Category Archives: Insects, Mites & Earthworms

Entomology: Insects, Mites & Earthworms

Thrips | Trichromothrips priesneri (Bhatti)

California Pest Rating  for
Thrips | Trichromothrips priesneri (Bhatti)
Thysanoptera: Thripidae
Pest Rating: A

 


PEST RATING PROFILE

Initiating Event:   

Trichromothrips priesneri was tentatively reported to be established on the island of Maui, Hawaii (Mound et al., 2017).  It is currently Q-rated, and a permanent pest rating proposal is required to support an official pest rating.

History & Status:

Background:  Adult T. priesneri are bicolored, with a dark brown abdomen and wings and white (with brown markings) thorax and head (Mound et al., 2017).  The size is probably similar to that of other Trichromothrips species: 1-1.5 mm (Nakahara, 1993).  Very little information is available on this species.  In Taiwan, T. priesneri has been collected from unidentified grass and Ipomoea nil (Wang, 2008).  In Hawaii, it was found in a coastal, wetland area with dodder and Cyperaceae (Mound et al., 2017).  It is not known if these plants are fed upon by the thrips.  Other species of Trichromothrips have been reported to feed on ferns, bamboo, orchids, and other plants (Goldarazena et al., 2012; Mound and Masumoto, 2004; Ng and Mound, 2015), although again, it is possible that some of these records do not represent feeding but rather plants that the thrips happened to be resting on.  One species of Trichromothrips was reported to be a pest on orchids and various greenhouse plants, but no further information was found to support this (Mound et al., 2016).

Worldwide Distribution:  Trichromothrips priesneri is found in, and is presumably native to India (Karnataka, Madhya Pradesh, Tamil Nadu, and Uttar Pradesh states) (Rachana and Varatharaja, 2017; Tyagi and Kumar, 2016).  It is also reported from Taiwan and Hawaii; these reports are presumed to represent introductions, although the identification of the Hawaii specimens appears to have been tentative (Mound et al., 2017; Wang, 2008).

Official Control: Trichromothrips priesneri is not known to be under official control anywhere.

California Distribution:  Trichromothrips priesneri is not known to be present in California (Symbiota Collections of Arthropods Network).

California Interceptions:  Trichromothrips priesneri has not been intercepted in California (CDFA Pest and Damage Report Database, 2017).

The risk Trichromothrips priesneri would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: The areas that priesneri occurs in have a tropical or subtropical climate, suggesting that this species requires such climates. This is expected to limit the potential distribution of this species in California to a limited area.  Not enough is known about the feeding habits of T. priesneri to consider the presence of host plants in the potential distribution of this species in California.  Therefore, T. priesneri receives a Medium (2) 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: Although the collection of specimens in Taiwan from grass and Ipomoea nil suggests that these may be host plants, too little is known about the biology of priesneri to assess its host range. To account for uncertainty, the host range will be assumed to be moderate.  Therefore, T. priesneri 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 Reproductive and Dispersal Potential: Trichromothrips priesneri has wings and presumably flies.  Therefore, it 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: Little is known about the biology of priesneri, but it presumably feeds on living plants.  At least one species of Trichromothrips is reported to be a pest.  It is possible that T. priesneri could become a pest if it became established in California.  If this happened, lower crop yields and increased crop production costs could result.  Therefore, it receives a Medium (2) in this category.

Economic Impact:  A, 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.

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: If priesneri became established in California and it became a pest, this could result in official or private treatment programs. Therefore, it receives a Medium (2) in this category.

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

Environmental Impact:  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: 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 Trichromothrips priesneri: Medium (10)

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: Trichromothrips priesneri is not known to be present 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 (10)

Uncertainty:

There is a great deal of uncertainty in this proposal.  The biology of T. priesneri is poorly known.  It is not known for certain what plants it feeds on.  The potential of this thrips to cause damage to the plants it feeds on is also not known.  Finally, it is not known how large of an area in California this species could become established in.  It appears to require a tropical or subtropical climate, and this could prevent its establishment in California or limit establishment to a very small area.

Conclusion and Rating Justification:

Trichromothrips priesneri is a thrips that apparently feeds on living plants.  It is not known to occur in California, and it may pose an economic and environmental threat to the state.  For these reasons, a “A” rating is justified.


References:

Goldarazena, A., Gattesco, F., Atencio, R., and Korytowski, C.  2012.  An updated checklist of the Thysanoptera of Panama with comments on host associations.  Check List 8:1232-1247.

Mound, L. and Masumoto, M.  2004.  Trichromothrips veversae sp. n. (Insecta, Thysanoptera), and the Botanical Significance of Insects Host-specific to Austral Bracken Fern (Pteridium esculentum).  Proceedings of the Linnaean Society of New South Wales 125:67-71.

Mound, L. A., Matsunaga, J. N., Bushe, B., Hoddle, M. S., and Wells, A.  2017.  Adventive Thysanoptera species in the Hawaiian Islands: New records and putative host associations.  Proceedings of the Hawaiian Entomological Society 49:17-28.

Mound, L., Nakahara, S., and Tsuda, D. M.  2016.  Thysanoptera-Terebrantia of the Hawaiian Islands: an identification manual.  ZooKeys 549:71-126.

Nakahara, S.  1993.  The genus Dorcadothrips (Thysanoptera: Thripidae) in Hawaii and North America with a description of a new species.  Journal of the New York Entomological Society 101:399-409.

Ng, Y. F., and Mound, L. A.  2015.  Species of Thripinae (Thysanoptera) from bamboo in Malaysia, with one new species and six new records.  Zootaxa 3918:492-502.

Rachana, R. and Varatharaja, R.  2017.  Checklist of terebrantian thrips (Insecta: Thysanoptera) recorded from India.  Journal of Threatened Taxa 9:9748-9755.

Symbiota Collections of Arthropods Network.  Accessed March 27, 2017: http://scan1.acis.ufl.edu

Tyagi, K. and Kumar, V.  2016.  Thrips (Insecta: Thysanoptera) of India – An updated checklist.  Halteres 7:64-98.

Wang, C -L.  2008.  A new synonym and two new records for Taiwan of Thripidae related to Trichromatothrips (Thysanoptera).  Zootaxa 1941:67-68.


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

6/26/18 – 8/10/18


*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.

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 

Scarab Beetle | Gymnetis stellata (Latreille)

California Pest Rating  for
Scarab Beetle | Gymnetis stellata (Latreille)
Coleoptera: Scarabaeidae: Cetoniinae
Pest Rating: A

 


PEST RATING PROFILE

Initiating Event:

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

History & Status:

Background:  Gymnetis stellata is a beetle that measures approximately 20 mm in length and 13 mm in width.  It is dark and velvety with a distinctive pattern of red-orange stripes that radiate from the center of its body.  It occurs in tropical forests at low elevations (below 1600 meters above sea level).  Adults are reported to feed on fruit, including banana, lemon, and guava (Juárez and González, 2015; Maes and Orozco, 2017; Oliveros-Guzmán, 2017).  Adults of other Gymnetis species are reported to feed on fruit, leaves, and flowers; feeding damage is reported to result in the loss of fruit (García, 2005; Montero and Seta, 2015; Segarra et al., 2014).  The larvae of Gymnetis stellata feed on decomposing organic matter.  Numerous larvae, pupal cells, and adults of this species were found in an accumulation of insectivorous bat guano in an unfinished building in Tabasco, Mexico.  It is likely other types of organic matter are used for development more frequently (Sánchez Soto et al., 2017).  The larvae of other species of Gymnetis are reported to feed on decomposing organic matter, including rotting logs (Montero and Seta, 2015; Neita et al., 2006).

Worldwide Distribution:  Gymnetis stellata has been reported from Mexico, Central America (Guatemala, Nicaragua, and Panamá), and South America (Colombia and Peru) (Duque and Cabrera, 2013; Juárez and González, 2015; Maes and Orozco, 2017; Oliveros-Guzmán et al., 2017; Ríos and Gómez, 2011; Sánchez Soto et al., 2017).

Official Control: Gymnetis stellata is not known to be under official control anywhere.

California Distribution:  Gymnetis stellata is not known to be present in California.

California Interceptions:  Gymnetis stellata was found outside of a produce terminal in San Francisco County in 2007 (CDFA Pest and Damage Report Database, 2018).

The risk Gymnetis stellata would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Gymnetis stellata appears to be restricted to warmer climates. It is likely that this beetle would be limited to the southern, coastal portion of California if it became established here.  Gymnetis stellata is presumed to be capable of feeding on a wide variety of fruit (and possibly flowers as well), and the larvae are known to feed on decomposing organic matter.  Presence of adult and larval food is not expected to be a significant limiting factor of the potential distribution of this species in California.  Therefore, Gymnetis stellata receives a Medium (2) 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: Gymnetis stellata apparently feeds on decomposing organic matter as a larva and a variety of fruits as an adult. Based on the known feeding habits of this species and others in the genus, it appears likely that a very wide variety of fruits could be fed upon by the adults.  Therefore, it receives a High (3) 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 Reproductive and Dispersal Potential: Cetoniines are typically strong fliers.  All life stages of stellata appear unlikely to be dispersed artificially, because the larvae live in rotting organic matter and the adults are large and mobile.  Therefore, it 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: Adult Gymnetis stellata are reported to feed on fruit.  Other Gymnetis species have been reported to cause damage to fruit as a result of adult feeding.  For example, adult feeding by two species of Gymnetis has damaged peach, apricot, and tomato fruit in Argentina (Montero and Seta, 2015).  It is possible that stellata could feed on and damage a variety of fruits, especially soft-skinned ones.  Some Gymnetis species feed on other plant parts, including leaves and flowers, as well as fruit.  It is possible that G. stellata may share such broad feeding habits, and if it does, it could damage crops other than fruit.  Damage to crops could lower yield and increase production costs.  Therefore, it receives a Medium (2) in this category.

Economic Impact:  A, 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.

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: Adult Gymnetis stellata feed on fruit, and they may also be capable of feeding on other plant parts, including flowers and leaves. If this beetle became established in California, it could attack native plants, which could disrupt natural communities.  In addition, if it was a pest in agricultural situations, it could trigger treatments.  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, 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.

Score the pest for Environmental Impact. Score:

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 Gymnetis stellata: Medium (12)

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: Gymnetis stellata is not known to be present 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 (12)

Uncertainty:

It is possible that the climate of California may not be conducive to the establishment of G. stellata.  It is also possible that this beetle would not have significant economic or environmental impacts even if it did become established in the state. Although adult feeding is capable of causing damage to, and loss of fruit, there appears to be little mention of Gymnetis species as significant pests in the literature.

Conclusion and Rating Justification:

Gymnetis stellata is a plant-feeding insect that has the potential to damage fruit and possibly other crops, and it could have environmental impacts as well.  It is not known to be present in California.  For these reasons, an “A” rating is justified.


References:

CDFA Pest and Damage Report Database.  2018.  Gymnetis stellata.  Plant Health and Pest Prevention Services. CA Department of Food and Agriculture.  Accessed April 25, 2018: https://pdr.cdfa.ca.gov/PDR/pdrmainmenu.aspx

Duque, M. E. T. and Cabrera, S. G.  2013.  Reporte de los fondos del MEFLG: Melolόntidos del Museo Entomolόgico Francisco Luís Gallego.  Boletin del Museo Entomolόgico Francisco Luís Gallego 5:27-56.

García, C. V.  2005.  Reconocimiento fitosanitario en cinco variedades cultivadas de macadamia (Macadamia integrifolia Maiden et Betche) en la zona cafetera colombiana.  Manejo Integrado de Plagas y Agroecología 74:69-76.

Maes, J- M. and Orozco, J.  2017.  Catalogo ilustrado de los Cetoniinae y Trichiinae (Coleoptera: Scarabaeidae) de Nicaragua.  Revista Nicaraguense de Entomologia 120:1-111.

Montero, G. A. and Seta, S. A.  2015.  Daños producidos por dos especies de Gymnetis (Cetoniinae: Scarabaeidae) en frutos de tomate, damasco y durazno en el sudeste de Santa Fe.  Agromensajes 41:18-22.

Neita, J. C., Orozco A., J., and Ratcliffe, B.  2006.  Escarabajos (Scarabaeidae: Pleurosticti) de la selva baja del bosque pluvial tropical <<BP-T>>, Chocό, Colombia.  Acta Zoológica Mexicana (n.s.) 22:1-32.

< lang="es">Oliveros-Guzmán, E., Ponce-Saavedra, J., and Niño-Maldonado, S.  2017.  Nuevos registros de Gymnetis stellata (Latreille, 1833) (Coleoptera: Scarabaeidae: Cetoniinae) para los estados de Michoacán y Tamaulipas, México.  Folia Entomológica Mexicana (nueva serie) 3:9−11.

Ríos, M. A. M. and Rojas-Gómez, C. V.  2011.  Escarabajos de mayo y mayates (Insecta: Coleoptera: Melolonthidae).  pp. 391-397 in Angón, A.C. (ed.), La Biodiversidad en Veracruz.  Volumen II.  Comisión Nacional para el Conocimiento y Uso de la Biodiversidad, Gobierno del Estado de Veracruz, Universidad Veracruzana, Instituto de Ecología, A.C. México.

Sánchez Soto, S., Jiménez, M. M., Gόmez, W. S. S., Aguilar, J. D. L., and Méndez, A. D. J.  2017.  Sitio de reproducciόn de Gymnetis stellata en Tabasco, México.  Boletín del Museo de Entomología de la Universidad del Valle 17:16-20.

Segarra, A. E., Morales-Pérez, A, Franqui, R. A., and Ratcliffe, B. C.  2014.  First report of a South American cetoniine beetle, Gymnetis strigosa (Olivier, 1789) (Coleoptera: Scarabaeidae: Cetoniinae), in Puerto Rico.  The Coleopterists Bulletin 68:217-218.

Symbiota Collections of Arthropods Network.  Accessed January 12, 2018: http://scan1.acis.ufl.edu


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

6/25/18 – 8/09/18


*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.

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 

Rice Beetle | Dyscinetus morator (Fabricius)

California Pest Rating  for
Rice Beetle | Dyscinetus morator (Fabricius)
Coleoptera: Scarabaeidae
Pest Rating: A

 


PEST RATING PROFILE

Initiating Event:

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

History & Status:

Background:  Adult Dyscinetus morator are beetles that measure ½ to ¾ of an inch in length.  They are black and shining with a slightly greenish sheen (Woodruff, 1999).  Adults feed on plant material aboveground, underground, and even under water.  They have been reported to feed on, burrow into, and cause significant damage (including crop losses up to 30%) to carrots and radishes in Florida (Foster et al., 1986).  Ornamental plants are also affected.  For example, tubers of caladium were attacked by D. morator adults in Florida (Price and Kring, 1991).   Adults were also reported to feed on leaves of a variety of crop species in the laboratory, including lettuce, peas, squash, and tomato. They apparently thrive in aquatic habitats and can spend several hours submerged under water while feeding on aquatic plants, including the aquatic weed Salvinia minima (Jäch and Balke, 2008; Parys et al., 2013).  Dyscinetus morator larvae are C-shaped, whitish grubs that live underground.  They are reported to feed on roots, including those of azalea (Rhododendron spp.) and juniper (Juniperus sp.) (Price and Kring, 1991; Staines, 1990).  The larvae may also feed on accumulations of decomposing organic matter, including compost (Richter, 1958).

Worldwide Distribution:  Dyscinetus morator is reported from the Caribbean (Bahamas, Cuba, and Puerto Rico) and the eastern United States (from Florida north to New York and west to Texas) (Ratcliffe and Cave, 2008; Staines, 1990).  This species is apparently native to the eastern United States, and the Caribbean records may represent introductions (Ratcliffe and Cave, 2008).

Official Control: Dyscinetus morator is not known to be under official control anywhere.

California Distribution:  Dyscinetus morator is not known to occur in California.

California Interceptions:  Dyscinetus morator has been intercepted on a variety of items, including nursery stock, from Arkansas, Florida, Georgia, Mississippi, Tennessee, Texas, Virginia, and possibly other states.  This beetle was found inside a warehouse in Alameda County in 1999 (CDFA Pest and Damage Report Database, 2018).

The risk Dyscinetus morator would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Dyscinetus morator is widely distributed in the eastern United States and the Caribbean, which suggests it has broad climatic tolerances and could establish over a large portion of California. This beetle is reported to feed on a wide variety of plants, including many crops and ornamentals, and would likely find suitable host plants over a large portion of California.  Therefore, Dyscinetus morator 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: Dyscinetus morator has been reported to feed on a wide variety of plants in at least eight families. Therefore, it receives a High (3) 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: Dyscinetus morator flies to light in large numbers (Woodruff, 1999).  Larvae of morator have been found in potted juniper plants, so it is possible that this beetle could be artificially dispersed through movement of potted nursery plants (Price and Kring, 1991).  Therefore, it 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: Dyscinetus morator is known to cause significant damage to crop plants in certain situations.  If this beetle became established in California, it could reduce yield and increase production costs of many different crops.  The presence of this species in nurseries could trigger the loss of markets, as the larvae could occur in soil in potted plants.  Therefore, it receives a High (3) in this category.

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: Dyscinetus morator is reported to attack crop and ornamental plants. If this species became established in California, it could trigger treatment programs in agricultural settings as well as in ornamental settings, including nurseries and gardens.  This species feeds on a wide variety of plants and can tolerate a wide range of conditions.  This beetle could invade natural California ecosystems and attack native plants. 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, 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.

Score the pest for Environmental Impact. Score:

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 Dyscinetus morator: High (14)

Add up the total score and include it here.

–Low = 5-8 points

–Medium = 9-12 points

–High = 13-15 points

Post Entry Distribution and Survey Information: Dyscinetus morator is not known to be present 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:

The final score is the consequences of introduction score minus the post entry distribution and survey information score: High (14)

Uncertainty:

There appears to be little uncertainty regarding the potential for this beetle to become established in California.  Even though this beetle is often very abundant and has been reported to feed on and cause significant damage to a wide variety of crop and ornamental plants in certain situations, its significance as a pest seems to be restricted in time and space.  This could be because this species is native to most of the area that it is known to occur in and is being controlled by natural enemies (predators and parasitoids).  If this species was introduced to California, it may escape the natural enemies present in the eastern United States.

Conclusion and Rating Justification:

Dyscinetus morator is a highly polyphagous plant-feeding beetle that is not known to occur in California.  If it became established in California, it could have severe economic and environmental impacts.  For these reasons, an “A” rating is justified.


References:

CDFA Pest and Damage Report Database. 2018.  Dyscinetus morator. Plant Health and Pest Prevention Services. CA Department of Food and Agriculture. Accessed April 6, 2018: http://phpps.cdfa.ca.gov/user/frmLogon2.asp

Foster, R. E., Smith, J. P., Cherry, R. H., and Hall, D.G.  1986.  Dyscinetus morator (Coleoptera: Scarabaeidae) as a pest of carrots and radishes in Florida 69:431-432.

Jäch, M. A. and Balke, M.  2008.  Global diversity of water beetles (Coleoptera) in freshwater.  Hydrobiologia 595:419-442.

Parys, K. A., Gimmel, M. L., and Johnson, S. J.  2013.  Checklist of insects associated with Salvinia minima Baker in Louisiana, USA.  CheckList 9:1488-1495.

Price, J. F. and Kring, J. B.  1991.  Dyscinetus morator (Coleoptera: Scarabaeidae) flight activity, food plant acceptance, damage and control in caladium.  Florida Entomologist 74:415-421.

Ratcliffe, B. C. and Cave, R. D.  2008.  The Dynastinae (Coleoptera: Scarabaeidae) of the Bahamas with a description of a new species of Cyclocephala from Great Inagua Island.  Papers in Entomology 105:1-10.

Ritcher, P. O.  1958.  Biology of Scarabaeidae.  Annual Review of Entomology 3:311-334.

Staines, C. L.  1990.  Dyscinetus morator (Coleoptera: Scarabaeidae) feeding on roots of azaleas (Rhododendron spp.) 101:98.

Symbiota Collections of Arthropods Network.  Accessed April 6, 2018: http://scan1.acis.ufl.edu

Woodruff, R. E.  1999.  Rice beetle, Dyscinetus morator (Fabricius) (Insecta: Coleoptera: Scarabaeidae).  EENY-102.  Entomology and Nematology Department, Florida Cooperative Extension Service, Institute of Food and Agricultural Sciences, University of Florida.


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

6/25/18 – 8/09/18


*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.

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;

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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: A

 


Posted by ls 

Sugarcane Beetle | Euetheola humilis rugiceps (LeConte)

California Pest Rating  for
Sugarcane Beetle example
Sugarcane Beetle | Euetheola humilis rugiceps (LeConte)
Coleoptera: Scarabaeidae
Pest Rating: A

PEST RATING PROFILE

Initiating Event:

Euetheola humilis rugiceps is currently Q-rated.  A permanent pest rating proposal is required to support an official pest rating.

History & Status:

Background:  Adult sugarcane beetles are black and approximately 1.5 cm in length.  Larvae are white, C-shaped grubs that live underground (Hammond, 2002).  Adults feed underground on roots and stems of a variety of plants, including corn, sorghum, sugarcane, sweet potatoes, rice, and turfgrass.  This causes significant economic damage to these crops, especially sweet potato and corn (Billeisen and Brandenburg, 2014; Guagliumi, 1960; Smith et al., 2015).  For example, losses of up to 30% of corn plants have been reported, and damage to sweet potatoes in Louisiana was over $1 million in 2010 (Smith et al., 2015).  Adult beetles were reported to attack the trunks of young eucalyptus trees in Brazil, resulting in the death of some trees (Bernardi et al., 2008).  The larvae are suspected to feed on decomposing organic matter and roots.  Damage to the roots of rice plants was reported, but some have suggested that damage to live roots is incidental to feeding on decomposing organic matter (Buntin, 2012; Fritz et al., 2008; Hammond, 2000).  Adult feeding is considered more economically-significant than larval feeding (Catchot, 2013).

The taxonomic history of this beetle is complex (Billeisen and Brandenburg, 2014).  Ratcliffe and Cave (2006) recognized Euetheola humilis (Burmeister) as a valid species and Ligyrus rugiceps LeConte as a synonym.  The sugarcane beetle has been referred to by several names, including Eutheola rugiceps (LeConte), Eutheola humilus (Burmeister), and Euetheola humilis (Burmeister) (note the difference in the spelling of the genus).  Some workers have recognized two separate entities: the subspecies E. humilis Burmeister, in Arizona, Mexico, Central America, and South America, and E. humilis rugiceps LeConte, in the southeastern United States (Hardy, 1991; Smith, 2008).  In this proposal, biological information that was attributed in references to beetles referred to by the names Euetheola humilis and E. rugiceps, (including any subspecies recognized in such references) was considered.

Worldwide Distribution:  The origin of the sugarcane beetle is not known.  However, it was found in the United States as early as 1856, and it is possible that it is native to the entirety of its current distribution (Billeisen and Brandenburg, 2014).  The sugarcane beetle is present in the southeastern United States, southeastern Mexico, Central America (including Panama), and South America (including Argentina, Brazil, and Venezuela) (Billeisen and Brandenburg, 2014).

Official Control: Euetheola humilis rugiceps is not known to be under official control anywhere.

California Distribution:  Euetheola humilis rugiceps is not known to be present in California (Symbiota Collections of Arthropods Network).

California Interceptions:  Euetheola humilis rugiceps was intercepted at border stations on squash and in a trailer from Arkansas and Georgia (CDFA Pest and Damage Report Database, 2018).

The risk Euetheola humilis rugiceps would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: The sugarcane beetle has a broad climatic tolerance. It occurs from the southeastern United States south to Argentina, where it is exposed to temperate, subtropical, and tropical climates.  This beetle feeds on a wide variety of plants, including grasses.  The species could become established over a large portion of California, although probably not in colder, mountainous or northern areas.  Therefore, it 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: The sugarcane beetle is reported to feed on at least three families of plants. Therefore, it 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 Reproductive and Dispersal Potential: The sugarcane beetle flies.  Therefore, it 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: The sugarcane beetle is a pest of many different crops, including corn and sweet potatoes, which are grown in California.  If this beetle became established in California, it could attack these crops, which could lower crop yield and increase production costs.  Therefore, it receives a Medium (2) in this category.

Economic Impact:  A, 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.

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: The sugarcane beetle damages a wide variety of plants through adult and larval feeding. The species could impact native California plants, and as a result, disrupt natural communities.  The feeding on eucalyptus trees by adult sugarcane beetles, reported by Bernardi et al. (2008), demonstrates that trees, and not only food crops and grasses, can be impacted by this beetle.  In addition, if this beetle became a pest in agricultural, ornamental, or residential settings, it could trigger treatments.  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, 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 sugarcane beetle: Medium (12)

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: The sugarcane beetle is not known to be present 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 (12)

Uncertainty:

The sugarcane beetle is widely distributed in the southeastern United States.  Yet, it has not yet become established in California.  This may indicate that the climate of California is not appropriate for this species.  There are native plants in California to which the sugarcane beetle has not been exposed yet in its current range.  The establishment of this beetle in California could have significant environmental impacts in the state not seen in its current range.

Conclusion and Rating Justification:

The sugarcane beetle is a reported pest of many crops, some of which are grown in California.  It is not known to be present in California, but it appears that the climate in this state would be conducive to the establishment of this beetle.  If it became established here, the sugarcane beetle could have economic and environmental impacts.  For these reasons, an “A” rating is justified.


References:

Bernardi, O., Garcia, M. S., Da Cunha, U. S., Back, E. C. U., Bernardi, D., Ramiro, G. A., and Finkenauer, E.  2008.  Ocorrência de Euetheola humilis (Burmeister) (Coleoptera: Scarabaeidae) em Eucalyptus saligna Smith (Myrtaceae), no Rio Grande do Sul.  Neotropical Entomology 37:100-103.

Billeisen, T. L. and Brandenburg, R. L.  2014.  Biology and management of the sugarcane beetle (Coleoptera: Scarabaeidae) in turfgrass.  Journal of Integrated Pest Management 5:1-5.

Buntin, G. D.  2012.  Grain sorghum insect pests and their management.  University of Georgia Cooperative Extension Bulletin no. 1283.

Catchot, A.  2013.  Have a plan for managing sugarcane beetles in field corn.  Mississippi State University Extension.  Accessed January 12, 2018:

Fritz, L. L., Heinrichs, E. A., Pandolfo, M., Martins de Salles, S., Vargas de Oliveira, J., and Fiuza, L. M.  2008.  Agroecossistemas orizícolas irrigados: Insetos-praga, inmigos naturais e manejo integrado.  Oecologia Brasiliensis 12:720-732.

Guagliumi, P.  1960.  Actual situation of entomology of sugar cane in Venezuela. Proceedings of the International Society of Sugarcane Technologists (10th Congress, Hawaii, 1959):1000-1010.

Hammond, A. M.  2002. Sugarcane beetle, Euetheola rugiceps (LeConte), Scarabaeidae, Coleoptera.  Publication 2892.  Louisiana State University Agricultural Center.

Smith, A. B. T.  2008.  Checklist of the Scarabaeoidea of the Nearctic Realm. Version 3.

The University of Nebraska State Museum.  Accessed: March 29, 2018:  http://digitalcommons.unl.edu/entomologypapers/3

Smith, T. P., Beuzelin, J. M., Catchot, A. L., Murillo, A. C., and Kerns, D. L.  2015.  Biology, ecology, and management of the sugarcane beetle (Coleoptera: Scarabaeidae) in sweetpotato and corn.  Journal of Integrated Pest Management 6:1-6.

Symbiota Collections of Arthropods Network.  Accessed March 29, 2018: http://scan1.acis.ufl.edu


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

6/25/18 – 8/09/18


*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.

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 

Slender-banded Pine Cone Longhorn Beetle | Chlorophorus strobilicola

California Pest Rating for
Chlorophorus strobilicola Champion: Slender-banded Pine Cone Longhorn Beetle
Coleoptera: Cerambycidae
Pest Rating: A

 


PEST RATING PROFILE

Initiating Event:

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

History & Status:

Background:  Chlorophorus strobilicola is an elongate beetle that measures 7.5-9.5 mm in length and is reddish-brown with white bands on the elytra (Champion, 1919; Jackson et al., 2010).  This beetle lays eggs in living, green (second and third-year) cones of Pinus roxburghii in India (Singh et al., 2005).  The larvae burrow into and feed on the internal portions of the cone (Duffy, 1953).  This feeding damage results in loss of cone fertility and the cone can break off before it completes development (Champion, 1919).  Up to 40 percent of cones can be infested (Beeson, 1941).  The habitat of this beetle is described as pine forests at elevations of 3500-6500 feet above sea level; the climate in this area is apparently subtropical (Champion, 1919).

Worldwide Distribution:  Chlorophorus strobilicola is only known to occur in Uttarakhand, India (Kariyanna et al., 2017).

Official Control: Chlorophorus strobilicola is a Cooperative Agricultural Pest Survey priority pest (Cooperative Agricultural Pest Survey, 2018).  Interceptions of this beetle triggered a Federal recall of pine cones imported from India in 2003-2004 (North American Plant Protection Organization, 2004).

California Distribution:  Chlorophorus strobilicola is not known to be present in California (Symbiota Collections of Arthropods Network).

California Interceptions:  Chlorophorus strobilicola was intercepted on pine cones from India in Alameda and Fresno counties in 2003 and 2004 (CDFA Pest and Damage Report Database, 2018).  These interceptions were apparently a result of the Federal recall.

The risk Chlorophorus strobilicola would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: The only known host plant of Chlorophorus strobilicola, Pinus roxburghii, may be grown in California, and it is possible that other species of pines present in this state could be utilized by this beetle as well. The native distribution in India of this beetle has a subtropical climate, and that climate might limit the potential distribution of this species in California.  Therefore, it receives a Medium (2) 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: Chlorophorus strobilicola is only known to feed on Pinus roxburghii. Therefore, it receives a Low (1) 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: Chlorophorus strobilicola is capable of flight.  This beetle is also obviously capable of being dispersed through movement of pine cones, as proven by the interception of numerous specimens in the United States of pine cones from India.  However, this may be an unlikely mode of dispersal within California (once this species is already present in the state). Therefore, it 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: Pines are important timber trees in California.  If Chlorophorus strobilicola became established in California, it could reduce the seed yield of pines, which might lower timber yield and impact the industry.  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: If Chlorophorus strobilicola became established in California, it could attack native pines, including some rare ones, including the threatened Santa Rosa Island torrey pine (Pinus torreyana insularis) (Calflora). Attacks on native pine trees could reduce natural regeneration of these species, which could disrupt natural communities.  Pines dominate millions of acres in California, and thus any impact on pines in California could also impact plant and animal species in these ecosystems.  Therefore, this beetle 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 Chlorophorus strobilicola: Medium (9)

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: Chlorophorus strobilicola 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 (9)

Uncertainty:

There is significant uncertainty regarding the ability of Chlorophorus strobilicola to become established in California and the suitability of California pines as host plants.  This beetle appears to be restricted to an area with a subtropical climate, and it is only reported to feed on one species of pine.  This beetle could feed on additional species of pines (possibly including native California species) and could survive in at least one climate represented in California.  Champion (1919) suggested that this beetle might only be able to attack injured cones, but evidence of this was not found in other literature.

Conclusion and Rating Justification:

Chlorophorus strobilicola is a beetle that attacks pine cones in India.  If it can become established in California and attack pines in California, it would pose an economic and environmental threat to the state.  For these reasons, an “A” rating is justified.

References:

Beeson, C. F. C.  1941.  The ecology and control of the forest insects of India and the neighboring countries.  C.F.C. Beeson.  Dehra Dun, India.

Calflora: Information on California plants for education, research and conservation, with data contributed by public and private institutions and individuals, including the Consortium of California Herbaria.  Accessed March 6, 2018: http://www.calflora.org

CDFA Pest and Damage Report Database. 2018. Chlorophorus strobilicola. Plant Health and Pest Prevention Services. CA Department of Food and Agriculture. Accessed April 6, 2018: http://phpps.cdfa.ca.gov/user/frmLogon2.asp

Champion, H. G.  1919.  A cerambycid infesting pine cones from India, Chlorophorus strobilicola, n. sp.  Entomologists’s Monthly Magazine 58:219-224.

Cooperative Agricultural Pest Survey.  2018.  Accessed February 28, 2018: https://caps.ceris.purdue.edu/pest-lists

Duffy, E. A. J.  1953.  A monograph of the immature stages of British and imported timber beetles (Cerambycidae).  British Museum, London.

Jackson, L., Price, T., Smith, G., Campbell, N., and Stiers, E.  2010.  Exotic wood borer/bark beetle national survey guidelines.  Accessed February 28, 2018:  http://apollo.umenfa.maine.edu/SFR457_458_557/Documents/SFR458/EWB_BB%20Survey%20Manual%208_31_10.pdf

Kariyanna, B., Mohan, M., Gupta, R., and Vitali, F.  2017.  The checklist of longhorn beetles (Coleoptera: Cerambycidae) from India.  Zootaxa 4345:001-317.

North American Plant Protection Organization.  2004.  Recall of various products containing pine cones from India.  Accessed February 28, 2018:  www.pestalert.org/oprDetail_print.cfm?oprid=99

Singh, S., Belokobylskij, S. A., Chauhan, N., and Pande, S.  2005.  Description of a new species of the genus Spasskia Belokobylskij, 1989 (Hymenoptera: Braconidae) from India, with first record of the genus in the Oriental region.  Annales Zoologici (Warszawa) 55:95-98.

Symbiota Collections of Arthropods Network.  Accessed March 6, 2018: http://scan1.acis.ufl.edu


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

6/21/18 – 8/5/18


*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.

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 

A Seed Bug | Ochrimnus mimulus (Stal)

California Pest Rating for
Ochrimnus mimulus (Stål): A Seed Bug
Hemiptera: Lygaeidae
Pest Rating: A

 


PEST RATING PROFILE

Initiating Event:

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

History & Status:

Background:  Adult Ochrimnus mimulus measure 5-6 mm in length and are grayish or brownish with pale yellow margins on the forewings and the pronotum (Hoffman, 1996).  This bug is found on and feeds on flowers of Asteraceae.  Baccharis species appear to be the preferred host, but feeding and development can take place on other genera as well.  Eggs are laid in the flowers, and the nymphs feed on these (Gould and Sweet, 2000; Palmer, 1986).  Feeding on flowers reduces seed production by the host plant.  Experiments have shown that this species will attack numerous genera of Asteraceae.  This lack of host specificity made it inappropriate as a biological control organism for the introduced weed Baccharis halimifolia in Australia (Gould and Sweet, 2000).

Worldwide Distribution:  Ochrimnus mimulus occurs in the eastern United States (from Virginia south to Florida and west to Texas), Mexico, and Central America (Cancino and Blanco, 2002; Hoffman, 1996; Slater and Baranowski, 1990).

Official Control: Ochrimnus mimulus is not known to be under official control anywhere.

California Distribution:  Ochrimnus mimulus is not known to occur in California (Symbiota Collections of Arthropods Network).

California Interceptions:  Ochrimnus mimulus has been intercepted on rice, oranges, and bee colonies from Texas (CDFA Pest and Damage Report Database, 2018).

The risk Ochrimnus mimulus would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Ochrimnus mimulus is found over a wide area, from Virginia to Mexico, suggesting that this bug has a wide climatic tolerance. Baccharis, the preferred host genus of mimulus, includes many species that are present in California (Calflora).  It appears likely that O. mimulus could become established over a large portion of California.  Therefore, Ochrimnus mimulus 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: Ochrimnus mimulus appears to be mostly restricted to the Asteraceae, although it feeds on multiple genera within this family. Therefore, it 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: Ochrimnus mimulus can apparently fly (it is collected at light). Therefore, it 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: Ochrimnus mimulus is not known to be an economic pest, even though it is found over a wide area.  It appears unlikely that it would become an economic pest in California if it became established in this state.  Therefore, it receives a Low (1) in this category.

Economic Impact:

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: Ochrimnus mimulus has been shown to have broad feeding preferences within the family Asteraceae and it prefers the genus Baccharis. Coyote brush, Baccharis pilularis, is a dominant shrub of coastal scrub in California.  If O.mimulus attacked this plant, it could impact species of plants and animals that live in these communities.  California also has rare Baccharis species, including Baccharis vanessae R.M. Beauch (Encinitas baccharis), that could be threatened by O. mimulus (Calflora).  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 Ochrimnus mimulus: 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: Ochrimnus mimulus 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:

Even if O. mimulus is capable of becoming established in the state, it is not certain that it would have a significant impact on native plant species.  If this insect became established in California, it could possibly attack crop plants in the family Asteraceae, including artichoke, safflower, and tarragon, although it is not known how much economic damage (if any) would result.

Conclusion and Rating Justification:

Ochrimnus mimulus is a flower-feeding insect that is not known to be present in California.  It poses a threat to native California plants, including rare species.  For these reasons, an “A” rating is justified.

References:

Calflora.  2018.  Information on California plants for education, research and conservation, with data contributed by public and private institutions and individuals, including the Consortium of California Herbaria.  Accessed April 3, 2018: http://www.calflora.org

Cancino, E. R. and Blanco, J. M. C.  2002.  Artrópodos terrestres de los estados de Tamaulipas y Nuevo León, México.  Universidad Autónoma de Tamaulipas, Ciudad Victoria, Tamaulipas, México.

CDFA Pest and Damage Report Database. 2018. Ochrimnus mimulus. Plant Health and Pest Prevention Services. CA Department of Food and Agriculture. Accessed April 9, 2018:  http://phpps.cdfa.ca.gov/user/frmLogon2.asp

Gould, G. G. and Sweet, M. H.  2000.  The host range and oviposition behavior of Ochrimnus mimulus (Hemiptera: Lygaeidae) in central Texas.  The Southwestern Naturalist 45:15-53.

Hoffman, R. L.  1996.  The Insects of Virginia.  Number 14: Seed Bugs of Virginia.  Virginia Museum of Natural History, Martinsville, Virginia.

Palmer, W. A.  1986.  Host specificity of Ochrimnus mimulus (Stål) (Hemiptera: Lygaeidae) with notes in its phenology.  Proceedings of the Entomological Society of Washington 88:451-454.

Slater, J. A. and Baranowski, R. M.  1990.  Arthropods of Florida and Neighboring Land Areas.  Volume 14: Lygaeidae of Florida (Hemiptera: Heteroptera).  Division of Plant Industry, Gainesville, Florida.

Symbiota Collections of Arthropods Network.  Accessed April 3, 2018: http://scan1.acis.ufl.edu


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

6/21/18 – 8/5/18


*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.

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 

Mealybug | Vryburgia succulentarum

California Pest Rating for
Vryburgia succulentarum Williams: mealybug
Hemiptera: Pseudococcidae
Pest Rating: A

 


PEST RATING PROFILE

Initiating Event:

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

History & Status:

Background:   Vryburgia succulentarum is a mealybug that occurs on succulent plants.  Adult females reach 3.1 mm in length (Williams, 1985).  This mealybug has been found on, and presumably feeds on plants in the families Aizoaceae, Cactaceae, and Crassulaceae (García Morales et al., 2016; Moghaddam, 2015; Williams, 1985).  Little else is known about the biology of this species.  Most Vryburgia species are native to Africa and are associated with succulent plants (Li and Suh, 2012).  Some Vryburgia species are capable of inflicting significant damage to succulents.  For example, V. trionymoides can kill succulents and is a greenhouse pest in California (Stocks, 2016).  Mealybugs in other genera that attack succulents have even been used as biological control agents of invasive cacti in Australia and South Africa (Aguirre et al., 2016).

Worldwide Distribution:  Vryburgia succulentarum is reported to occur in southern Australia, Iran (in greenhouses), South Africa, and Tasmania (García Morales et al., 2016; Moghaddam, 2015).  This species may be native to Africa; if so, the other localities represent introductions.

Official Control: Vryburgia succulentarum is not known to be under official control anywhere.

California Distribution:  Vryburgia succulentarum is not known to be present in California (Symbiota Collections of Arthropods Network).

California Interceptions:  Vryburgia succulentarum has not been intercepted in California (CDFA Pest and Damage Report Database, 2018).

The risk Vryburgia succulentarum would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: The full distribution of succulentarum may not be fully known. However, this species has been reported from areas in Australia and Tasmania that have Mediterranean and temperate climates (Atlas of Living Australia; Williams, 1985).  Therefore, much of California could have a suitable climate for this species.  There are many members of the families Cactaceae and Crassulaceae in California, so there are many potential host plants.  It appears likely that this mealybug could establish over a large portion of California.  Therefore, V. succulentarum 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: This mealybug has been reported to be associated with three families of succulent plants.  Therefore, it 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: This mealybug has been intercepted multiple times on plants in quarantine, so it is evidently capable of being spread artificially on infested plants (García Morales et al., 2016).  The Cactaceae and Crassulaceae include many popular landscaping plants, so this mode of dispersal is likely.  Therefore, it 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: The primary economic impact that is anticipated to occur if Vryburgia succulentarum becomes established in California is damage to cacti and succulents.  Nursery production of these plants were worth $83 million in 2016 in California, an increase of 15% from the previous year.  Continued growth appears likely, as water shortages in the state encourage the use of drought-tolerant plants.  Production of cacti and succulents appears to be concentrated in San Diego County (CDFA Nursery Program, 2018; San Diego County Department of Agriculture, Weights and Measures).  If it became established in the state, Vryburgia succulentarum could lower yield and increase production costs of cacti and succulents in California nurseries.  Therefore, it receives a Medium (2) in this category.

Economic Impact:  A, 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.

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: There are numerous rare members of the families Cactaceae and Crassulaceae in California. For example, bright green dudleya (Dudleya virens insularis) and Bakersfield cactus (Opuntia basilaris treleasei) (Calflora).  If V. succulentarum became established in this state, these plants could be threatened.  In addition, if V. succulentarum attacks succulent plants in residential or other areas, this could trigger treatments.  Therefore, it receives a High (3) in this category.

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

Environmental Impact:  B, 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.

Consequences of Introduction to California for Vryburgia succulentarum: Medium (12)

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: Vryburgia succulentarum 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 (12)

Uncertainty:

The distribution and biology of V. succulentarum are poorly known.  The most significant unknown in this proposal is the ability of this mealybug to damage the plants that it feeds upon.  At least one species in the genus is reported to be a pest, but it may not be of economic significance.

Conclusion and Rating Justification:

Vryburgia succulentarum is a mealybug that attacks succulents, including Cactaceae and Crassulaceae.  This mealybug, which is not known to occur in California, poses a threat to native California species and to the nursery industry as well.  For these reasons, an “A” rating is justified.

References:

Aguirre, M. B., Diaz-Soltero, H., Claps, L. E., Saracho Bottero, A., Triapitsyn, S., Hasson, E., and Logarzo, G. A.  2016.  Studies on the biology of Hypogeococcus pungens (sensu stricto) (Hemiptera: Pseudococcidae) in Argentina to aid the identification of the mealybug pest of Cactaceae in Puerto Rico.  Journal of Insect Science 16:1-7.

Atlas of Living Australia website.  Accessed March 29, 2018: http://www.ala.org.au

Calflora: Information on California plants for education, research and conservation, with data contributed by public and private institutions and individuals, including the Consortium of California Herbaria.  Accessed March 26, 2017: http://www.calflora.org

CDFA Nursery Program.  2018. Value of California nursery products.  Nursery Advisory 01-2018:1-2.

CDFA Pest and Damage Report Database. 2018. Vryburgia succulentarum. Plant Health and Pest Prevention Services. CA Department of Food and Agriculture. Accessed April 5, 2018: http://phpps.cdfa.ca.gov/user/frmLogon2.asp

García Morales, M., Denno, B. D., Miller, D. R., Miller, G. L., Ben-Dov, Y., and Hardy, N. B. 2016.  ScaleNet: A literature-based model of scale insect biology and systematics.  Accessed March 28, 2018: http://scalenet.info

Ji, J. and Suh, S.-J.  2012.  A list of scale insects (Hemiptera: Coccoidea) intercepted in quarantine on imported succulent plants in Korea 2006-2010.  Insecta Mundi 0272:1-5.

Moghaddam, M.  2015.  New records of mealybug species in Iran with discussions on morphological variations (Hemiptera, Coccoidea: Pseudococcidae).  Entomologica Fennica 26:122-131.

San Diego County Department of Agriculture, Weights and Measures.  County of San Diego Crop Statistics & Annual Report (2016).  Accessed June 18, 2018:   https://www.sandiegocounty.gov/content/dam/sdc/awm/docs/AWM_2016_Crop_Report.pdf

Stocks, I.  2016.  A mealybug – Vryburgia trionymoides (DeLotto) (Pseudococcidae).  Florida Department of Agriculture and Consumer Services, Division of Plant Industry.  Accessed: April 5, 2018: http://entnemdept.ufl.edu/creatures/ORN/MEALYBUG/vryburgia_trionymoides.htm

Symbiota Collections of Arthropods Network.  Accessed March 28, 2018: http://scan1.acis.ufl.edu

Williams, D. J.  1985.  Australian mealybugs.  British Museum of Natural History, London.


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

6/20/18 – 8/4/18


*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.

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 

A Mealybug | Trionymus sasae (Kanda)

California Pest Rating for
Trionymus sasae (Kanda): a mealybug
Hemiptera: Pseudococcidae
Pest Rating: A

 


PEST RATING PROFILE
Initiating Event:

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

History & Status:

Background:  Trionymus sasae is only known to occur in Japan and it is associated with (and presumably feeds on) bamboo (García Morales et al., 2016).  The localities it is reported from in Japan have a subtropical climate (Kawai, 1980).  Other species of Trionymus are also associated with grasses (Poaceae), and some are pests of crop (e.g., barley and sugarcane) or ornamental (e.g., bamboo) plants (Alvarez, 2004; Jansen, 2009; Portilla and Cardona, 2004).

Worldwide Distribution:  Trionymus sasae is only known from Japan.  It was reportedly intercepted in California on bamboo from Oregon in 1995, so it is possible that this mealybug may be established in other areas (possibly Oregon), but if so, this has not been reported (Gill, 1995).  Alternatively, this bamboo may have originally been shipped from Japan.

Official Control: Trionymus sasae is not known to be under official control anywhere.

California Distribution:  Trionymus sasae is not known to be present in California.

California Interceptions:  Trionymus sasae has been intercepted on bamboo from Japan and Oregon (California Department of Food and Agriculture; Gill, 1995).

The risk Trionymus sasae would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: The areas in Japan where sasae is reported to occur have a subtropical climate. If this mealybug became established in California, it might be limited to warmer areas, for example, the southern coast.  Therefore, T. sasae receives a Medium (2) 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: Trionymus sasae has been associated with two genera of bamboo. Therefore, it receives a Low (1) 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: Trionymus sasae has been intercepted on bamboo, so it is apparently capable of being dispersed through shipment of plant material.  Bamboo is a popular plant and is presumably moved frequently throughout the state.  Therefore, sasae 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: Trionymus sasae lives on bamboo plants, which are popular ornamentals in California.  If this mealybug became established in California, it could attack bamboo plants in nurseries, impacting their health or at least detracting from their appearance and value.  This could increase production costs.  Therefore, sasae receives a Low (1) in this category.

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.

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: There are many rare species in the family Poaceae in California (Calflora). If sasae became established in California, it could threaten some of these species.  This mealybug could also impact ornamental bamboo plantings, and this could trigger treatments.  Therefore, it receives a High (3) in this category.

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

Environmental Impact:  B, 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.

Consequences of Introduction to California for Trionymus sasae: Medium (9)

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: Trionymus sasae is not known to be present 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 (9)

Uncertainty:

The known distribution of this species suggests it may be limited to warmer (subtropical) climates.  If so, it may not be capable of establishment in California, or its area of potential distribution in the state could be quite limited.  The potential of T. sasae to damage plants is also not known.  Little information is available on this species, so the pest significance of other Trionymus species was considered in this proposal.  The potential of this mealybug to impact native grasses in California would require that this species not be limited to bamboo.

Conclusion and Rating Justification:

Very little information is available regarding the biology of Trionymus sasae.  This mealybug is not known to be present in California and it attacks bamboo (an important ornamental plant in the state).  For these reasons, an “A” rating is justified.


References:

Alvarez, J.M.  2004.  Trionymus haancheni McKenzie: A new pest of barley in Idaho.  Plant Management Network.  5 pp.

Calflora: Information on California plants for education, research and conservation, with data contributed by public and private institutions and individuals, including the Consortium of California Herbaria.  Accessed March 30, 2017 http://www.calflora.org

California Department of Food and Agriculture.  Pest and damage record database.  Accessed March 30, 2018. https://pdr.cdfa.ca.gov/PDR/pdrmainmenu.aspx

García Morales, M., Denno, B.D., Miller, D.R., Miller, G.L., Ben-Dov, Y., and Hardy, N.B. 2016.  ScaleNet: A literature-based model of scale insect biology and systematics.  Accessed March 28, 2018  http://scalenet.info

Gill, R.J.  1995.  Exclusion.  California Plant Pest and Disease Report.  14: 8-12.

Jansen, M.  2009.  New and less observed scale insect species for the Dutch fauna (Hemiptera: Coccoidea).  Entomologische Berichten.  69: 162-168.

Kawai, S.  1980.  Scale Insects of Japan in Colors.  National Agricultural Education Association.  Tokyo.  455 pp.

Portilla, A.A.R. and Cardona, F.J.S.  2004.  Coccoidea de Colombia, con énfasis en las cochinillas harinosas (Hemiptera: Pseudococcidae).  Revista Facultad Nacional de Agronomía Medellín.  57: 2383-2412.

Symbiota Collections of Arthropods Network.  Accessed March 30, 2018. http://scan1.acis.ufl.edu


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

4/30/18 – 6/14/18


*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.

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 

A Thrips | Coremothrips pallidus Hood

California Pest Rating for
Coremothrips pallidus Hood: a thrips
Thysanoptera: Thripidae
Pest Rating: A

 


PEST RATING PROFILE
Initiating Event:

Coremothrips pallidus was recently reported to be established in Hawaii (Mound et al., 2017).  It is currently Q-rated, and a permanent pest rating proposal is required to support an official pest rating.

History & Status:

Background:  Coremothrips pallidus is a tiny (~1 mm in length), pale yellowish-white thrips (Hood, 1925).  It has been found feeding on avocado leaves in Hawaii (Mound et al., 2017).  Adults and larvae were found on Guettarda scabra (Rubiaceae) in Guadeloupe, which suggests that this plant was being fed upon (Etienne et al., 2015).  It has also been found on leaves of other plants in the families Bixaceae, Combretaceae, Sterculiaceae, and Ulmaceae, but it is not known if these records represent feeding (Cavalleri, 2015; Etienne et al., 2015; Goldarazena et al., 2012; Hood, 1925).

Worldwide Distribution:  Coremothrips pallidus has been reported from Central America (Panama), South America (Brazil), and the Caribbean (Guadeloupe, Saint Vincent, and Trinidad) (Cavalleri, 2005; Etienne et al., 2015; Monteiro, 2002; Symbiota Collections of Arthropods Network).  It was recently reported to be established on the islands of Hawaii and Oahu in Hawaii (Mound et al., 2017).

Official Control: Coremothrips pallidus is not known to be under official control anywhere.

California Distribution:  Coremothrips pallidus is not known to be present in California.

California Interceptions:  Coremothrips pallidus has not been intercepted in California.

The risk Coremothrips pallidus would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Coremothrips pallidus appears to feed on at least two species of plants, including avocado. Avocado is widely planted in southern California.  However, this thrips is apparently restricted to tropical or subtropical areas.  It is possible that it could become established in a limited portion of California.  Therefore, Coremothrips pallidus receives a Medium (2) 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: Although pallidus has been reported from several plants species, only two of these plants are considered verified hosts here: Avocado (because the report specified that feeding had occurred) and Guettarda scabra (because adults and larvae were found on this plant), representing two families. It is likely that some of the other plants in the families listed above (under Background) were also fed upon.  Therefore, C. pallidus 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: Coremothrips pallidus has wings and presumably flies.  It could also be dispersed artificially via transport of infested plant material.  Lastly, it may be capable of wind-aided dispersal.  Therefore, it 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: Coremothrips pallidus has been reported to feed on avocado, which is an important crop in California.  If this species was established in California, it is possible that it could lower the value of avocados.  Therefore, it receives a Low (1) in this category.

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.

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: Coremothrips pallidus feeds on plants in at least two families. If this species became established in California, it would encounter plants that are not present in the area of its current distribution.  If it fed on these plants, it is possible that this thrips could have an impact on natural communities.    Therefore, it receives a Medium (2) in this category.

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

Environmental Impact: A

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:

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 Coremothrips pallidus: Medium (9)

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: Coremothrips pallidus 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 (9)

Uncertainty:

Coremothrips pallidus is fairly widely distributed, and yet there do not appear to be any reports of this species being a pest.  It is therefore possible that this proposal is overly pessimistic and this thrips may not become a problem even if it was established in California. Some thrips are vectors of plant viruses, and it is possible (though no reports were found of C. pallidus vectoring diseases) that this species could transmit virus diseases of avocado if it was established in California.

Conclusion and Rating Justification:

Coremothrips pallidus is a plant-feeding thrips that attacks avocado and is not known to be present in California.  If it became established in this state, it could impact avocado cultivation and could also have environmental impacts.  For these reasons, an “A” rating is justified.


References:

Cavalleri, A.  2005.  Comunidades de tripes (Insecta: Thysanoptera) em flores e ramos, com ênfase em Asteraceae, no Parque Estadual de Itapuã, Vlamão, RS.  Ph.D. dissertation.  Instituto de Biociências da Universidade Federal do Rio Grande do Sul, Porto Alegre.

Etienne, J., Ryckewaert, P., and B. Michel.  2015.  Thrips (Insecta: Thysanoptera) of Guadeloupe and Martinique: Updated check-list with new information on their ecology and natural enemies.  Florida Entomologist.  98(1): 298-304.

Goldarazena, A., Gattesco, F., Atencio, R., and C. Korytowski.  2012.  An updated checklist of the Thysanoptera of Panama with comments on host associations.  Check List.  8(6): 1232-1247.

Hood, J.D.  1925.  New neotropical Thysanoptera collected by C.B. Williams.  1925.  Psyche.  32: 48-69.

Monteiro, R.  2002.  The Thysanoptera fauna of Brazil.  Pages 325-340 in R. Marullo and L. Mound, editors.  Thrips and Tospoviruses: Proceedings of the 7th International Symposium on Thysanoptera.  Australian National Insect Collection, Canberra.  390 pp.

Mound, L.A., Matsunaga, J.N., Bushe, B., Hoddle, M.S., and A. Wells.  2017.  Adventive Thysanoptera species in the Hawaiian Islands: New records and putative host associations.  Proceedings of the Hawaiian Entomological Society.  49: 17-28.

Symbiota Collections of Arthropods Network.  Accessed 13 November 2017.  http://scan1.acis.ufl.edu


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

4/30/18 – 6/14/18


*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.

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 

Thrips | Indusiothrips seshadrii Priesner

California Pest Rating  for
Indusiothrips seshadrii Priesner: thrips
Thysanoptera: Thripidae
Pest Rating: A

 


PEST RATING PROFILE
Initiating Event:

A specimen of Indusiothrips seshadrii was recently found on Oahu Island, Hawaii (Mound et al., 2017).  It is currently Q-rated, and a permanent pest rating proposal is required to support an official pest rating.

History & Status:

Background:  Indusiothrips seshadrii is a small (~1 mm in length), whitish-yellow thrips (Priesner, 1952).  It has been reported from unidentified ferns in India and Hawaii (Mound et al., 2017; Priesner, 1952).  This species appears to be rarely collected, and little additional information is available regarding its biology.

Worldwide Distribution:  Indusiothrips seshadrii is known from, and is presumed native to India and Malaysia (Kudô, 1992; Priesner, 1952).  It has been introduced to Oahu, Hawaii (Mound et al., 2017).

Official Control: Indusiothrips seshadrii is not known to be under official control anywhere.

California Distribution:  Indusiothrips seshadrii is not known to occur in California.

California Interceptions:  Indusiothrips seshadrii has not been intercepted in California.

The risk Indusiothrips seshadrii would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Although seshadrii is presumed to feed on ferns, the species it feeds on are not known. California has many species of native ferns, and it is possible that I. seshadrii could find suitable host plants over much of the state.  However, this thrips is currently known to be limited to areas with a tropical climate.  For this reason, I. seshadrii is not expected to be capable of establishing over more than a very limited area.  Therefore, Indusiothrips seshadrii receives a Low (1) 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: Indusiothrips seshadrii may feed on ferns. However, it is not known what species in particular act as hosts.  The fact that it is known from India, Malaysia, and Hawaii suggests that more than a single species of fern is involved.  To incorporate this uncertainty, host range will be considered to be moderate.  Therefore, it 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: This species has wings and presumably flies (Priesner, 1952).  Therefore, it 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: Indusiothrips seshadrii is presumed to feed on ferns.  It has not been reported to be a pest, and it does not appear to pose an economic threat to California.  Therefore, it receives a Low (1) in this category.

Economic Impact:

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: Indusiothrips seshadrii is presumed to feed on ferns. No reports were found indicating the extent, if any, of damage inflicted by these thrips on ferns.  However, this could simply be because the host plants are not economically significant.  There are many rare, native ferns in California.  If this thrips became established in California, it could feed on and impact our native ferns.  Therefore, it receives a Medium (2) in this category.

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

Environmental Impact:  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.

Score the pest for Environmental Impact. Score:

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 Indusiothrips seshadrii: Low (8)

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: Indusiothrips seshadrii 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: Low (8)

Uncertainty:

No reports were found indicating that I. seshadrii has any economic or environmental impact, although this could simply reflect a lack of study of the biology of this species because it does not feed on economically-significant plants.  It is possible that I. seshadrii may not be capable of becoming established in California because it requires a tropical climate.

Conclusion and Rating Justification:

Indusiothrips seshadrii is a thrips that apparently feeds on ferns and is not known to be present in California.  It poses a risk to the environment, including rare fern species, of which there are many in California.  For these reasons, an “A” rating is justified.


References:

Kudô, I.  1992.  A new Malaysian thrips with notes on some species of Dendrothripoides and Indusiothrips (Thysanoptera, Thripidae).  Insecta Matsumurana.  47: 91-101.

Mound, L.A., Matsunaga, J.N., Bushe, B., Hoddle, M.S., and A. Wells.  2017.  Adventive Thysanoptera species in the Hawaiian Islands: New records and putative host associations.  Proceedings of the Hawaiian Entomological Society.  49: 17-28.

Priesner, H.  1952.  On some new genera and species of Thysanoptera from the Oriental region.  Indian Journal of Entomology.  13: 183-200.

Symbiota Collections of Arthropods Network.  Accessed 18 December 2017. http://scan1.acis.ufl.edu


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

4/30/18 – 6/14/18


*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.

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 

Weevil | Dryophthorus homoeorhynchus Perkins

California Pest Rating for 
Dryophthorus homoeorhynchus Perkins: weevil
Coleoptera: Dryopthoridae
Pest Rating: C

 


PEST RATING PROFILE
Initiating Event:

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

History & Status:

Background:  This beetle is black in color, elongate, and 4.5-6 mm in length.  The species has a short rostrum (“beak”) (Perkins, 1900).  Larvae of all species of Dryophthorus, including D. homoeorhynchus, apparently feed on rotting plant material, primarily wood.  Dryophthorus homoeorhynchus is reported to feed on decomposing Chrysodracon species (Dracaenaceae) in Hawaii (Swezey, 1931; Swezey, 1954; Wagner et al., 2005).  Other species in the genus are reported to feed on rotting hardwood and conifer wood, and at least one species has been reported to feed on rotting tree fern fronds (Hawaiian Entomological Society, 1928; O’Brien, 1997).

Worldwide Distribution:  This beetle is native to, and is only known to occur in Hawaii.  The species has been reported from Hawaii, Oahu, Maui, and Molokai islands (Natural Resources Conservation Service, 2009; Swezey, 1954).

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

California Distribution:  This beetle is not known to be present in California (Symbiota Collections of Arthropods Network).

California Interceptions:  This beetle was intercepted on pineapple from Hawaii in February 2004 (California Department of Food and Agriculture).

The risk Dryophthorus homoeorhynchus would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: Dryophthorus homoeorhynchus is only known to occur in Hawaii. If this beetle requires the climate found in its current area of distribution, then only a small portion of California would offer a similar suitable climate.   At least one species in the family Dracaenaceae, Dracaena draco, is grown as an outdoor plant in California and could possibly serve as a host plant for homoeorhynchus.  Due to the apparent climate restrictions, it appears unlikely that this beetle could become established in more than a small portion of California.  Therefore, D. homoeorhynchus receives a Low (1) 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: Dryophthorus homoeorhynchus is only known to feed on the genus Chrysodracon. Therefore, it receives a Low (1) 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: The biology of homoeorhynchus is poorly known.  The beetle is assumed to fly.  Therefore, it 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: This beetle is only known to feed on dead plant material, as are all other members of the genus.  Negative economic impacts are unlikely if this beetle became established in California.  The species apparently feeds on decomposing plant material, not freshly-cut wood, and is known to be restricted to plants in the family Dracaenaceae, therefore there is little risk to timber. Therefore, it receives a Low (1) in this category.

Economic Impact:

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: Negative environmental impacts of this species if it became established in California appear minimal. The species feeds on dead plant material, and it appears to be restricted to a family of plants, the Dracaenaceae, that do not include any native California species.  Therefore, it receives a Low (1) in this category.

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

Environmental 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.

Environmental Impact Score: 1

– 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 Dryophthorus homoeorhynchus: Low (6)

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: Dryophthorus homoeorhynchus 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: Low (6)

Uncertainty:

Dryophthorus homoeorhynchus may be able to tolerate cooler temperatures than are present in its native distribution.  If this is the case, the species could become established over a greater portion of California if suitable plant material is present.  The beetle may also be able to feed on plants in families other than Dracaenaceae.  Feeding on living plant tissue, however, has not been reported in Hawaii and apparently all species in the genus Dryophthorus feed on dead, rotting plant tissue.

Conclusion and Rating Justification:

Dryophthorus homoeorhynchus is a tropical/subtropical beetle that feeds on dead plants in the family Dracaenaceae, and it is a member of a genus that is apparently restricted to dead, rotting plant material.  This beetle appears to pose no threat, economic or environmental, to California.  For these reasons, a “C” rating is justified.


References:

California Department of Food and Agriculture.  Pest and damage record database.  Accessed March 22, 2018. https://pdr.cdfa.ca.gov/PDR/pdrmainmenu.aspx

Hawaiian Entomological Society.  1928.  January 6, 1927; notes and exhibitions.  Proceedings of the Hawaiian Entomological Society.  7: 1-31.

Natural Resources Conservation Service.  2009.  At-risk species and habitats lists.  Biology Technical Note.  22: 1-403.

O’Brien, C.W.  1997.  A catalog of the Coleoptera of America north of Mexico.  Family: Curculionidae.  Subfamilies: Acicnemidinae, Cossoninae, Rhytirrhininae, Molytinae, Petalochilinae, Trypetidinae, Dryophthorinae, Tachygoninae, Thecesterninae.  United States Department of Agriculture.  48 pp.

Perkins, R.C.L.  1900.  II.  Coleoptera Rhyncophora, Proterhinidae, Heteromera and Cioidae.  117-270 in   (D. Sharp, ed.) Fauna Hawaiiensis.  Cambridge University Press.  London.  579 pp.

Swezey, O.H.  1931.  Some new records of insects on Molokai.  Proceedings of the Hawaiian Entomological Society.  7: 485-488.

Swezey, O.H.  1954.  Forest entomology in Hawaii.  Bernice P. Bishop Museum Special Publication.  44: 1-265.

Symbiota Collections of Arthropods Network.  Accessed March 20, 2018. http://scan1.acis.ufl.edu

Wagner, W.L., Herbst, D.R., and Lorence, D.H.  2005.  Flora of the Hawaiian Islands.  Accessed March 20, 2018. http://botany.si.edu/pacificislandbiodiversity/hawaiianflora/index.htm


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

4/30/18 – 6/14/18


*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.

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: C

 


Posted by ls 

A Leafhopper | Paraulacizes irrorata (Fabricus)

California Pest Rating for
Paraulacizes irrorata (Fabricius): a leafhopper
Hemiptera: Cicadellidae
Pest Rating: A

 


PEST RATING PROFILE
Initiating Event:

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

History & Status:

Background:  This is a large (~14 mm in length) leafhopper that is dark with numerous tiny, yellow spots (Overall and Rebek, 2017; Young, 1968).  It is reported to feed on a variety of plants, including thistles (Cirsium spp.) (Asteraceae), crape myrtle (Lagerstroemia indica) (Lythraceae), Virginia wildrye (Elymus virginicus) (Poaceae), horseweed (Conyza canadensis) (Asteraceae), prickly lettuce (Lactuca serriola) (Asteraceae), wholeleaf rosinweed (Silphium integrifolium) (Asteraceae), and sorghum (Sorghum sp.) (Poaceae).  It is found in vineyards, fruit orchards, and tree nurseries, so it is possible that it feeds on grapevines and trees (Ma et al., 2010; Myers et al., 2007; Overall, 2013).  Eggs are laid inside twigs and woody/hardened stems and leaf petioles (Tipping et al., 2006).  In a study in North Carolina vineyards, P. irrorata was shown to carry Xylella fastidiosa, the bacteria that causes Pierce’s disease and almond leaf scorch (Myers et al., 2007; Sisterson et al., 2010).  However, P. irrorata has not yet been shown to transmit the disease (Overall and Rebek, 2017).

Worldwide Distribution:  Paraulacizes irrorata is reported from the central, northeastern, and southeastern United States, Canada (Ontario), and northern Mexico (Maw et al., 2000; Pajero et al., 2008).

Official Control: Paraulacizes irrorata is not known to be under official control anywhere.

California Distribution:  Paraulacizes irrorata is not known to occur in California (Symbiota Collections of Arthropods Network).

California Interceptions:  Paraulacizes irrorata has been intercepted on plants from Arkansas, West Virginia, Louisiana, and Oklahoma in 1992, 2000, and 2007, in a trailer from Arkansas in 2017, on aircraft from Tennessee in 2000 and 2002, and on a FedEx shipment from Florida in 2017 (California Department of Food and Agriculture).

The risk Paraulacizes irrorata would pose to California is evaluated below.

Consequences of Introduction:

1) Climate/Host Interaction: The distribution of Paraulacizes irrorata extends from northern Mexico to Ontario, Canada.  This suggests that it could become established over a wide area in California.  This leafhopper feeds on a wide variety of plants, and there are likely suitable host plants in much of the state.  Therefore, Paraulacizes irrorata 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: Paraulacizes irrorata has been reported to feed on at least seven genera of plants in three families, but it probably has a much broader host range than this. Therefore, it receives a High (3) 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: Paraulacizes irrorata presumably flies.  Therefore, it 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: Paraulacizes irrorata feeds on a broad range of plants.  The feeding damage could possibly lower crop yield, but a more serious concern, and a general one for the family Cicadellidae, is the potential for vectoring plant diseases.  It is not known if irrorata can vector plant diseases, but it has been confirmed as a carrier of Xylella fastidiosa, the bacteria that causes Pierce’s disease and almond leaf scorch.  If it was introduced to California, P. irrorata could potentially vector such pathogens and impact crops, including grapes and almonds.  Therefore, it receives a Medium (2) in this category.

Economic Impact:  A, E

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: The presence of Praulacizes irrorata could trigger treatment programs. Therefore, it receives a Medium (2) in this category.

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

Environmental Impact:  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: 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 Paraulacizes irrorata: Medium (12)

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: Paraulacizes irrorata 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 (12)

Uncertainty:

The possible impact of Paraulacizes irrorata is somewhat speculative and it is based on demonstrated examples of impact from other cicadellid species and the possibility of this leafhopper vectoring Pierce’s disease (or other diseases) in crops, including grapes.  This leafhopper has not been proven to transmit any plant diseases.

Conclusion and Rating Justification:

Paraulacizes irrorata is a plant-feeding insect that is potentially capable of vectoring plant diseases, including the causative agent of Pierce’s disease, Xylella fastidiosa.  There is little evidence that P. irrorata has a significant economic or environmental impact in its current range.  However, if it was established in California, this insect would be exposed to a new combination of variables, including new host plants and plant diseases; it is difficult to predict what impacts could result.  For these reasons, an “A” rating is justified.


References:

California Department of Food and Agriculture.  Pest and damage record database.  Accessed April 2, 2018. https://pdr.cdfa.ca.gov/PDR/pdrmainmenu.aspx

Maw, H.E.L., Foottit, R.G., Hamilton, K.G.A., and Scudder, G.G.E.  2000.  Checklist of the Hemiptera of Canada and Alaska.  National Research Council, Canada.  220 pp.

Myers, A.L., Sutton, T.B., Abad, J.A., and Kennedy, G.G.  2007.  Pierce’s disease of grapevines; Identification of the primary vectors in North Carolina.  Phytopathology.  97: 1440-1450.

Overall, L.M.  2013.  Incidence of Xylella fastidiosa in Oklahoma, survey of potential insect vectors, and identification of potential plant reservoir hosts.  Ph.D. Dissertation.  Oklahoma State University.  155 pp.

Overall, L.M. and Rebek, E.J.  2017.  Insect vectors and current management strategies for diseases caused by Xylella fastidiosa in the southern United States.  Journal of Integrated Pest Management.  8: 1-12.

Paiero, S.M., Marshall, S.A., Pratt, P.D., and Buck, M.  2008.  The insects of Ojibway Prairie, a southern Ontario tallgrass prairie.

Sisterson, M.S., Thammiraju, S.R., Lynn-Patterson, K., Groves, R.L., and Daane, K.M.  2010.  Epidemiology of diseases caused by Xylella fastidiosa in California: Evaluation of alfalfa as a source of vectors and inocula. Plant Disease. 94: 827-834.

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

Tipping, C., Triapitsyn, S.V., and Mizell III, R.F.  2006.  First record of an egg parasitoid for the North American proconiine sharpshooter Paraulacacizes irrorata (Hemiptera: Cicadellidae), with notes on rearing techniques.  Florida Entomologist.  89(2): 288-289.

Young, D.A.  1968.  Taxonomic study of the Cicadellinae (Homoptera: Cicadellidae); Part 1: Proconiini.  United States National Museum Bulletin.  261.  287 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

4/30/18 – 6/14/18


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Pest Rating: A

 


Posted by ls