Teliospores appear in the uredinia or telia (Liberato et al. 2007). Teliospores are club shaped, ellipsoid to oblong measuring 30-48 x 17-22µm.They are rounded at the apex, narrow below and slightly constricted at the septum. The cell walls are pale yellow in colour, smooth and measure 1.5-2.5 µm thick at sides and 2-4 µm at apex (Hernández 2006). Teliospores are bicellular, and both cells can germinate to form basidia. Basidia are 40 to 70 µm in length and only 0.1% produce basidiospores, which are borne on sterigmata (Ferreira 1989 in Coutinho et al. 1998). It is not known if the basidiospores are uni- or bi- nucleate (Simpson et al. 2006). Aeciospores are morphologically identical to urediniospores (Liberato et al. 2007).
Symptoms on susceptible hosts appear as brown to grey lesions with masses of yellow or orange-yellow urediniospores on young, actively growing leaves, shoots, fruits and sepals. Lesions may have sori containing dark brown teliospores. Purpling of leaf and shoot margins occur on older lesions in some host species. Severe disease in young trees may kill shoot tips, causing loss of leaders and a bushy growth form to develop. In eucalypts prolific branching and galling is a symptom of previous rust infection (Glen et al. 2007).
Please see PaDIL (Pests and Diseases Image Library) Species Content Page Fungi: Eucalyptus rust for high quality diagnostic and overview images.
Several races or biotypes of P. psidii are known to exist, which differ in their host specificity, environmental tolerances, characteristics of sporulation and spore survival, and virulence. However very little is known of these specialized forms (Glen et al 2007).
A diagram detailing the lifecycle of P. psidii is available in Glen et al. (2007).
Principal source: Glen et al. 2007; Loope and La Rosa 2008; Simpson et al. 2006; Tommerup et al. 2003.
Compiler: IUCN SSC Invasive Species Specialist Group (ISSG) with support from the Ministry of Agriculture and Forestry (MAF)- Biosecurity New Zealand
Review:
Publication date: 2010-06-22
Recommended citation: Global Invasive Species Database (2024) Species profile: Puccinia psidii. Downloaded from http://iucngisd.org/gisd/species.php?sc=1538 on 24-11-2024.
Tommerup et al. (2003) report that “The disease is particularly severe on susceptible eucalypt seedlings, cuttings, juvenile trees, or coppice from stumps or damaged mature trees. Heavy infection of juvenile eucalypt shoots causes plants to be stunted and multi-branched, reducing their potential to develop into marketable trees”. There is wide variety in susceptibility to P. psidii among young eucalypt trees. Usually around 10-20% of a stand is highly susceptible, causing gross malformations and death. The pathogen is particularly virulent on species with no evolutionary history of exposure (naïve hosts) (Loope and La Rosa 2008).
P. psidii has already had devastating impacts on some industries. Oil refineries based on Pimenta dioica in Jamaica were forced to close two years after P. psidii was first recorded on the island (Maclachlan 1938 in Booth et al. 2000).
There is also potential for this pathogen to cause damage in natural ecosystem. The family Myrtaceae consists of approximately 3600 species in 155 genera distributed across Australia, South-east Asia, New Caledonia and other Pacific Islands, South and Central America and southern Africa (Tommerup et al. 2003). In many of these countries susceptible trees are significant components of communities. For example in Australia many ecosystems are dominated by Eucalyptus (Booth et al. 2000), and in Hawai'I the ohia (Metrosideros polymorpha) is the dominant tree in most of Hawai'I's forests. Outbreaks of P. psidii which affect these dominant trees could result in significant changes to the structure, composition, and potentially, the function, of forests on a landscape level. This would likely have impacts on biodiversity of other flora and fauna in these ecosystems (Loope and La Rosa 2008).
Detection and Prediction: Early, rapid and accurate pathogen diagnosis is critical for management of high-quarantine-risk pathogens such as P. psidii. Langrell et al. (2008) developed a species-specific, nested polymerase chain reaction (PCR)-based detection assay for P. psidii. They report that “The assay reliably, accurately and sensitively detected the rust from naturally infected, geographically widespread eucalypt and fruit tree plantation and nursery species from diverse tissues types including symptomless or cryptically contaminated plants or plant tissue.” This assay provides an effective biosecurity tool for rapid responses to threats or incursions of P. psidii (Langrell et al. 2008).
Booth et al. (2000) modeled disease-prone regions using climate interpolation and disease-hazard mapping methods. They showed that areas highly prone to the rust occur across tropical and subtropical regions globally. These areas are likely to coincide with major eucalypt- and melaleuca-oil production areas (Booth et al. 2000).
Chemical: Fungicide use is most appropriate in nurseries and clonal hedge plantings, as it is not cost effective for large areas. Fungicides used include the protectant fungicide mancozeb and the systemic fungicides triamenol and triforine. In most cases, however, resistant trees are chosen over susceptible varieties, eliminating the need for fungicides (Old et al. 2003).
Biological: There are a number of biological control agents with potential for management of P. psidii. Bacillus subtilis was found to be effective in reducing in vitro germination of P. psidii, although there are no field experiments to confirm this and it may be difficult to reproduce in vivo (van Toor et al. 2005 in Glen et al. 2007). However these initial results are promising and deserve further investigation.
Other biological agents with potential include Fusarium decemcellulare, a hyper-parasite of P. psidii (Amorium et al. 1993 in Glen et al. 2007), and other fungi which co-occur in rust pustules. Strains of rhizobacteria (Pseudomonas aeruginosa) which have been demonstrated to induce systemic resistance in some trees may be developed into tools for managing disease (Glen et al. 2007). Glen et al. (2007) however, state that “Much further work is also necessary before any fungus or bacterium can be recommended as a biological control agent.”
Breeding Resistance: According to Glen et al. (2007) “Resistance represents the most economically viable approach to controlling P. psidii where it has become established.” In Brazil guava cultivars have been evaluated for resistance, and resistant progeny selected for breeding (Ribeiro and Pommer 2004). Also elite hybrid clones of Eucalyptus grandis and E. grandis x Eucalyptus rophylla are widely used by the cellulose and paper industry in Brazil as E. grandis is highly susceptible to P. psidii (Junghans et al. 2004 in Glen et al. 2007). Selection of resistant species and clones has been a high research priority in Brazil (Xavier et al. 2001 in Glen et al. 2007). A single dominant allele conferring rust resistance has been identified and mapped in E. grandis (Junghans 2000; Junghans et al. 2003 in Tommerup et al. 2003), which will further assist selection of resistant offspring.