Risk Analysis in the Release of Biological Control Agents: AntagonisticFusarium oxysporumas a Case Study

Plant Disease ◽  
1995 ◽  
Vol 79 (12) ◽  
pp. 1193 ◽  
Author(s):  
M. Lodovica Gullino
2018 ◽  
Vol 127 ◽  
pp. 31-38 ◽  
Author(s):  
Louise B. Rasmussen ◽  
Kim Jensen ◽  
Jesper G. Sørensen ◽  
Elsa Sverrisdóttir ◽  
Kåre L. Nielsen ◽  
...  

2010 ◽  
Vol 3 (4) ◽  
pp. 462-469 ◽  
Author(s):  
Jennifer L. Birdsall ◽  
George P. Markin

AbstractYellow starthistle is an invasive, annual, spiny forb that, for the past 30 yr has been steadily advancing up the Salmon River Canyon in west central Idaho. In 1994, a decision was made to attempt to manage yellow starthistle by establishing a complex of biological control agents in a containment zone where the weed was most dense. Between 1995 and 1997, six species of seedhead-attacking insects were introduced and successfully established. By 1999, the insects had spread through the entire containment zone. Following this dispersal, a rapid buildup of insect populations occurred, and, since 2003, seed destruction has fluctuated around 90%. Vegetation monitoring plots, however, have shown no consistent decline in the overall population of yellow starthistle, indicating that the amount of seed produced is still sufficient to allow full replacement. However, county weed control personnel, who are responsible for surveying and destroying outlying populations of yellow starthistle beyond the containment zone, report that, during this period, the number of new, isolated pockets of yellow starthistle they are finding has dropped dramatically. This case study discusses how the biological control program partially met the objective of managing yellow starthistle by reducing the rate of advance of this weed in the Salmon River Canyon.


EDIS ◽  
2017 ◽  
Vol 2017 (6) ◽  
Author(s):  
James P. Cuda ◽  
Patricia Prade ◽  
Carey R. Minteer-Killian

In the late 1970s, Brazilian peppertree, Schinus terebinthifolia Raddi (Sapindales: Anacardiaceae), was targeted for classical biological control in Florida because its invasive properties (see Host Plants) are consistent with escape from natural enemies (Williams 1954), and there are no native Schinus spp. in North America. The lack of native close relatives should minimize the risk of damage to non-target plants from introduced biological control agents (Pemberton 2000). [...]


Sign in / Sign up

Export Citation Format

Share Document