New data on introduction pathways: handicrafts & aquarium decorations

photo by Gabriella sellart via Wikimedia

One of the pathways is wooden handicrafts – identified as a pathway more than a decade ago but only partially regulated. The other is new: wood used to decorate aquaria. Two new papers demonstrate that both carry multiple and diverse taxa of fungi. At least 30 have never been detected before in the US. They include both plant and human pathogens.  

Both sets of authors call on the U.S. Department of Agriculture to remedy ineffective regulations. However, it appears unlikely that APHIS will be able to do so now, when its budget and staff are being cut. (Lawsuits might restore some of these resources.) Extending APHIS’ authority to regulate organisms that are not plant pests would require Congress to adopt new legislation.

Live Pathogens Imported in Wooden Handicrafts

In 2022, Jason Smith and others (full citation at the end of this blog) published an analysis of the viability and diversity of fungi brought to the U.S. in imported wooden handicrafts. They isolated 47 fungal taxa originating from at least seven countries on three continents. All remained viable despite being subjected to various phytosanitary requirements. Fourteen were plant pathogens; 17 were human pathogens; several were producers of mycotoxins. Three taxa have not been reported before in North America: Bipolaris austrostipae, Paecilomyces formosus, and Xylaria badia. All three are plant pathogens. P. formosus is a human pathogen as well.

Three quarters of the taxa have tolerances that would increase their likelihood of surviving standard heat or fumigation treatments.

Smith et al. point out that wood from sources other than China are subject only to general permit requirements outlined here. Only if pests are detected during port inspections are quarantine actions taken.

APHIS has certified more than a thousand Chinese exporters of handicrafts that incorporate wood, straw, or other biological components. APHIS encourages importers to buy products from these businesses. However, importers may choose other sources. In that case, the product must be treated before entry.

However, as Smith et al. point out, regulation and treatments are focused on arthropods. They do not address the risk from disease pathogens. Smith et al. conclude that these regulations are insufficient to protect plants from damage.

A second issue is that USDA has no authority to regulate organisms that pose a risk to non-plant hosts, including humans. This is especially worrying in this case because many of the handicrafts being intended for food preparation and distribution. Others are handled by purchasers during crafting activities, or used in bath and beauty products.

photo by Sean Welton via Flickr

Live Fungi Imported in Decorative Wood for Aquaria

A second study has expanded the types of material raising concern. The Minnesota Invasive Terrestrial Plant and Pests Center sponsored research that confirms that pieces of wood imported to decorate aquatic and terrestrial aquaria support live fungal-like organisms. The scientists worry that the wood – and the organisms it harbors – might be discarded in a way that facilitates escape and establishment of these organisms. Another possible route of escape is if the water from these mini-habitats is dumped into surface waters.

Blanchette, Rajtar, Lochridge and Held (2025; full citation at end of this blog) obtained 44 samples of such wood from on-line sellers. Some samples had evidence of fungal infestation. Many of the wood pieces were extensively degraded, with large holes, some of which held mud or sand.

The scientists isolated 202 cultures representing 123 fungal taxa in the Ascomycota, Basidiomycota, and Mucoromycota. They detected no Oomycota. The organisms included 30 or 31 species that have not previously been reported in the United States. Twenty-one species are potential plant pathogens, 37 species are wood decay fungi. Twenty-four taxa appear to be previously unknown.

The origins of the wood pieces have not been revealed by the sellers. The scientists believe wood might have come from China, Vietnam, Thailand, and possibly other Asian countries.

Blanchette et al. note that many fungal-like pathogens that have caused devastating diseases in North American forests came from Asia, although not all were introduced directly from there. They name as examples chestnut blight, white pine blister rust, Dutch elm disease, Port-Orford cedar root disease, sudden oak death, and laurel wilt. [Brief descriptions of all these diseases can be found here.] These past introductions occurred via transport of soil, timber, wood products, living trees, or other plant material.

Blanchette et al. cite Smith et al. regarding detection of novel fungal pathogens of both plants and people on imported wooden handicrafts. They cite Brasier, Jung, and others for the likely Asian origins of many Phytophthora species (see citations at the end of this blog). They note the risk associated with the many undescribed species found in that region. In agreement with many others, Blanchette et al. suggest that fungal pathogens pose a very high risk for the U.S. due to rapid emergence of new diseases, low resistance in host populations, and limited surveillance infrastructure for detection.

The Blanchette et al. study was prompted by detection of Xylaria apoda growing on wood submerged in aquariums located in two states which are quite far from each other – Minnesota and Colorado. Despite the pieces of wood having been dried, shipped and stored for a long period during the import process, the fungus remained viable and was producing fruiting bodies. In total, they isolated eight species as known pathogens of agricultural crops and trees. They also report other fungi that might have potential to be plant or human pathogens. Blanchette et al. express specific concerns about possible impacts of the saprophytic taxa on ecosystem functions. That is, wood decay communities could be adversely affected by changes to biomass degradation and native wood-inhabiting insects.

fungus illustrating web summary of Blanchette et al. https://plpa.cfans.umn.edu/news/underwater-xylaria25

Blanchette et al. point out that their detections came from 44 samples, which represent a very small fraction of the wood being imported for these purposes. Nevertheless the researchers detected impressive quantities and diversity of viable fungi.

Although they did not isolate any Oomycota species, Blanchette et al. say the presence of mud and soil indicates this type of wood could be a pathway for introduction of various exotic Phytophthora – which reside in aquatic and wet soil environments. They call for additional sampling and investigation using more selective methods of isolating Phytophthora species to determine if this could be a successful avenue for importing species of plant pathogenic Oomycota.

Blanchette et al. recommend that people who purchase wood for aquaria repeatedly soak and rinse the wood in water before putting it into an aquarium. This helps eliminate some of the heartwood extractives from the tropical woods and reduces water discoloration in aquariums, as well as possible toxicity to fish and plants. They warn that disposal of the water in contact with this wood into waterways or outdoors could easily release fungal species or Phytophthora spp. that might be in the wood.

Blanchette et al. say their results support earlier indications that current regulations to prevent the importation of non-native fungi on decorative woods used in aquariums are ineffective. In this investigation alone, they cultured more than 100 different live taxa that survived any fumigation or sterilization treatment. They note that scientists have repeatedly called for stronger phytosanitary regulations on imported wood.

One important step they suggest is increasing biosurveillance at the global level. They also suggest prohibiting importation of fungi and fungal-like organisms via this pathway before they become serious problems in their new environment. I concur with these suggestions – with the caveat that while the importation ban is in effect, APHIS and other agencies with authority over invasive species threats to non-plant resources should assess the risks and identify what steps each should take to address them.

[For the history of earlier critiques of weak regulation of imported wood, see blogs on this site under the category “wood packaging” and Fading Forest reports Two and Three (links at the end of this blog). For my critique of regulation of pathogens, see here or contact me.

SOURCES

Blanchette, R.A., Rajtar, N.N., Lochridge, A.G. et al. 2025. Intercontinental movement of exotic fungi on decorative wood used in aquatic and terrestrial aquariums. Scientific Reports 15, 9142. https://doi.org/10.1038/s41598-025-94540-x

Smith, J.A., T. Quesada, G. Alake, N. Anger. 2022. Transcontinental Dispersal of Nonendemic Fungal Pathogens through Wooden Handicraft Imports. mBio July/August 2022 Volume 13 Issue 4 10.1128/mbio.01075-22

Background sources

Brasier, C. M. 2008. The biosecurity threat to the UK & global environment from international trade in plants. Plant Pathol. 57, 792–808.

Brasier, C. M., Vettraino, A. M., Chang, T. T. & Vannini, A. 2010. Phytophthora lateralis discovered in an old growth Chamaecyparis forest in Taiwan. Plant. Pathol. 59, 595–603.

Jung, T., B. Scanu, C.M. Brasier, J. Webber, et al. 2020. A survey in natural forest ecosystems of Vietnam reveals high diversity of both new & described Phytophthora taxa including P. ramorum. Forests 11, 93.

Jung, T., Horta Jung, M.; Webber, J.F. et al. 2021. The destructive tree pathogen Phytophthora ramorum originates from the Laurosilva forests of East Asia. J. Fungi 7, 226.

Jung, T., Milenković I, Balci Y,  et al. 2024 Worldwide forest surveys reveal forty-three new spp in Phytophthora major clade 2 with fundamental implications for the evolution & biogeography of the genus & global plant biosecurity. Stud. Mycol. 107, 251-388.

Roy, B. A. et al. 2014. Increasing forest loss worldwide from IAS pests requires new trade regulations. Front. Ecol. Environ. 12, 457–465.

Wingfield, M. J., Brockerhoff, E. G., Wingfield, B. D. & Slippers, B. 2015. Planted forest health: The need for a global strategy. Science 349, 832–836.

Posted by Faith Campbell

We welcome comments that supplement or correct factual information, suggest new approaches, or promote thoughtful consideration. We post comments that disagree with us — but not those we judge to be not civil or inflammatory.

For a detailed discussion of the policies and practices that have allowed these pests to enter and spread – and that do not promote effective restoration strategies – review the Fading Forests report at  https://treeimprovement.tennessee.edu/

or

www.fadingforests.org

Shothole borer & associated fungus – demonstrating threat in South Africa & possibly beyond

Erythrina caffra one of the native tree species in South Africa killed by PSHB. photo by Coana/Riti via Flickr

Introductions of bark and ambrosia beetles (Coleoptera: Curculionidae, Scolytinae) have significantly increased over the past century. Surveys conducted at borders and ports of entry around the world have shown the majority of beetles intercepted were scolytines. These insects are highly destructive on their own. Also, they can carry pathogenic fungal symbionts that can have devastating effects on the trees they attack.

One or more species in a complex in the Euwallacea genus have become established in countries around the world.  One of these, the polyphagous shot hole borer (Euwallacea fornicatus; PSHB) and its associated fungus (renamed from Fusarium euwallaceae to Neocosmospora euwallaceae) is threatening havoc in South Africa about a decade after its establishment (Townsend, Hill, Hurley, and Roets. 2025).

Over this brief period PSHB/Fusarium disease has spread from two introduction sites – Pietermaritzburg, in KwaZulu-Natal Province, and Cape Town, in Western Cape Province – to all but one of the country’s nine provinces. It has become established in four of five forest types studied – Afrotemperate, coastal, sand, and swamp forests. It has not established in mangrove forests. (The Western Cape Province is home to its own “floral kingdom”. The kingdom’s charactersitic fynbos flora is a heathland habitat, not a forest one.)

Townsend and colleagues established a network of 78 monitoring plots in the Western Cape and KwaZulu-Natal provinces. The sites reflected a variety of natural and human impacts.

tree infested by PSHB/Fusarium disease in KwaZulu-Natal Botanical Garden, Pietermaritzburg. Photo from website of Greenpop.org

By monitoring these plots over five years (2019 – 2024), Townsend and colleagues have demonstrated that the beetle/fungus complex and resulting “Fusarium disease” is spreading and intensifying. The number of infected trees rose from 100 to 176 over the five years – a mean increase of 0.6% per year. The number of PSHB entry holes increased by over 10% annually. The number of plots containing infected trees roughly doubled from 23 in 2019 (29% of the 78 plots) to 48 (60%) in 2023.

By the end of the study, 29% of the 148 species sampled had been infected. This represented 43 species and 7 unidentified trees infected. Trees of eight native species died, , although one — Diospyros glabra (Ebenaceae) – resprouted after the main bole died.

In addition to the eight species known to suffer mortality, another 18 species were found to be able to support PSHB reproduction. Townsend and colleagues worry that, as the infestation spreads and intensifies, some of these species might also succumb. They mention specifically Erythrina caffra (coral tree), which is prevalent in coastal forest ecosystems across South Africa.

Most of the hosts are in the same families as those identified earlier by Lynch et al. (2021), e.g., Ebenaceae, Fagaceae, Fabaceae, Malvaceae, Podocarpaceae, Rutaceae, Sapindaceae and Stilbaceae.

Disease progress, speed of death, and visibility of symptoms varied not only between species, but sometimes among individuals of the same species. Some trees died rapidly. Townsend and colleagues say it is impossible to predict which individuals will succumb to infection.

There is, though, a clear frequency-dependent relationship between trees and beetles. Sites with higher relative abundance of host trees also had a higher proportion of infected trees, on average. The number of PSHB holes per species and per plot both increased to a larger extent at these same sites.

Individual trees’ traits influenced the severity of infestations (measured by the number of PSHB entry holes). Larger trees, those with a less healthy canopy, and those farther from a water source suffered more attacks. (This last finding differs from others’; Townsend et al. speculate that in the absence of flood-stressed trees, drought-stressed trees might be more attractive to ambrosia beetles.)

native tree in Tsitsikama National Park; photo by F.T. Campbell

Characteristics of the monitoring plots also affected disease progression. Higher proportions of trees became infected when they grew in plots that were closer to source populations, or that contained a higher proportion of host species as distinct from non-host species. The proportion of trees infected decreased in plots with higher tree densities or tree species richness.

As of 2023, “Fusarium disease” is more widespread and intense in KwaZulu-Natal than in the Western Cape. In KwaZulu-Natal 0.11% of monitored trees are infected compared to 0.06% in the Western Cape. The number of infected trees rose twice as fast over the five years in KwaZulu-Natal – ~6%, than in Western Cape – 3%. While all KwaZulu-Natal plots contained infected trees, three of 11 monitoring sites in the Western Cape did not. Townsend and colleagues believe that the most likely explanation is that PSHB arrived in KwaZulu-Natal earlier (as far back as 2012 as opposed to 2017 in Western Cape). Another possible factor is that source populations of infected trees are indigenous trees within the forest in KwaZulu-Natal whereas, in the Western Cape, they are often non-native trees planted in urban areas far from the study plots. Also, forests in KwaZulu-Natal are fragmented while, in Western Cape, the study forests are nearly contiguous. Townsend et al. conclude that the disease will spread and intensify in Western Cape as additional source populations become established in the forest.

locations of PHSB/Fusarium disease in Cape Town, South Africa – West of the study sites; map from City of Cape Town

As of 2023, the proportion of trees infected appears to be small — 7.6% of the 2,313 trees monitored. Only 11 trees in the monitored plots have died. However, the longer PSHB is active in the environment the more trees it will infest, the higher its impact will be on hosts, and the higher the number of dispersing individuals produced. This will substantially increase the chances and rates of additional areas becoming infected, especially in areas close to infestations – e.g., cities. They fear that in the future impacts will increase as progressively more competent host individuals are infected. Therefore, they emphasize the importance of mitigating PSHB increase in natural ecosystems, even in already infected areas.

Townsend and colleagues urge phytosanitary officials and resource managers to prioritize surveillance and management on the families containing several host species (above) and within plant communities in which they predominate. Managers must also be alert to new reproductive hosts for the beetle that appear as the infestation spreads and intensifies.

The situation could be worse than described; the Townsend et al. study did not examine how the invasion might affect eco-regions outside these two provinces. Because the PSHB has such a broad host range, hosts can die quickly, and South Africa provides ideal climatic conditions, this bioinvader could cause severe ecological effects on most indigenous forest types as well as agriculture and urban trees throughout Africa.

SOURCES

Lynch, S.C., A. Escalen, and G.S. Gilbert. 2021. Host evolutionary relationships explain tree mortality caused by a generalist pest-pathogen complex. Evol Appl 14:1083 – 1094. https://doi.org/10.1111/eva.13182

Townsend, G., M. Hill, B.P. Hurley, and F. Roets 2025. Escalating threat: increasing impact of the polyphagous shot hole borer beetle, Euwallacea fornicatus, in nearly all major South African forest types. Biol Invasions (2025) 27:88 https://doi.org/10.1007/s10530-025-03551-2  

Posted by Faith Campbell

We welcome comments that supplement or correct factual information, suggest new approaches, or promote thoughtful consideration. We post comments that disagree with us — but not those we judge to be not civil or inflammatory.

For a detailed discussion of the policies and practices that have allowed these pests to enter and spread – and that do not promote effective restoration strategies – review the Fading Forests report at  https://treeimprovement.tennessee.edu/

or

www.fadingforests.org