California.

– High (3) likely to establish a widespread distribution in California.

2) Known Pest Host Range: Stemphylium solani has a wide host range of plants included primarily in the family Solanaceae. However, numerous other plant families are also included with their associated hosts.  Economically important crops include tomato, pepper, cotton, citrus, cucumber, lettuce, garlic, eggplant and others.  Several wild solanaceous host plants could allow build-up of fungal inoculum.

Evaluate the host range of the pest.

Score: 3

– Low (1) has a very limited host range.

– Medium (2) has a moderate host range.

High (3) has a wide host range.

3) Pest Dispersal Potential: Conidia are produced in abundance and readily dispersed by wind and splashing water. Also, the pathogen is spread through infected plants, seedlings, plant debris, and seed.

Evaluate the natural and artificial dispersal potential of the pest.

Score: 3

– Low (1) does not have high reproductive or dispersal potential.

– Medium (2) has either high reproductive or dispersal potential.

High (3) has both high reproduction and dispersal potential.

4) Economic Impact: Stemphylium solani causes gray leaf spot in tomato and peppers as well as leaf blight in other hosts. Leaves are almost always entirely affected by the disease and defoliation can be severe reducing available photosynthetic areas of plants thereby, resulting in reductions in plant development, quality, and fruit yields.  If not controlled, significant reductions in crop yield and markets could occur.  Use of fungicides and cultural management practices could increase costs of crop production.

Evaluate the economic impact of the pest to California using the criteria below.

Economic Impact: A, B, C, D

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Economic Impact Score: 3

– Low (1) causes 0 or 1 of these impacts.

– Medium (2) causes 2 of these impacts.

High (3) causes 3 or more of these impacts.

5) Environmental Impact:  The pathogen could significantly affect home/urban gardening of agricultural crops and ornamental hosts.

Evaluate the environmental impact of the pest on California using the criteria below.

Environmental Impact: E

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Environmental Impact Score: 2

– Low (1) causes none of the above to occur.

Medium (2) causes one of the above to occur.

– High (3) causes two or more of the above to occur.

Consequences of Introduction to California for Stemphylium solani: High (13)

Add up the total score and include it here.

-Low = 5-8 points

-Medium = 9-12 points

High = 13-15 points

6) Post Entry Distribution and Survey Information: Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included.

Evaluation is Not establishedin California.

Score: (0)

Not established (0) Pest never detected in California, or known only from incursions.

-Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

-Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

-High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Final Score:

7) The final score is the consequences of introduction score minus the post entry distribution and survey information score: (Score)

Final Score:  Score of Consequences of Introduction – Score of Post Entry Distribution and Survey Information = 13

Uncertainty:  

None.

Conclusion and Rating Justification:

Based on the evidence provided above the proposed rating for Stemphylium, solani is A.

References:

CABI, 2017.  Stemphylium solani (gray leaf spot) basic datasheet.  Crop Protection Compendium. http://www.cabi.org/cpc/datasheet/51531

Cerkauskas, R.  2005.  Tomato diseases, Gray leaf spot, Stemphylium solani, S. lycopersici found worldwide in warm climates.  AVRDC – The World Vegetable Center Fact Sheet.  AVRDC Publication 05-634.

Cadeño, L., and C. Carrero.  1997.  First report of tomato gray leaf spot caused by Stemphylium solani in the Andes Region of Venezuela.  Plant Disease 81: 1332. http://dx.doi.org/10.1094/PDIS.1997.81.11.1332B

Damicone, J. P., and L. Brandenberger.  2015.  Common diseases of tomatoes Part 1.  Diseases caused by fungi.  Oklahoma Cooperative Extension Service EPP-7625.

Farr, D. F., and A. Y. Rossman.  2017.  Fungal Databases, U. S. National Fungus Collections, ARS, USDA. Retrieved April 3, 2017, from http://nt.ars-grin.gov/fungaldatabases/

Jones, J. P., and K. L. Pernezny.  2014.  Gray Leaf Spot.  In Compendium of Tomato Disease and Pests Second Edition.  Ed. J. B. Jones, T. A. Zitter, T. M. Momol, and S. A. Miller, APS Press. The American Phytopathological Society.  29-30 p.

Koike, S. T., P. Gladders, and A. O. Paulus.  2007.  Stemphylium solani, S. lycopersici – gray leaf spot.  In Vegetables diseases a color handbook.  Academic Press, an imprint of Elsevier, Burlington, San Diego.  211-212 p.

Mehta, Y. R.  1998.  Severe outbreak of Stemphylium leaf blight, a new disease of cotton in Brazil. Plant Disease, 82: 333-336.

Nasehi, A., J. B. Kadir, M. A. Zainal Abidin, M. Y. Wong, and F. Mahmodi.  First report of tomato gray leaf spot disease caused by Stemphylium solani in Malaysia.  Plant Disease 96: 1226.  http://dx.doi.org/10.1094/PDIS-03-12-0223-PDN

USDA PCIT.  2017.  USDA Phytosanitary Certificate Issuance & Tracking System. April 3, 2017, 1:17:10 pm CDT.  https://pcit.aphis.usda.gov/PExD/faces/ReportHarmOrgs.jsp.

Zheng, L., J. B. HUANG, and T. HSIANG.  2008.  First report of leaf blight of garlic (Allium sativum) caused by Stemphylium solani in China. Plant Pathology 57: 380.

Zheng, L., L. V. Rujing, J. Huang, D. Jiang, X. Liu, and T. Hsiang.  2010.  Integrated control of garlic leaf blight caused by Stemphylium solani in China.  Canadian Journal of Plant Pathology 32: 135-145.


Responsible Party:

John J. Chitambar, Primary Plant Pathologist/Nematologist, California Department of Food and Agriculture, 3294 Meadowview Road, Sacramento, CA 95832. Phone: 916-262-1110, plant.health[@]cdfa.ca.gov.


Comment Format:

♦  Comments should refer to the appropriate California Pest Rating Proposal Form subsection(s) being commented on, as shown below.

Example Comment:
Consequences of Introduction:  1. Climate/Host Interaction: [Your comment that relates to “Climate/Host Interaction” here.]

♦  Posted comments will not be able to be viewed immediately.

♦  Comments may not be posted if they:

Contain inappropriate language which is not germane to the pest rating proposal;

Contains defamatory, false, inaccurate, abusive, obscene, pornographic, sexually oriented, threatening, racially offensive, discriminatory or illegal material;

Violates agency regulations prohibiting sexual harassment or other forms of discrimination;

Violates agency regulations prohibiting workplace violence, including threats.

♦  Comments may be edited prior to posting to ensure they are entirely germane.

♦  Posted comments shall be those which have been approved in content and posted to the website to be viewed, not just submitted.


Pest Rating: A


Posted by ls

Pseudocercospora purpurea (Cooke) Deighton 1976

California Pest Rating for
Pseudocercospora purpurea (Cooke) Deighton 1976
Pest Rating: B

PEST RATING PROFILE
Initiating Event:

On November 17, 2016, USDA APHIS PPQ inquired if CDFA had conducted a pest risk assessment of the fungal pathogen, Pseudocercospora purpurea on avocados in California.  Subsequently, the risk of infestation of P. purpurea in California is evaluated and a permanent rating is herein proposed.

History & Status:

BackgroundPseudocercospora purpurea is a fungal plant pathogen that causes Pseudocercospora (Cercospora) spot (blotch) disease exhibiting leaf and fruit spot symptoms in Persea spp., including avocado (P. americana) plants. The pathogen was originally known as Cercospora purpurea. In South Africa, the disease is known as black spot or Cercospora spot and is the most serious pre-harvest disease affecting all cultivars of avocado, particularly, cv. Fuerte (Crous et al., 2000; Pohronezny et al., 1994).  The disease occurs in warm, humid and rainy climates and is found in southeastern USA, South America, northern Australia, Asia, Africa, and the Caribbean (CABI, 2016; Menge & Ploetz, 2003).  The pathogen has not been reported from California.

Disease cycle:  Initial inoculum of conidia (asexual spores) mostly comes from infected leaves.  New shoot tissues are infected wherever this disease occurs.  The pathogen penetrates host tissue either directly or through wounds. Conidia are easily detached and blown by wind often over long distances.  On landing on surfaces of a plant host, conidia require water or heavy dew to germinate and penetrate the host.  In South Africa, the pathogen remains latent for about 3 months after penetration.  Infected plants produce conidiophores (specialized hypha) that arise from the plant surface in clusters through stomata and form conidia successively.  Substomatal stroma (compact mycelial structure) may form from which conidiophores develop.  Fruit are susceptible when developed to a quarter to three-quarter of their full size.  Very small fruit (< 4 cm diameter) and those at or near maturity are almost immune.  Disease development is severe during warm, rainy weather when fruit are about a quarter size (Agrios, 2005; Menge & Ploetz, 2003; Pohronezny et al., 1994).  High relative humidity is necessary for conidial germination and plant infection.  The pathogen can overwinter as mycelium (stromata) in old infected leaves (Agrios, 2005).  

Dispersal and spread: Wind, rain, irrigation water, infected nursery plants, infected leaves, insects (Menge & Ploetz, 2003).

Hosts: Avocado is the main host; Persea spp. in the family Lauraceae, namely, P. americana (syn. P. gratissima, avocado), P. borbonia (redbay), P. drymifolia (Mexican avocado), P. palustris (swamp bay), and Persea sp. (Farr & Rossman, 2016).

Symptoms: Symptoms occur on leaves, stems, and fruit (Pohronezny et al., 1994).  On leaves, lesions initially appear as small (1-5 mm) angular, purple to purplish brown flecks or spots near leaf margins.  Over time, chlorotic halos surround older spots and are visible on both leaf surfaces.  The fungus sporulates under high humid conditions, appearing as gray, felty mycelial growths in the center of lesions. Individual lesions may coalesce forming larger regions of necrotic tissue.  Leaves become curled, deformed and may fall.

On fruit, lesions initiate as small flecks which later become slightly sunken, expand or coalesce becoming somewhat circular, and turn brown to brownish black in color.  Fissures or cracks usually develop in fruit lesions and serve as avenues for infection by other pathogens.  In certain cases, if the disease is temporarily arrested, the lesions appear as minute, raised, shiny, black specks associated with the corking of lenticels.  While blotch is usually confined to the rind of fruit, in advanced cases, the flesh may be invaded.  Once defoliation occurs, fruit may turn chlorotic, shrivel and drop.  Dark brown to black, 2-10 mm lesions may also form on green twigs and fruit pedicels (Pohronezny et al., 1994; Menge & Ploetz, 2003).

Damage Potential:  Pseudocercospora spot (blotch) is one of the most common diseases of avocado in Florida (Pohronezny et al., 1994).  Losses in avocado production may be severe and have been reported to be up to 69% in non-sprayed orchards in South Africa (Pohronezny et al., 1994; Menge & Ploetz, 2003).  Photosynthetic area can be reduced due to leaf spotting.  In severe infections, leaf wilt and drop may be expected.  In California, avocado production is a major industry producing 75% and 92% of the nation’s avocado fruit supplies (Lazicki et al., 2016).  Therefore, losses due to this pathogen is of particular concern.

Worldwide Distribution: Pseudocercospora purpurea is widespread in subtropical and tropical regions.  Asia:  India, Japan, Philippines; Africa: Cameroon, Democratic Republic of Congo, Côte d’Ivoire, Guinea, Kenya, South Africa; North America: Bermuda, Mexico, USA; Central America and Caribbean: Dominica, El Salvador, Honduras, Jamaica, Nicaragua, Panama, Puerto Rico, Trinidad and Tobago, United States Virgin Islands; South America: Argentina, Bolivia, Brazil, Chile, Guyana, Peru, Venezuela; Oceania: Australia, Palau (CABI, 2016; Farr & Rossman, 2016).

In the USA, the pathogen has been found in the states of Florida, Georgia, and Mississippi (CABI, 2016).

Official Control:  Presently, Cercospora purpurea (syn. Pseudocercospora purpurea) is on the ‘Harmful Organism Lists’ for Namibia and South Africa and P. purpurea is on the ‘Harmful Organism Lists’ for French Polynesia and New Caledonia (USDA PCIT, 2016).

California Distribution: Pseudocercospora purpurea has not been reported from California.  The pathogen is not known to be established in California.

California Interceptions:  None reported.

The risk Pseudocercospora purpurea would pose to California is evaluated below.

Consequences of Introduction: 

1) Climate/Host Interaction: Evaluate if the pest would have suitable hosts and climate to establish in California:

Score: 2

– Low (1) Not likely to establish in California; or likely to establish in very limited areas.

Medium (2) may be able to establish in a larger but limited part of California.

– High (3) likely to establish a widespread distribution in California.

Risk is Medium (2): In California, Pseudocercospora purpurea may be able to establish on avocado, under high moisture and warm climate conditions.  In the State, avocados are grown mostly along the southern coast (Lazicki et al., 2016).

2) Known Pest Host Range: Evaluate the host range of the pest.

Score: 1

Low (1) has a very limited host range.

– Medium (2) has a moderate host range.

– High (3) has a wide host range.

Risk is Low (1)The host range for Pseudocercospora purpurea is limited to Persea spp. with avocado being the main host.

3) Pest Dispersal Potential: Evaluate the natural and artificial dispersal potential of the pest.

Score: 3

– Low (1) does not have high reproductive or dispersal potential.

– Medium (2) has either high reproductive or dispersal potential.

High (3) has both high reproduction and dispersal potential.

Risk is High (3)Pseudocercospora purpurea has high reproductive potential resulting in the successive production of conidia which are mainly dependent on wind, rain, and infected plants for dispersal and spread.

4) Economic Impact: Evaluate the economic impact of the pest to California using the criteria below:

A. The pest could lower crop yield.

B. The pest could lower crop value (includes increasing crop production costs).

C. The pest could trigger the loss of markets (includes quarantines).

D. The pest could negatively change normal cultural practices.

E. The pest can vector, or is vectored, by another pestiferous organism.

F. The organism is injurious or poisonous to agriculturally important animals.

G. The organism can interfere with the delivery or supply of water for agricultural uses.

Score: 3

– Low (1) causes 0 or 1 of these impacts.

– Medium (2) causes 2 of these impacts.

High (3) causes 3 or more of these impacts.

Risk is High (3):  Infected host plants with leaf and fruit spot symptoms caused by Pseudocercospora spot (blotch) disease could lower value and yield of commercially produced avocado plants as well as affect nursery productions resulting in loss of markets.

5) Environmental Impact: Evaluate the environmental impact of the pest on California using the criteria below:

A. The pest could have a significant environmental impact such as lowering biodiversity, disrupting natural communities, or changing ecosystem processes.

B. The pest could directly affect threatened or endangered species.

C. The pest could impact threatened or endangered species by disrupting critical habitats.

D. The pest could trigger additional official or private treatment programs.

E. The pest significantly impacts cultural practices, home/urban gardening or ornamental plantings.

Score the pest for Environmental Impact:

Score: 2

– Low (1) causes none of the above to occur.

Medium (2) causes one of the above to occur.

– High (3) causes two or more of the above to occur.

Risk is Medium (2):  The pathogen could significantly impact avocado plants grown for fruit and aesthetic value in private residential and public environments.

Consequences of Introduction to California for Pseudocercospora purpurea:

Add up the total score and include it here:

-Low = 5-8 point

Medium = 9-12 point

-High = 13-15 points

Total points obtained on evaluation of consequences of introduction to California = 11

6) Post Entry Distribution and Survey Information: Evaluate the known distribution in California. Only official records identified by a taxonomic expert and supported by voucher specimens deposited in natural history collections should be considered. Pest incursions that have been eradicated, are under eradication, or have been delimited with no further detections should not be included.

Score: 0

Not established (0) Pest never detected in California, or known only from incursions.

-Low (-1) Pest has a localized distribution in California, or is established in one suitable climate/host area (region).

-Medium (-2) Pest is widespread in California but not fully established in the endangered area, or pest established in two contiguous suitable climate/host areas.

-High (-3) Pest has fully established in the endangered area, or pest is reported in more than two contiguous or non-contiguous suitable climate/host areas.

Evaluation is not established (0):  Pseudocercospora purpurea is not established in California.

Final Score:

7) The final score is the consequences of introduction score minus the post entry distribution and survey information score:

Final Score:  Score of Consequences of Introduction – Score of Post Entry Distribution and Survey Information = 11

Uncertainty:  

None.

Conclusion and Rating Justification:

Based on the evidence provided above the proposed rating for Pseudocercospora purpurea is B.

References:

Agrios, G. N.  2005.  Plant Pathology (Fifth Edition).  Elsevier Academic Press, USA.  922 p.

CABI.  2016.  Pseudocercospora purpurea (spot blotch) (basic) datasheet.  Crop Protection Compendium.  http://www.cabi.org/cpc/datasheet/12266 .

Crous, P.W., A. J. L. Phillips, A. P. and Baxter.  2000.  Phytopathogenic fungi from South Africa. University of Stellenbosch, Department of Plant Pathology Press, 358 pages (referenced by Farr & Rossman, 2016).

Farr, D. F., & A. Y. Rossman.  2016.  Fungal Databases, Systematic Mycology and Microbiology Laboratory, ARS, USDA.  Retrieved August 18, 2016, from http://nt.ars-grin.gov/fungaldatabases/.

Lazicki, P., D. Geisseler, and W. R. Horwath.  2016.  Avocado production in California. https://apps1.cdfa.ca.gov/FertilizerResearch/docs/Avocado_Production_CA.pdf. (Last updated April, 2016.)

Menge, J. A., and R. C. Ploetz.  2003.  Disease of Avocado.  In Diseases of Tropical Fruit Crops, Edited by R. C. Ploetz, CABI Publishing, CAB International, UK, USA, 527 p.

Pohronezny, K. L., G. W. Simone, and J. Kotzé.  1994.  Pseudocercospora spot (blotch).  In Compendium of Tropical Fruit Diseases, Edited by R. C. Ploetz, G. A. Zentmeyer, W. T. Nishijima, K. G. Rohrbach, and H. D. Ohr, APS Press, The American Phytopathological Society, 79-80 p.

Responsible Party:

John J. Chitambar, Primary Plant Pathologist/Nematologist, California Department of Food and Agriculture, 3294 Meadowview Road, Sacramento, CA 95832. Phone: 916-262-1110, plant.health[@]cdfa.ca.gov.


Comment Format:

♦  Comments should refer to the appropriate California Pest Rating Proposal Form subsection(s) being commented on, as shown below.

Example Comment: 

Consequences of Introduction:  1. Climate/Host Interaction: [Your comment that relates to “Climate/Host Interaction” here.]

♦  Posted comments will not be able to be viewed immediately.

♦  Comments may not be posted if they:

Contain inappropriate language which is not germane to the pest rating proposal;

Contains defamatory, false, inaccurate, abusive, obscene, pornographic, sexually oriented, threatening, racially offensive, discriminatory or illegal material;

Violates agency regulations prohibiting sexual harassment or other forms of discrimination;

Violates agency regulations prohibiting workplace violence, including threats.

♦  Comments may be edited prior to posting to ensure they are entirely germane.

♦  Posted comments shall be those which have been approved in content and posted to the website to be viewed, not just submitted.


Pest Rating: B


Posted by ls

Insects, Mites & Earthworms

Insects and mites are related in that their skeletons are on the outside (Phyllum: Arthropoda), but differ in that adult insects have six legs and adult mites have eight.  Both groups can be beneficial, neutral or destructive to their environment.  Like nematodes, they can cause yearly losses in the billions of dollars for agricultural crops around the world.

PEST RATING PROPOSALS:

ACARI:

Eutetranychus orientalis (Klein): Citrus brown mite
Current Pest Rating: Q
Proposed Pest Rating: A
Comment Period: 04/04/2025 through 05/19/2025 

ISOPTERA:

Cryptotermes brevis (Walker): West Indian drywood termite
Current Pest Rating: Q
Proposed Pest Rating: A
Comment Period: 04/07/2025 through 05/22/2025 

PEST RATINGS:

ACARI

Acalitus phloeocoptes (Nalepa): Plum bud gall mite
Pest Rating: B

Aceria nerii Channabasavana: an oleander mite
Pest Rating: C

Germander crinkle mite | Aculus teucrii (Nalepa)
Pest Rating: C

Ice plant mite | Aceria mesembryanae Smith-Meyer
Pest Rating: Q

Hoary cress gall mite Aceria drabae (Nal.)
Pest Rating: D

Notallus nerii Keifer: an oleander mite
Pest Rating: C

Peacock Mite | Tuckerella sp.
Pest Rating: A

Tropilaelaps clareae Delfinado and Baker: Asian bee mite
Pest Rating: A

Tropilaelaps mercedesae Anderson and Morgan: Asian bee mite
Pest Rating: A

 BLATTODEA

Three-lined Cockroach | Luridiblatta trivittata
Pest Rating: C

COLEOPTERA

Agrilus auroguttatus Schaeffer: Goldspotted oak borer
Pest Rating: B

Agrilus planipennis Fairmaire: Emerald ash borer
Pest Rating: A

Ambrosia Beetle | Euwallacea similis (Ferrari)
Pest Rating: A

Ambrosia Beetle |  Xylosandrus amputatus (Blandford)
Pest Rating: A

Anthonomus rubi (Herbst): strawberry blossom weevil
Pest Rating: A

Anomala orientalis (Waterhouse): Oriental beetle
Pest Rating: A

Banded Elm Bark Beetle | Scolytus schevyrewi Semenov
Pest Rating: C

A Bark Beetle | Pycnarthrum hispidum (Ferrari)
Pest Rating: C

Bark Beetle | Coccotrypes rutschuruensis Eggers
Pest Rating: A

Beetle | Anomala ausonia Erichson
Pest Rating: A

Beetle: Dactylotrypes longicollis (Wollaston)
Pest Rating: C

Beetle | Dyscinetus dubius (Olivier)
Pest Rating: A

Beetle | Semanotus sinoauster Gressitt
Pest Rating: A

Black Pine Bark Beetle | Hylastes ater (Paykull)
Pest Rating: A

Black Timber Bark Beetle | Xylosandrus germanus (Blandford)
Pest Rating: A

Black Twig Borer | Xylosandrus compactus (Eichhoff)
Pest Rating: A

Bruchus pisorum (L.), pea seed beetle
Pest Rating: C

Callidiellum rufipenne (Motschulsky): cedar longhorn beetle
Pest Rating: A

Camphor Shot Borer | Cnestus mutilatus (Blandford)
Pest Rating: A

Carpophilus truncatus Murray: a sap beetle
Pest Rating: B

Ceratapion basicorne (Illiger): a weevil
Pest Rating: D

Cereal Leaf Beetle: Oulema melanopus (Linnaeus)
Pest Rating:  B

Chrysolina bankii (Fabricius): a leaf beetle
Pest Rating: C                    

Click Beetle | Conoderus posticus (Eschscholtz)
Pest Rating: A  

Coffee Bean Weevil | Araecerus fasciculatus
Pest Rating: B

Cyclorhipidion distinguendum (Eggers): an ambrosia beetle
Pest Rating: C

Diaprepes Root Weevil | Diaprepes abbreviatus
Pest Rating: B

Dwarf Siberian Pine Beetle | Dryocoetes pini
Pest Rating: A

Euwallacea interjectus (Blandford): Greater shothole borer
Pest Rating: B

Garden Chafer | Phyllopertha horticola (L.)
Pest Rating: A

Granulate Ambrosia Beetle | Xylosandrus crassiusculus Motschulsky
Pest Rating: A

Hylesinus cingulatus Blandford
Pest Rating: A

Hypothenemus eruditus Westwood
Pest Rating: B

Icosium tomentosum Ganglebauer: a longhorn beetle
Pest Rating: B

Japanese Pine Sawyer | Monochamus alternatus (Hope)
Pest Rating: A

Jewel Beetle | Actenodes auronotatus (Gory & Laporte)
Pest Rating: A

Lilioceris lilii (Scopoli): lily leaf beetle
Pest Rating: A

Longhorned Beetle | Acalolepta aesthetica (Olliff)
Pest Rating: A

Longhorned Beetle | Arhopalus pinetorum (Wollaston)
Pest Rating: A

Longhorned Beetle | Plagionotus arcuatus (Linnaeus)
Pest Rating: A

Mediterranean pine engraver | Orthotomicus erosus (Wollaston)
Pest Rating: C

New Guinea Sugarcane Weevil | Rhabdoscelus obscurus (Boisduval)
Pest Rating: A

Olive Bark Beetle | Phloeotribus scarabaeoides (Bernard)
Pest Rating: B

Palmetto weevil | Rhynchophorus cruentatus (Fabricius)
Pest Rating: A

Paropsis atomaria Olivier: leaf beetle
Pest Rating: B                    

Polyphagous Shot Hole Borer: Euwallacea sp. nr. fornicatus
Pest Rating:  B

Protaetia fusca (Herbst): a flower chafer
Pest Rating: A                    

Red-Black False Blister Beetle: Ananca bicolor (Fairmaire)
Pest Rating:  B

Redneck Longhorn Beetle | Aromia bungii
Pest Rating: A

Rice Beetle | Dyscinetus morator (Fabricius)
Pest Rating: A

Sap Beetle:  Brachypeplus basalis (Erichson)
Pest Rating:  B

Scarab Beetle | Gymnetis stellata (Latreille)
Pest Rating: A

Scolytid Weevil: Pagiocerus frontalis (Fabricius)
Pest Rating:  B

Seed Beetle | Bruchidius terrenus
Pest Rating:  B

Slender-banded Pine Cone Longhorn Beetle | Chlorophorus strobilicola Champion
Pest Rating: A

Small Hive Beetle (SHB): Aethina tumida Murray
Pest Rating: B

Small Spruce Bark Beetle | Polygraphus poligraphus (L.)
Pest Rating: A

South American Palm Weevil | Rhynchophorus palmarum (Linnaeus)
Pest Rating: B

Sri Lankan weevil | Myllocerus undecimpustulatus undatus
Pest Rating:  A

Strangulate Weevil | Trochorhopalus strangulatus (Gyllenhal)
Pest Rating: A

Sugarcane Beetle | Euetheola humilis rugiceps (LeConte)
Pest Rating: A

Sybra alternans Wiedemann: longhorn beetle
Pest Rating: A

Taiwan Slender Longhorned Beetle: Stenhomalus taiwanus Matsushita
Pest Rating: A

Trichoferus campestris (Faldermann): velvet longhorn beetle
Pest Rating: B

Trypodendron signatum (Fabricius)
Pest Rating: A

Twobanded Japanese Weevil | Pseudocneorhinus bifasciatus (Roelofs)
Pest Rating: A

Weevil | Dryophthorus homoeorhynchus Perkins
Pest Rating: C

Weevil | Oxydema longula (Boheman)
Pest Rating: C

West Indian Sugarcane Weevil | Metamasius hemipterus (L.)
Pest Rating:  C 

Xyleborus monographus (Fabricius): Mediterranean oak borer
Pest Rating:  B

Xyleborus pfeilii (Ratzeburg): an ambrosia beetle
Pest Rating: C                              

DIPTERA

Allium Leafminer: Phytomyza gymnostoma Loew
Pest Rating: A

Apple Leaf Gall Midge: Dasineura mali (Kieffer)
Pest Rating:  A

Daylily Leafminer: Ophiomyia kwansonis Sasakawa
Pest Rating:  B

European Pine Resin Midge | Cecidomyia pini (DeGeer)
Pest Rating: A

Ginger Maggot: Eumerus figurans (Walker)
Pest Rating:  B

Lamprolonchaea smaragdi Walker: a fly
Pest Rating: C                    

An Ornamental Fig Pest: Horidiplosis ficifolii Harris
Pest Rating:  B 

Resseliella citrifrugis Jiang: Citrus fruit midge
Pest Rating: A

Resseliella maxima Gagné: soybean gall midge
Pest Rating: A 

Silba adipata McAlpine: black fig fly
Pest Rating: B

Striped Vinegar Fly: Zaprionus indianus Gupta
Pest Rating: B

Tomato leaf miner | Liriomyza bryoniae (Kaltenbach)
Pest Rating: A

Zaprionus tuberculatus Malloch: Vinegar fly
Pest Rating: B

HEMIPTERA

Agave Mealybugs: Paracoccus gillianae and Pseudococcus inconstans (formerly variabilis and sp. A)
Pest Rating: C

Agave Scale:  Acutaspis agavis (Townsend & Cockerell)
Pest Rating: B

Alazon Mealybug | Dysmicoccus grassii (Leonardi)
Pest Rating:  A

Aleuroclava aucubae (Kuwana): a whitefly
Pest Rating: C

Aleurotulus anthuricola Nakahara: anthurium whitefly
Pest Rating: C 

Annona/Gray Pineapple Mealybug | Dysmicoccus neobrevipes
 Pest Rating: A   

Aphalara itadori (Shinji): a psyllid
 Pest Rating: D

Aphis punicae Passerini: pomegranate aphid
Pest Rating: A

Armored Scale | Melanaspis leivasi (Costa Lima)
Pest Rating: A  

Aspidiotus excisus Green: Aglaonema scale
Pest Rating: A 

Aspidiella hartii (Cockerell): a scale
Pest Rating: A

Aspidiella sacchari (Cockerell): sugarcane scale
Pest Rating: A

Aulacaspis yasumatsui Takagi: Cycad Aulacaspis scale
Pest Rating: B

Acizzia conspicua (Tuthill): a psyllid
Pest Rating: C

Balsam Woolly Adelgid |  Adelges piceae
Pest Rating: B

Bamboo pit scale | Bambusaspis miliaris (Boisduval)
Pest Rating: B

Banana Mealybug:  Pseudococcus elisae Borchsenius
Pest Rating:  A

Barber Giant Mealybug | Puto barberi (Cockerell)
Pest Rating: A

Bondar’s Nesting Whitefly: Paraleyrodes bondari Peracchi
Pest Rating:  A

Boxwood Scale: Pinnaspis buxi (Bouché)
Pest Rating: A

Bougainvillea Mealybug: Phenacoccus peruvianus Granara de Willink
Pest Rating: B

Brachynotocoris puncticornis Reuter: a bug
Pest Rating: C

Bronze Bug: Thaumastocoris peregrinus Carpintero and Dellapé
Pest Rating: B

A Burrowing Bug | Rhytidoporus indentatus Uhler
Pest Rating: C

Centrocoris volxemi (Puton): leaf-footed bug
Pest Rating: A                    

Citrus Snow Scale:  Unaspis citri Comstock
Pest Rating:  A

Coccus viridis (Green): green scale
Pest Rating: B                    

Cotton Seed Bug |  Oxycarenus hyalinipennis (Costa)
Pest Rating: A

Crapemyrtle Scale: Acanthococcus lagerstroemiae
Pest Rating: A

Crenidorsum aroidephagus Martin & Aguiar: Aroid whitefly
Pest Rating: C                    

Curtain Fig Psyllid: Macrohomotoma gladiata
Pest Rating: B

Cycad Poliaspis Scale | Poliaspis media Maskell
Pest Rating: B

Dialeurodes kirkaldyi (Kotinsky): Arabian jasmine whitefly
Pest Rating: A

Dialeurodes schefflerae Hodges & Dooley: schefflera whitefly
Pest Rating: C                 

Duges wax scale | Ceroplastes dugesii Lichtenstein
Pest Rating: A

Dysmicoccus mackenziei Beardsley: McKenzie mealybug
Pest Rating: A                   

Elongate Hemlock Scale: Fiorinia externa Ferris
Pest Rating: A

False Trochanter Mealybug | Pseudococcus dolichomelos Gimpel and Miller
Pest Rating: A

Ficus Leaf-rolling Psyllid: Trioza brevigenae Mathur
Pest Rating: B

Fig Wax Scale | Ceroplastes rusci (L.)
Pest Rating:  A

Fiorinia japonica Kuwana: coniferous fiorinia scale
Pest Rating: B                  

Floridana Scale: Lindingaspis floridana Ferris
Pest Rating:  B

Florida Wax Scale | Ceroplastes floridensis Comstock
Pest Rating: A

Fly Speck Scale:  Gymnaspis aechmeae Newstead
Pest Rating:  B

Fromundus pygmaeus (Dallas): Oceanic burrower bug
Pest Rating: A                    

Garden Fleahopper: Halticus bractatus
Pest Rating: A

Geococcus coffeae Green: coffee root mealybug
Pest Rating: A                  

Gray Scale | Pseudoparlatoria ostreata Cockerell
Pest Rating: A

Graphocephala versuta (Say): versute sharpshooter
Pest Rating: B

Gray Sugarcane Mealybug | Trionymus boninsis (Kuwana)
Pest Rating: A

Harrisia Cactus Mealybug | Hypogeococcus pungens Granara de Willink
Pest Rating: A

Hemiberlesia diffinis (Newstead): a hard scale
Pest Rating: A

Hemlock Scale: Hemiberlesia ithacae (Ferris)
Synonym: Abgrallaspis ithacae
Pest Rating: B  

Herculeana Scale: Clavaspis herculeana
Pest Rating: A

Hoplocallis picta (Ferrari): an aphid
Pest Rating: B                    

Jack Beardsley mealybug: Pseudococcus jackbeardsleyi
Pest Rating: A  

A Leafhopper | Paraulacizes irrorata (Fabricius)
Pest Rating: A

Laminicoccus pandani (Cockerell): a mealybug
Pest Rating: A                    

Lepidosaphes chinensis Chamberlin: Chinese mussel scale
Pest Rating: A

Lepidosaphes laterochitinosa Green: an armored scale
Pest Rating: A

Lepidosaphes tokionis (Kuwana): croton mussel scale
Pest Rating: A                 

Lesser Snow Scale: Pinnaspis strachani (Cooley)
Pest Rating: A

Longan Scale: Thysanofiorinia nephelii (Maskell)
Pest Rating:  B

Longistigma liquidambarus (Takahashi): giant sweetgum aphid
Pest Rating: B

Lychee scale | Thysanofiorinia leei Williams
Pest Rating: A

Magnolia White Scale: Pseudaulacaspis cockerelli (Cooley)
Pest Rating: A

Mango Scale | Aulacaspis tubercularis Newstead
Pest Rating: A

Mango Scale: Radionaspis indica
Pest Rating: B

Mango Shield Scale: Milviscutulus mangiferae (Green)
Pest Rating: A

Masked Scale: Mycetaspis personata (Comstock)
Pest Rating: A

A Mealybug: Dysmicoccus texensis (Tinsley)
Pest Rating: A

Mealybug | Ferrisia dasylirii (Cockerell)
Pest Rating: C

A Mealybug | Nipaecoccus floridensis Beardsley
Pest Rating: A

Mealybug | Palmicultor browni (Williams)
Pest Rating: A

A Mealybug | Trionymus sasae (Kanda)
Pest Rating: A

Mealybug | Vryburgia succulentarum Williams
Pest Rating: A

Melanaspis corticosa (Brain): South African obscure scale
Pest Rating: A

Mining Scale: Howardia biclavis
Pest Rating: A

Miscanthicoccus miscanthi (Takahashi) – Miscanthus mealybug
Pest Rating: B

Nipaecoccus floridensis Beardsley: a mealybug
Pest Rating: B

Nipaecoccus viridis (Newstead): Lebbeck mealybug
Pest Rating: A

Odermatt Mealybug | Pseudococcidae mealybug
Pest Rating: A

Oncometopia orbona (Fabricius): broad-headed sharpshooter
Pest Rating: A                    

Oriental Scale: Aonidiella orientalis
Pest Rating: A

Pacific Mealybug: Planococcus minor (Maskell) 
Pest Rating: A 

Palm Mealybug | Palmicultor palmarum (Ehrhorn)
Pest Rating: A  

Papaya Mealybug | Paracoccus marginatus Williams and Granara de Willink
Pest Rating: A

Pellaea stictica (Dallas): stinkbug
Pest Rating: C

Phalacrococcus howertoni Hodges & Hodgson: Croton Scale
Pest Rating: A

Phorodon cannabis Passerini: cannabis aphid
Pest Rating: C

Pink Hibiscus Mealybug | Maconellicoccus hirsutus (Green)
Pest Rating:  A

Plant Bug | Rubrocuneocoris calvertae Henry
Pest Rating: A

A Planthopper:  Kallitaxila granulata (Stål)
Pest Rating:  A

Protea Mealybug:  Delottococcus confusus (De Lotto)
Pest Rating:  C  

Protea Mealybug: Paracoccus hakeae (Williams)
Synonym: Phenacoccus hakeae
Pest Rating:  C 

Pseudaonidia duplex (Cockerell): camphor scale
Pest Rating:  A

Pseudischnaspis bowreyi (Cockerell): Bowrey scale
Pest Rating: A                  

Pseudococcus landoi (Balachowsky): Lando mealybug
Pest Rating: A

Pseudococcus lycopodii Beardsley: a mealybug
Pest Rating: C

Pulvinaria psidii Maskell: Green shield scale
Pest Rating: C

Pyrrhocoris apterus (L.): European firebug
Pest Rating: C

Red Streaked Leafhopper: Balclutha rubrostriata (Melichar)
Pest Rating: A

Red Wax Scale | Ceroplastes rubens Maskell
Pest Rating:  A

Remaudiereana nigriceps (Dallas): a bug
Pest Rating: A                    

Rhizoecus americanus (Hambleton): root mealybug
Pest Rating: A

Rhizoecus floridanus Hambleton: a root mealybug
Pest Rating: A

Root Mealybug: Ripersiella hibisci (Kawai & Takagi)
Pest Rating: A

Rufous Scale | Selenaspidus articulatus (Morgan)
Pest Rating: A

Seed Bugs | Nysius spp.
Pest Rating: NR

A Seed Bug | Ochrimnus mimulus (Stål)
Pest Rating: A

Singhiella simplex (Sing): Ficus whitefly
Pest Rating: C                    

Soft scale | Coccus capparidis (Green)
Pest Rating: A                        

Soft scale | Coccus moestus De Lotto
 Pest Rating: A                        

Soft Scale | Kilifia americana Ben-Dov
Pest Rating: A

Spanish Moss Orthezia: Graminorthezia tillandsiae (Morrison)
Pest Rating: C

Spiraling Whitefly: Aleurodicus dispersus Russell
Pest Rating: A

Spotted Lanternfly:  Lycorma delicatula White
Pest Rating:  A

Stellate Scale: Ceroplastes stellifer
Synonym: Vinsonia stellifera
Pest Rating: A

Stink Bug | Kalkadoona pallida (Van Duzee)
Pest Rating: A

Striped mealybug | Ferrisia virgata (Cockerell)
Pest Rating: A

Taro Planthopper: Tarophagus colocasiae
Pest Rating: B

Tea Scale of Camellia | Fiorinia phantasma Cockerell & Robinson
Pest Rating: A

Thysanococcus pandani Stickney: Pandanus Halimococcia
Pest Rating: A

Toumeyella liriodendri (Gmelin): tuliptree scale
Pest Rating: C

Trilobe Scale: Pseudaonida trilobitiformis (Green)
Hemiptera: Diaspididae
Pest Rating: A

Tropical Palm Scale | Hemiberlesia palmae (Cockerell)
Pest Rating: A

Toumeyella parvicornis (Cockerell): pine tortoise scale
Pest Rating: B                                      

Two-lined Spittlebug | Prosapia bicincta (Say)
Pest Rating: A

Unaspis yanonensis (Kuwana): arrowhead scale
Pest Rating: A

Unilobed Scale:  Pinnaspis uniloba (Kuwana)
Pest Rating:  B

Waratah Scale: Pseudaulacaspis brimblecombei Williams
Pest Rating:  A

Whitefly | Aleurotrachelus anonae Corbett
Pest Rating: A

White Fly: Asiothrixus antidesmae (Takahashi)
Pest Rating: A

White Peach Scale: Pseudaulacaspis pentagona (Targioni)
Pest Rating: A

White Prunicola Scale | Pseudaulacaspis prunicola (Maskell)
Pest Rating: A

HYMENOPTERA 

Anagyrus callidus Triapitsyn, Andreason & Perring Hymenoptera: Encyrtidae
Pest Rating:  D

An Ant:  Ochetellus glaber (Mayr)
Pest Rating:  A

An Ant | Pheidole dentigula
Pest Rating: A

Anoplolepis gracilipes (Fr. Smith): Long-legged ant
Pest Rating: A

Asian Needle Ant | Brachyponera chinensis
Pest Rating: A

Bigheaded Ant: Pheidole megacephala
Pest Rating:  A

Compact Carpenter Ant | Camponotus planatus
Pest Rating: A

Difficult White-Footed Ant  |  Technomyrmex difficilis Forel
Pest Rating: A

Erythrina gall wasp: Quadrastichus erythrinae
Pest Rating: B

Eucalyptus Gall Wasp: Ophelimus maskelli (Ashmead)
Pest Rating: C

Florida Carpenter Ant | Camponotus floridanus (Buckley)
Pest Rating: A  

Flower Ant | Monomorium floricola
Pest Rating: A

Ganaspis brasiliensis (Ihering) (G 1 lineage): parasitoid wasp
Pest Rating: D

Little Fire Ant: Wasmannia auropunctata (Roger)
Pest Rating: A

Long-legged Ant: Anoplolepsis longipes
Pest Rating: A

Modoc Carpenter Ant: Camponotus modoc Wheeler
Pest Rating: C

Native Ant: Formica francoeuri Bolton
Pest Rating: C

Parasitoid wasp | Jaliscoa hunteri (Crawford)
Pest Rating: D

Pheidole megacephala (Fabricius): Big-headed ant
Pest Rating: B

Psyllaephagus euphyllurae (Masi): a parasitoid wasp 
Pest Rating: D

Solenopsis geminata (Fabricius): Tropical fire ant
Pest Rating: A

Spathius galinae Belokobylskij and Strazanac: a parasitoid wasp
Pest Rating: D

Stingless Bee: Plebeia frontalis (Friese)
Pest Rating: B

Tawny Crazy Ant | Nylanderia fulva
Pest Rating: A

Tetrastichus planipennisi Yang: a parasitoid wasp
Pest Rating: D

Trissolcus japonicus (Ashmead): Samurai wasp
Pest Rating: D

Vespa mandarinia Smith: Northern giant hornet
Pest Rating: A

Vespa velutina Lepeletier: yellow-legged hornet
Pest Rating: A

⇒ LEPIDOPTERA

Agonopterix alstroemeriana (Clerck): a moth
Pest Rating: D

Arcola malloi (Pastrana): Alligatorweed stem borer moth
Pest Rating: D

Azalea Leafminer | Caloptilia azaleella (Brants)
Pest Rating: C

Banana Moth |  Opogona sacchari (Bojer)
Pest Rating: C

Barred Fruit-tree Tortrix | Pandemis cerasana Hübner
Pest Rating:  A

Carnation tortrix  |  Cacoecimorpha pronubana (Hübner)
Pest Rating: A  

Cherry Bark Tortrix | Enarmonia formosana (Scopoli)
Pest Rating:  A

Choreutis cf. emplecta (Turner): a moth
Pest Rating:  C

Cotton Bollworm | Helicoverpa armigera (Hübner)
Pest Rating: A

Cucumber Moth | Diaphania indica (Saunders)
Pest Rating: A

Cydalima perspectalis (Walker): box tree moth
Pest Rating: A

Dichomeris acuminatus (Staudinger): alfalfa leaftier
Pest Rating: B                   

Eastern Tent Caterpillar |  Malacosoma americanum (Fabricius)
Pest Rating: A

Epiphyas postvittana (Walker): light brown apple moth (LBAM)
Pest Rating: C

Erythrina Twigborer: Terastia meticulosalis Guenée
Pest Rating:  B

Golden twin-spot moth: Chrysodeixis chalcites (Esper)
Pest Rating: A

Green Garden Looper | Chrysodeixis eriosoma (Doubleday)
Pest Rating:  A

Grey Tortrix | Cnephasia stephensiana Doubleday
Pest Rating: A

Harrisina metallica Stretch: western grapeleaf skeletonizer
Synonym: Harrisina brillians Barnes and McDunnough
Pest Rating: C                    

Leek Moth | Acrolepiopsis assectella (Zeller)
Pest Rating: A                        

Southern Armyworm: Spodoptera eridania (Stoll)
Pest Rating: A

Tomato Leafminer: Tuta absoluta (Meyrick)
Pest Rating: A  

Winter Moth | Operophtera brumata (L.)
Pest Rating:  A

OLIGOCHAETA:

Amynthas agrestis (Goto & Hatai): Jumping worm
Pest Rating: B

Metaphire hilgendorfi (Michaelsen): Jumping worm
Pest Rating: B

Perionyx excavatus (Perrier): blue worm
Pest Rating: C 

ORTHOPTERA:

Gryllus locorojo Weissman & Gray, 2012 (Crazy Red Field Cricket)
Pest Rating:  D

PHASMATODEA

Carausius morosus (Sinéty): Indian walking stick 
Pest Rating: C                        

THYSANOPTERA 

Arorathrips mexicanus (Crawford): a thrips
Synonym: Chirothrips mexicanus Crawford

Pest Rating:  C

Androthrips ramachandrai Karny: a thrips
Pest Rating:  C

Bamboo Orchid Thrips: Dichromothrips smithi (Zimmerman)
Pest Rating:  A

Banana-silvering Thrips: Hercinothrips bicinctus (Bagnall)
Pest Rating: B

Biltothrips minutus (Bhatti)
Pest Rating: A

Black Vine Thrips: Retithrips syriacus (Mayet)
Pest Rating: A

Chilli Thrips:  Scirtothrips dorsalis Hood
Pest Rating: B

Frankliniella schultzei (Trybom): common blossom thrips
Pest Rating: B

Frankliniella tritici (Fitch): eastern flower thrips(Trybom): common blossom thrips
Pest Rating: B                    

Gorse Thrips | Sericothrips staphylinus Haliday
Pest Rating: D

Japanese Flower Thrips | Thrips setosus
Pest Rating:  A 

Kelly’s Citrus Thrips: Pezothrips kellyanus (Bagnall)
Pest Rating: A

Klambothrips myopori Mound & Morris: thrips
Pest Rating: C                    

Lord Howe Island Thrips | Dendrothrips howei Mound
Pest Rating: B 

Melon Thrips: Thrips palmi (Karny)
Pest Rating:  A

Rose Thrips | Thrips fuscipennis
Pest Rating:  A

A Thrips | Coremothrips pallidus Hood
Pest Rating: A

Thrips | Indusiothrips seshadrii Priesner
Pest Rating: A

Thrips maculicollis (Hood): a thrips 
Pest Rating: A                    

Thrips orientalis (Bagnall): a thrips
Pest Rating: A                    

Thrips | Trichromothrips priesneri (Bhatti)
Pest Rating: A

Weeping Ficus Thrips: Gynaikothrips uzeli (Zimmermann)
Pest Rating:  B

Nematodes

(Plant Parasitic Nematodes)

Nematodes (also called ‘roundworms’) are relatively small, multicellular, worm-like animals. They are found in almost every environmental niche imaginable, living free in soil, marine and freshwater habitats while feeding on bacteria, fungi, and nematodes, or as parasites of humans, insects, fish, larger animals and plants.

Plant parasitic nematodes are abundant in many soils and may be feed on roots and other below ground plant tissue as external feeders while living outside a plant or penetrate and enter plant tissue to live and feed internally causing damage to plants. While most species of plant parasitic nematodes feed on below ground plant tissue, a relatively fewer number may inhabit and feed on above ground tissue. Billions of dollars in losses to agricultural crops due to damages caused by plant parasitic nematodes occur worldwide every year. California’s agricultural industry could lose several hundred million dollars annually in crop losses if certain plant parasitic nematodes not known to occur or of limited occurrence in California would become widespread within the State.

PEST RATING PROPOSALS:

NEMATODES:

PEST RATINGS:

Nematodes:

Anguina agrostis (Steinbuch, 1799) Filipjev, 1936 Bent grass seed gall nematode
Pest Rating: B

Anguina funesta
Pest Rating: A

Anguina pacificae Cid del Prado Vera & Maggenti 1984 Pacific shoot-gall nematode
Pest Rating: C

Anguina tritici | Wheat Seed gall nematode
Pest Rating: A 

Aphelenchoides besseyi Christie, 1942 (Allen, 1952) Strawberry summer crimp nematode
Pest Rating: A

Aphelenchoides fragariae (Ritzema – Bos, 1891) Christie, 1932 Strawberry crimp nematode, Strawberry spring dwarf nematode, Foliar nematode
Pest Rating: C

Aphelenchoides ritzemabosi (Schwartz, 1911) Steiner & Buhrer 1932
Pest Rating: C                                          

Asian Citrus Root-knot Nematodes
Pest Rating:  A

Belonolaimus longicaudatus Rau, 1958 Sting nematode
Pest Rating: A

Bitylenchus maximus (Allen, 1955) Siddiqi, 1986 Stunt nematode
Pest Rating: C

Bursaphelenchus coccophilus 
Pest Rating: A

Bursaphelenchus mucronatus Mamiya and Enda, 1979 pine wood nematode
Pest Rating: A

Bursaphelenchus xylophilus (Steiner & Bruhrer, 1934) Nickle, 1970 Pine wilt disease
Pest Rating: C

Cactodera cacti (Filipjev & Schuurmans Stekhoven, 1941 Krall & Krall, 1978 Cactus cyst nematode)
Pest Rating: A

Criconemoides (syn. Criconemella De Grisse and Loof 1965), Taylor 1936
Pest Rating: C 

Ditylenchus destructor Thourne, 1945
Pest Rating: A

Ditylenchus dipsaci (Kühn, 1857) Filipjev, 1936
Pest Rating: C

Dolichodorus heterocephalus Cobb, 1914 Cobb’s awl nematode
Pest Rating: A

Globodera pallida (Stone 1973) Behrens Pale cyst nematode
Pest Rating: A

Globodera rostochiensis Wollenweber 1923 Golden nematode
Pest Rating: A 

Helicotylenchus spp.
Pest Rating: C

Helicotylenchus multicinctus
Pest Rating:  B

Hemicriconemoides chitwoodi Esser, 1960 Sheathoid nematode
Pest Rating: C 

Hemicriconemoides spp. Chitwood & Birchfield, 1957 Sheathoid nematodes
Pest Rating: C

Hemicycliophora arenaria
Pest Rating: B 

Heterodera australis Subbotin, Sturhan, Rumpenhorst & Moens, 2002 Australian cereal cyst nematode
Pest Rating: A

Heterodera avenae Wollenweber, 1924 European cereal cyst nematode
Pest Rating: A

Heterodera carotae Jones, 1950
Pest Rating: B

Heterodera ciceri Vovlas, Greco & Di Vito, 1985 Chickpea cyst nematode
Pest Rating: A

Heterodera cruciferae Franklin, 1945 Cabbage cyst nematode
Pest Rating: C

Heterodera fici Kirjanova, 1954 Fig cyst nematode
Pest Rating: C

Heterodera filipjevi (Madzhidov, 1981) Stelter, 1984 Filipjev’s cereal cyst nematode
Pest Rating: A

Heterodera glycines Ichinohe, 1952 Soybean cyst nematode
Pest Rating: A

Heterodera latipons Franklin, 1969 Mediterranean cereal cyst nematode
Pest Rating: A

Heterodera mani Mathews, 1971 Rye grass cyst nematode
Pest Rating: B

Heterodera schachtii A. Schmidt, 1871 Sugarbeet cyst nematode            Pest Rating: C

 Heterodera sturhani Subbotin 2015 Sturhan cereal cyst nematode 
 Pest Rating: A

Heterodera trifolii Goffart, 1932 clover cyst nematode
Pest Rating: C

Heterodera ustinovi Kirjanova, 1969 Ustinov’s grass cyst nematode
Pest Rating: A

Hirschmanniella belli Sher 1968
Pest Rating: C

Hirschmanniella diversa Sher 1968
Pest Rating: C

Hirschmanniella oryzae (van Breda de Haan, 1902) Luc & Goodey,1964 rice root nematode
Pest Rating: A

Hoplolaimus galeatus (Cobb, 1913) Filipjev & Schuurmans Stekh Lance nematode
Pest Rating: A

Longidorus africanus Merny, 1966 Needle nematode
Pest Rating: C

Longidorus elongatus: Needle nematode
Pest Rating:  B

Longidorus orientalis Loof, 1982 Needle nematode
Pest Rating: C

Meloidogyne arenaria (Neal) Chitwood, 1949 Peanut root-knot nematode
Pest Rating: C

 Meloidogyne artiellia Franklin (1961) British root-knot nematode
Pest Rating: A 

Meloidogyne chitwoodi Golden, O’Bannon, Santo & Finley, 1980 Columbia root-knot nematode
Pest Rating: B                                          

Meloidogyne enterolobii Yang and Eisenback, 1983.
Pest Rating: A

Meloidogyne fallax Karssen, 1996 False Columbia root-knot nematode
Pest Rating: A

Meloidogyne floridensis Handoo et al., 2004
Pest Rating: A

Meloidogyne graminis (Sledge & Golden) Whitehead 1968 Grass root-knot nematode
Pest Rating: C

Meloidogyne hapla Chitwood, 1949 Northern Root-Knot Nematode
Pest Rating: C 

Meloidogyne haplanaria Eisenback et al. 2003 Texas peanut root-knot nematode
Pest Rating: A

Meloidogyne hispanica Hirschmann 1986 Seville root-knot nematode
Pest Rating: A

Meloidogyne incognita (Kofoid & White, 1919) Chitwood 1949 Southern root-knot nematode
Pest Rating: C

Meloidogyne javanica (Treub, 1885) Chitwood, 1949 Javanese root-knot nematode
Pest Rating: C

Meloidogyne mali Itoh, Oshima & Ichinohe 1969 apple root-knot nematode
Pest Rating: A

Meloidogyne marylandi Jepson and Golden, 1987
Pest Rating: C

Meloidogyne minor Karssen et al. 2004
Pest Rating: A

Meloidogyne naasi Franklin 1965 Barley root knot nematode
Pest Rating: B

Meloidogyne paranaensis Carneiro et al. 1996 Parana coffee root-knot nematode
Pest Rating: A

Merlinius spp. (Allen 1955) Siddiqi, 1970
Pest Rating: C 

Mesocriconema (Macroposthonia) xenoplax (Raski) Loof & de Grisse 1989 ring nematode
Pest Rating: C

Nacobbus aberrans (Thorne, 1935) Thorne & Allen, 1944 (sensu lato) False root-knot nematode
Pest Rating: A

Nanidorus spp. Siddiqi, 1974 Stubby root nematode
Pest Rating: C

Paratrichodorus minor (Colbran, 1956) Siddiqi, 1974
Pest Rating: C   

Paratrichodorus porosus (Allen, 1957) Siddiqi, 1974
Pest Rating: C 

Paratrichodorus spp. (Siddiqi 1974) and Trichodorus spp. (Cobb 1913)
Pest Rating: C

Paratylenchus spp. Micoletzky, 1922
Pest Rating: C

Pratylenchus alleni 
Pest Rating:  A

Pratylenchus brachyurus (Godfrey, 1929) Filipjev & Schuurmans-Stekhoven, 1941 smooth-headed lesion nematode
Pest Rating: C

Pratylenchus coffeae 
Pest Rating: B

Pratylenchus crenatus Loof 1960 Root lesion nematode
Pest Rating: C

Pratylenchus hippeastri (Inserra et al., 2007) Amaryllis lesion nematode
Pest Rating: B

Pratylenchus neglectus
Pest Rating: C

Pratylenchus penetrans (Cobb, 1917) Filipjev & Schuurmans Stekhoven, 1941 Cobb’s lesion nematode
Pest Rating: C

Pratylenchus scribneri Steiner, 1943 Scribner’s root-lesion nematode
Pest Rating: C 

Pratylenchus thornei
Pest Rating: C

Pratylenchus vulnus Allen & Jensen, 1951 walnut root lesion nematode
Pest Rating: C

Pratylenchus zeae Graham, 1951 Corn lesion nematode
Pest Rating: C

Punctodera punctata (Thorne, 1928) Mulvey & Stone, 1976
Pest Rating: C  

Quinisulcius spp. Siddiqi 1971
Pest Rating: C                          

Radopholus similis (Cobb, 1893) Thorne, 1949
Pest Rating: A

Rotylenchulus reniformis
Pest Rating: A

Rotylenchulus parvus (Williams) Sher 1961
Pest Rating: C

Rotylenchus robustus (de Man, 1876) Filipjev, 1936 Spiral nematode
Pest Rating: C

Scutellonema spp. Cobb, 1913
Pest Rating: C   

Tylenchorhynchus spp.
Pest Rating: C 

Tylenchulus semipenetrans (Cobb, 1913) Citrus nematode
Pest Rating: C

Xiphinema americanum Cobb, 1913 American dagger nematode
Pest Rating: C

Xiphinema bakeri Williams, 1961 Baker’s dagger nematode
Pest Rating: C

Xiphinema basiri Siddiqi, 1959 dagger nematode
Pest Rating: A

 Xiphinema brasiliense Lordello, 1951 Dagger nematode
 Pest Rating: A

 Xiphinema californicum Lamberti & Bleve-Zacheo, 1969
California dagger nematode

Pest Rating: C

Xiphinema chambersi Thorne, 1939 Chambers’ dagger nematode
Pest Rating: B

Xiphinema diversicaudatum (Micoletzky, 1927), Thorne, 1939 European dagger nematode
Pest Rating: A

Xiphinema index
Pest Rating: B

Xiphinema pachtaicum (Tulaganov, 1938) Kirjanova, 1951 Dagger nematode
Pest Rating: C   

Xiphinema rivesi Dalmasso 1969 Dagger nematode
Pest Rating: C

Xiphinema setariae Luc 1958 (syn. Xiphinema vulgare Tarjan, 1964) dagger nematode 
Pest Rating: A