The first symptoms of the disease in C. lawsoniana involve gradual colour changes in the foliage: to yellow, bronze and finally a light brown to tan colour as the foliage dries out. In cool, damp weather this colour change sequence may take two to three months, whereas in hot and dry weather it may only take two to three weeks (Tucker & Milbraith, 1942). These symptoms are uniform throughout the tree if the infection begins in the roots, but localized on individual branches in the case of aerial infection (Erwin & Ribeiro, 1996). The pathogen generally invades the roots, killing tissues as it advances, and causing a brown and water-soaked appearance. The infection eventually spreads to the root crown of the tree and causes girdling of the trunk and ensuing foliar changes described (Tucker & Milbraith, 1942). Removal of the outer bark from the infected root collar shows a sharp line of demarcation between the white healthy tissue and the dark brown dead tissue; a black resinous line can sometimes be seen on the cambium (Tucker & Milbraith, 1942). Eventually plants die; infected seedlings die rapidly but it may take several years for larger trees to die. Pacific yew (Taxus brevifolia) shows similar but less severe symptoms (EPPO, 2009).
Zoospores initiate the infection in the fine roots (Kliejunas, 1994 in EPPO, 2009). The mycelium then spreads throughout the inner bark and cambium of the root system to the root collar. Infection spreads upwards in an irregular triangle. Under favourable conditions, the pathogen may be splashed from soil onto foliage, and produce sporangia on the foliage. These sporangia may be dispersed by wind and rain, and aerial spread is possible (Trione & Roth, 1957; Trione, 1959 in EPPO, 2009). P. lateralis also forms chlamydospores, thick walled resting spores, which persist in the soil and in leaf or root debris, allowing long-term survival and overland movement of the pathogen (EPPO, 2009). P. lateralis, which is homothallic, sometimes also produces oospores, which are similarly hardy and can survive long distance travel (Kauffmann & Jules, 2006).\r\n\r\n
P. lateralis can survive and remain infectious in absence of living host tissue for at least 7 years in a range of natural environments (Hansen & Hamm, 1997).
Artificial infection has also been achieved in inoculation experiments with Rhododendron species (Hoitink & Schmitthenner, 1974 in EPP0, 2009), Pseudotsuga menziesii (Pratt et al., 1976 in EPPO, 2009) and Chamaecyparis nootkatensis (Kliejunas, 1994 in EPP0, 2009). This suggests that P. lateralis may be carried latently by some plants which hare not natural hosts (EPPO, 2009).
There are a number of published reports of this oomycete infecting other species. However reports on hosts other than cedars (Chamaecyparis spp.) and T. brevifolia are considered to be misidentifications of other Phytophthora spp. (CSL, 2006; EPPO, 2009).
Infection can occur at temperatures of 3-25 °C, but temperatures of 15-20 °C are optimal. Growth is restricted at 25 °C and inhibited entirely at 30 °C (Sinclair et al., 1987 in EPPO, 2009; Tucker & Milbraith, 1942).
Principal source: European and Mediterranean Plant Protection Organization (EPPO) 2009. Phytophthora lateralis. Bulletin OEPP. 39(1). APR 2009. 43-47.
Compiler: National Biological Information Infrastructure (NBII) & IUCN/SSC Invasive Species Specialist Group (ISSG)
Review: Everett M. Hansen, Professor, Emeritus, University of Wisconsin, Madison
Publication date: 2011-02-23
Recommended citation: Global Invasive Species Database (2024) Species profile: Phytophthora lateralis. Downloaded from http://iucngisd.org/gisd/species.php?sc=564 on 19-08-2024.
Port Orford-cedar has been drastically reduced or eliminated from large portions of riparian environments and wetlands by P. lateralis. Reduction of this important tree can have catastrophic impacts on streamside plant communities and aquatic ecology. Particularly on ultramafic soils, where Port Orford-cedar may be the only tree species able to grow, consequences to stand structure can be particularly pronounced (Hansen & Hamm, 1997; Hansen, 1999; Hansen et al., 2000). Loss of old-growth stands of Port Orford-cedar can have negative impact on wildlife species that require old-growth characteristics (Hansen et al., 2000). Additionally, the size and age class of cedar has shifted as a result of the disease and forest harvest, with large old trees being replaced by smaller, young trees (Hansen et al., 2000).\r\n
While Pacific yew is also an important forest species, providing food and cover for wildlife and shade and stability for streams, it is less susceptible to P. lateralis and mortality is low (Hansen et al., 2000).\r\n\r\n
Economic: Port Orford-cedar or Lawson’s cypress is grown as an ornamental tree in Europe and the Pacific Northwest. Since the incursion of P. lateralis the multi-million dollar ornamental nursery production in Washington and Oregon has largely been destroyed (Hansen & Hamm, 1997; Hansen et al., 2000). Port Orford-cedar trees in parks in British Columbia experience significant annual losses due to P. lateralis with a high cost of replacement (Utkhede et al., 1997). \r\n
Port Orford-cedar has been one of the most valuable commercial timbers in the world, with a value on the export market of up to ten times that of Douglas-fir (Pseudotsuga menziesii) (Hansen et al., 2000). \r\n\r\n\r\n
Pacific yew is less susceptible to P. lateralis, and the pathogen is likely to have only limited impact on this tree. Unusual morality of Pacific yew has only been observed in areas where it grows in close proximity to Port Orford-cedar (Murray & Hansen, 1997).\r\n\r\n
Other: Social impacts include loss of business in nursery and forestry sectors, and effects on tourism and fishing due to forest closures (Hansen et al., 2000).
Preventative: The US Forest Service has established permanent and wet season road closures in areas with Port Orford-cedar. These closures are an important tool to stop the spread of P. lateralis, as transportation via roads has been identified as the primary method of spread. Other preventative methods include confining harvesting, road maintenance and other activities to the summer dry season; sanitation of vehicles and equipment before they reach uninfested areas; altering and diverting roads away from cedar areas; growing cedar on sites unfavourable for disease spread (Hansen et al. 2000; Hansen & Hamm, 1997; Jules et al., 2002).
In nurseries preventative measures include soil sterilisation, use of fungicides registered for use against Phytophthora root rots, disinfection of materials and preventing the introduction or movement of infested soil (EPPO, 2009).\r\n
Cultural: Methods that have been suggested to reduce P. lateralis infection include growing disease-free stock in uninfected soil, avoiding monocultures of Port Orford-cedar in windbreaks or hedges and ensuring adequate drainage (Utkhede et al., 1997). However the most commonly suggested and employed technique is the reduction of cedar density, especially in infected sites near roads (Goheen, 2000 in Jules et al., 2002). \r\n\r\n
Genetic resistance:\r\nFollowing observations of healthy trees in the midst of dead neighbours led Hansen et al. (1989) to demonstrate that heritable resistance to P. lateralis occurs in Port Orford-cedar. Since then a resistance breeding programme for Port Orford-cedar has been underway with the goal of providing resistant seedlings for forest regeneration.The programme has produced promising results and first generation resistant seedlings are now available (Oh et al., 2006; Sniezko, 2003; Sniezko, 2006). Resistance to P. lateralis offers the best chance of re-establishing Port Orford-cedar in areas where the pathogen is established and is important in long-term disease management. However, genetic resistance offers no protection for surviving stands of the cedar, and it will be hundreds of years before the resistant seedlings can replace the large old trees (Hansen et al., 2000). \r\n\r\n
Biological: Treating Port Orford-cedar with drench applications of the bacteria Enterobacter aerogenes (Strain B8) has shown some success. Diseased trees treated over four years in Vancouver, British Columbia had lower disease ratings and higher growth rates than water-treated controls (Utkhede et al., 1997). However this, or any other biological control method, have not been used in practice (EPPO, 2009).