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Status of the Spotted Lanternfly – Threatening Crops & – Possibly – Forest Trees

spotted lanternfly; photo by Holly Raguza, PA Department of Agriculture

Environmental Entomology, in partnership with other journals from the Entomological Society of America, has published a special collection of papers on the spotted lanternfly, Lycorma delicatula. All papers in the collection are freely available to read and download through February 16, 2022. I will summarize key points, with brief references to the specific article.

The papers are available at https://academic.oup.com/ee/pages/research-on-spotted-lanternfly

Areas at Risk

As this map shows, the spotted lanternfly (SLF) is thought able to establish in more than 26 states.

Source: T.T Wakie et al., 2020. The Establishment Risk of Lycorma delicatula (Hemiptera: Fulgoridae) in the United States and Globally. Journal of Economic Entomology, Volume 113, Issue 1, February 2020, Pages 306-314, https://doi.org/10.1093/jee/toz259

Host Trees

SLF prefers the invasive tree species, Tree of Heaven (Ailanthus altissima), especially for oviposition. Ailanthus is widespread, so this is not very limiting. However, the SLF can complete its life cycle in the absence of this host. [O. Uyi et al. 2020. Spotted Lanternfly (Hemiptera: Fulgoridae) Can Complete Development and Reproduce Without Access to the Preferred Host, Ailanthus altissima. Environmental Entomology, Volume 49, Issue 5, October 2020, Pages 1185–1190, https://doi.org/10.1093/ee/nvaa083]

Spotted lanternflies have been recorded as feeding on at least 56 plant species in North America and 103 plant species worldwide; most are shrubs, trees, or stout vines. [L. Barringer and C.M. Ciafré. 2020. Worldwide Feeding Host Plants of Spotted Lanternfly, With Significant Additions From North America. Environmental Entomology, Volume 49, Issue 5, October 2020, Pages 999–1011, https://doi.org/10.1093/ee/nvaa093]

SLF aggregates on tree-of-heaven by its adult stage. However, egg masses are found on 24 types of substrates with tree-of-heaven, black cherry, black birch, and sweet cherry. [H. Liu. 2019. Oviposition Substrate Selection, Egg Mass Characteristics, Host Preference, and Life History of the Spotted Lanternfly (Hemiptera: Fulgoridae) in North America. Environmental Entomology, Volume 48, Issue 6, December 2019, Pages 1452–1468, https://doi.org/10.1093/ee/nvz123]

An evaluation of spotted lanternfly survivorship on 26 host plant species in 17 families found that eight species supported development from first instar to adult: black walnut, chinaberry, oriental bittersweet, tree-of-heaven, hops, sawtooth oak, butternut, and tulip tree. When offered a choice between black walnut and tree-of-heaven, nymphs showed no preference; adults showed a significant preference for tree-of-heaven. [K. Murman et al. 2020. Distribution, Survival, and Development of Spotted Lanternfly on Host Plants Found in North America. Environmental Entomology, Volume 49, Issue 6, December 2020, Pages 1270–1281, https://doi.org/10.1093/ee/nvaa126]

Dispersal

Spotted lanternfly nymphs (all instars) usually moved only short distances over a 7-day period, but a few were discovered 50-65 meters away. [J.A. Keller et al. 2020. Dispersal of Lycorma delicatula (Hemiptera: Fulgoridae) Nymphs Through Contiguous, Deciduous Forest. Environmental Entomology, Volume 49, Issue 5, October 2020, Pages 1012–1018, https://doi.org/10.1093/ee/nvaa089]

Detection – Traps & Lures

A test of 43 host plant volatiles found 11 to be significantly attractive. [N.T. Derstine et al. 2020. Plant Volatiles Help Mediate Host Plant Selection and Attraction of the Spotted Lanternfly (Hemiptera: Fulgoridae): a Generalist With a Preferred Host. Environmental Entomology, Volume 49, Issue 5, October 2020, Pages 1049–1062, https://doi.org/10.1093/ee/nvaa080]

A comparison of several trap types found that circle traps caught more SLF than sticky bands, and fewer non-target organisms. Traps placed on the trunks of trees caught more SLF than traps placed in the tree canopy. [J.A. Francese, et al. 2020. Developing Traps for the Spotted Lanternfly, Lycorma delicatula (Hemiptera: Fulgoridae). Environmental Entomology, Volume 49, Issue 2, April 2020, Pages 269–276, https://doi.org/10.1093/ee/nvz166] In one study, addition of a lure containing methyl salicylate did not increase captures. [L.J. Nixon, et al. 2020. Development of Behaviorally Based Monitoring and Biosurveillance Tools for the Invasive Spotted Lanternfly (Hemiptera: Fulgoridae). Environmental Entomology, Volume 49, Issue 5, October 2020, Pages 1117–1126, https://doi.org/10.1093/ee/nvaa084] his contradicted an earlier study that suggested that traps with high release methyl salicylate lures did capture more SLF. [M.F. Cooperband, et al. 2019. Discovery of Three Kairomones in Relation to Trap and Lure Development for Spotted Lanternfly (Hemiptera: Fulgoridae). Journal of Economic Entomology, Volume 112, Issue 2, April 2019, Pages 671–682, https://doi.org/10.1093/jee/toy412]

Potential Controls: Parasites, Parasitoids, and a Pathogen

Significant efforts are afoot to find possible biocontrol agents. Scientists have surveyed SLF and associated parasites/parasitoids across 27 provinces and administrative regions of China from 2015 to 2019. They recovered an egg parasitoid, Anastatus orientalis, and a nymphal parasitoid, Dryinus sinicus, and are studying these further as potential biological control agents of spotted lanternfly. [B. Xin et al. 2020. Exploratory Survey of Spotted Lanternfly (Hemiptera: Fulgoridae) and Its Natural Enemies in China Environmental Entomology, nvaa137, https://doi.org/10.1093/ee/nvaa137]

The egg parasitoid Anastatus orientalis has the advantages of being easy to rear and long lived. Research is under way to tests its host specificity. [H.J. Broadley et al. 2020. Life History and Rearing of Anastatus orientalis (Hymenoptera: Eupelmidae), an Egg Parasitoid of the Spotted Lanternfly (Hemiptera: Fulgoridae). Environmental Entomology, nvaa124, https://doi.org/10.1093/ee/nvaa124]

The spotted lanternfly leaves behind a chemical trail when walking – a trail which the parasitoid wasp Anastatus orientalis uses to locate the host’s eggs. [R. Malek et al. 2019. Footprints and Ootheca of Lycorma delicatula Influence Host-Searching and -Acceptance of the Egg-Parasitoid Anastatus orientalis [Environmental Entomology, Volume 48, Issue 6, December 2019, Pages 1270–1276, https://doi.org/10.1093/ee/nvz110]

The established gypsy moth egg parasitoid Ooencyrtus kuvanae has been observed attacking SLF egg masses in the field. [H. Liu and J. Mottern. 2017. An Old Remedy for a New Problem? Identification of Ooencyrtus kuvanae (Hymenoptera: Encyrtidae), an Egg Parasitoid of Lycorma delicatula (Hemiptera: Fulgoridae) in North America. Journal of Insect Science, Volume 17, Issue 1, January 2017, 18, https://doi.org/10.1093/jisesa/iew114]

Single applications of the insect pathogenic fungus Beauveria bassiana strain GHA killed 43-48% of spotted lanternflies on preferred host plants in a park. Adult spotted lanternflies feeding on potted grapevines were sprayed with the same fungus, resulting in 100% mortality after 9 days. [E.H. Clifton, et al. 2020. Applications of Beauveria bassiana (Hypocreales: Cordycipitaceae) to Control Populations of Spotted Lanternfly (Hemiptera: Fulgoridae), in Semi-Natural Landscapes and on Grapevines Environmental Entomology, Volume 49, Issue 4, August 2020, Pages 854 – 864, https://doi.org/10.1093/ee/nvaa064]

Ambrosia Beetles: Not All the Same (laurel wilt v. shot hole borers)

Horton House on Jekyll Island, Georgia – when the redbays were still alive!
photo by Faith Campbell

A recent USFS book on invasive species reports that at least 58 species of bark and ambrosia beetles have been established in the US. Recent studies highlight very different situations due to two invasive ambrosia beetles. Here are summaries of each.

1. Laurel Wilt: Unmitigated Disaster in Atlantic and Gulf Coastal Plains – and Possibly More Widely

The disease laurel wilt, caused by the pathogen Raffaelea lauricola and vectored primarily by the redbay ambrosia beetle (Xyleborus glabratus) presents a dire contrast. (For this section, see Olatinwo, Fraedrich & Mayfield. 2021; full reference at end of the blog.) In the nearly 20 years since its first detection near Savannah, Georgia in 2002, laurel wilt has spread across more than 100 counties and parishes in 11 states from North Carolina south through Florida, west to eastern Texas, and as far northward as Kentucky.

Laurel wilt has killed hundreds of millions of trees in the plant family Lauraceae. Approximately 13 Lauraceae species in eight genera (depending on taxonomic proclivities!) are indigenous to the U.S. Individual species’ vulnerability appears to depend largely on size; the beetle is attracted to vertical stems of a certain diameter. As a result, the native tree species redbay (Persea borbonia), swampbay (Persea borbonia var. pubescens or P. palustris), and more recently sassafras (Sassafras albidum) have experienced the most damaging attacks. Also heavily attacked has been the commercial avocado (Persea americana) which is native to Central America.

While redbay is widespread in a defined geographic area – a long the Atlantic and Gulf Coastal Plain from North Carolina to Texas, sassafras is subcontinental: it is found in 28 states, 53 ecoregions, and 69 forest types. Approximately 80% of sassafras in affected areas have been killed. In recent years, spread has proceeded by many “jumps” to disjunct areas where sassafras occurs in isolation from other hosts. At present, approximately 52% of the range of sassafras might experience winter temperatures sufficiently cold to cause significant mortality of the redbay ambrosia beetle. However, this temperature protection is likely to decline to about10% of sassafras’ range as a result of even modest climate change (a 1.4 °C increase in winter minimum temperatures).

The ecological impact of loss of redbay and sassafrass are not clear. Both are sources of wildlife food. The principal specialist on redbay is the Palamedes swallowtail butterfly (Papilio palamedes), which is also the primary pollinator of a rare plant, yellow-fringed orchid. The rapid loss of swampbay on tree islands in the Everglades could facilitate establishment of even more individuals of the already widespread invasive plant species Brazilian pepper (Schinus terebinthifolius) or Melaleuca quinquenervia.

Other U.S. native plant species in the Lauracea family are apparently partially protected by the small diameter of their stems, which the beetle doesn’t find acceptable. These include – in the Southeast — the federally listed pondberry (Lindera melissifolia), “species of interest” pondspice (Litsea aestivalis), bog spicebush (Lindera subcoriacea), pepperleaf sweetwood (Licaria trianda), lancewood (Ocotea coriacea), and love-vine (Cassytha filiformis). The common shrub spicebush (Lindera benzoin) might be protected by its possession oflower quantities of the primary host volatile attractant. On the other hand, the widespread Pacific state shrub California laurel or Oregon myrtle (Umbellularia californica) is considered highly vulnerable, should laurel wilt be moved there in wood, mulch, or nursery plants.

Laurel wilt poses an unknown threat to the many plant species in the Lauraceae in Central and South America (750 species), Australia (125 species), Madagascar (135 species), and the Macaronesian Islands off the coasts of Europe and Africa – the Azores, Canary Islands, and Madeira. The commercial spice bay laurel (Laurus nobilis) is native to the Mediterranean region (and planted elsewhere, including in the US). However, its small size, discontinuous distribution and isolation from other lauraceous host species might prevent development of a widespread epidemic.

The authors note the absence of effective measures to manage laurel wilt 20 years after its detection. They recommend restricting long-distance movement of infested wood, associated public awareness efforts, development and deployment of resistant hosts, silviculture (sanitation), targeted application of preventive chemical treatments for protecting high-value trees, and severing root grafts in avocado orchards and sassafras clones. They note that success will be dependent on sustained funding and a commitment to long-term area-wide implementation.

[As I noted in past blogs about APHIS deregulating the emerald ash borer, it is now up to the states to regulate movement of firewood. The lead will continue to be the non-governmental “Don‘t Move Firewood” campaign. The message will continue to encourage the public to buy firewood where they burn it and to refrain from moving firewood from areas that are under Federal quarantine for other pests of firewood (e.g., Asian longhorned beetle). This campaign and the new National Plant Board guidelines stress that firewood is a high-risk pathway for many pests of national or regional concern; they do not focus on any particular species. Leigh Greenwood, director of Don’t Move Firewood, thinks this is a good approach.]

Mayfield adds that the spread northwards on sassafras means that state diagnostic pathology labs should familiarize themselves with protocols for isolating the laurel wilt pathogen.

As to developing resistant varieties of redbay, I note that Potter et al. 2019 ranked redbay as fifth species highest in priority for genetic conservation and restoration breeding efforts. However, it is my impression that few federal resources have been allocated to such an effort on behalf of redbay.

2. Ambrosia beetles in California

At least 22 of the recently-established ambrosia and bark beetles are in California. Heavily urbanized southern California appears to be particularly vulnerable to such introductions. The proximity of ship traffic and associated cargo, as well as the great diversity of potential hosts in the area’s urban forests, are likely to blame.

Two such pests are the polyphagous (PSHB) and Kuroshio (KSHB) shot hole borers [collectively, invasive shot hole borers (ISHB)]. John Boland has studied the KSHB outbreak in the Tijuana River estuary intensively since 2015. Two recent studies – 2019 and 2021– demonstrate the importance of ecological and tree-related factors in determining the severity of attack by this ambrosia beetle. See references at the end of the blog.

The most susceptible site is wet and nutrient enriched (in the case of the Tijuana River, due to pollution).

The most susceptible trees are young, fast growing, and have thin bark (allowing KSHB access) and wood of low density and high moisture content (providing ideal conditions for KSHB and associated fungi).

willows killed by KSHB in Tijuana River estuary; photo by John Boland

As Boland has noted, all of these conditions occurred in the “wet” forests close to perpetual streams in the Tijuana River delta in 2015. These factors led to dramatic levels of mortality, which have not been equaled in other southern California deltas. In the five years from 2015 to 2020, the beetle/fungus complex infested an estimate 350,000 willows and killed an estimated 123,000 in a boom-and-bust cycle. Since 2016, the trees in the Tijuana River estuary have regrown to almost pre-infestation dimensions. (Boland is not certain why these new, fast-growing trees have not been attacked by the KSHB that remain in the area. He suggests that a local pathogen, parasite, parasitoid or predator is keeping the KSHB in check – although this has not been verified.)

Willows near the main river channel (“Wet Forest” units) cumulatively had a fatality rate of 39%. Strikingly, more distant “Dry Forest” units had a combined fatality rate of only 9%.

The 2019 study linked the higher rates of infestation, damage, and mortality that occurred in trees near the main river channel to the presence of year-round water that was often enriched by a heavy load of sewage. The trees respond by growing rapidly, resulting in thinner bark and less dense wood. The KSHB attacked in much higher numbers, impeding water transport and weakening the trees’ structure so that they were more easily broken during windstorms.

The 2021 study provided further detail. By comparing bark samples cut from 27 infested trees at the height of the infestation, in 2016 – 17, Boland and Woodward demonstrated thicker bark on the “Dry Forest” trees protected the trees by limiting the density of KSHB entry points. The fewer holes reduced internal structural damage to the trees, which allowed them to survive. Boland notes that the protection might arise from either the bark thickness itself, or higher quantities of protective chemicals.

Repercussions

The results suggest that a KSHB individual actively searches for a suitable tree and then searches for the thinnest bark on that tree in which to drill its hole.
Trees can recover from KSHB attack, indicating that the fungal symbionts are only moderately pathogenic at worst.
The ISHB are likely to cause much less damage than indicated by the one early model developed before these factors were understood. We need new models for ISHB spread and impact that incorporate these factors of site characteristics and host tree condition.

SOURCES

Boland, J.M. 2019. The Ecology and Management of the Kuroshio Shot Hole Borer in the Tijuana River Valley Final Report. (Year 5) https://trnerr.org/wp-content/uploads/2020/05/KSHB-TRValley2020.pdf

Boland J.M. and D.L. Woodward. 2021. Thick bark can protect trees from a severe ambrosia beetle attack. PeerJ 9:e10755 https://peerj.com/articles/10755/

[all of Boland’s reports and articles on the KSHB are available at: The Ecology and Management of the Kuroshio Shot Hole Borer in the Tijuana River Valley — Tijuana Estuary : TRNERR]

Olatinwo, R.O., S.W. Fraedrich & A.E. Mayfield III. 2021. Forests 2021, 12, 181. Laurel Wilt: Current and Potential Impacts and Possibilities for Prevention and Management

Potter, K.M., Escanferla, M.E., Jetton, R.M., Man, G., Crane, B.S. 2019. Prioritizing the conservation needs of US tree spp: Evaluating vulnerability to forest P&P threats, Global Ecology and Conservation (2019), doi: https://doi.org/10.1016/ j.gecco.2019.e00622.

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 http://treeimprovement.utk.edu/FadingForests.htm

Interior’s Invasive Species Plan: Let’s Implement It!

Posted by Scott J. Cameron, former Acting Assistant Secretary for Policy Management and Budget , US Department of the Interior

locations in Hawaii Volcanoes National Park where ohia trees were infected by rapid ohia death pathogen in 2017

In 2019 Congress passed the John D. Dingell, Jr. Conservation, Management, and Recreation Act. Among other things, it directed the Department of the Interior to “develop a strategic plan that will achieve, to the maximum extent practicable, a substantive annual net reduction of invasive species population or infested acreage on land or water managed by the Secretary.” This provision triggered a year-long process of public involvement and inter-bureau coordination. The result was a plan published in January 2021. It represents the first attempt by Interior at a Department-wide multi-taxa, multi-year approach to invasive species. It has the potential to spur integration of invasive species work across the Department’s many bureaus and to focus each bureau’s efforts on a set of common goals, strategies, and performance metrics.

While Congress’ language is open-ended, any planning exercise is constrained by the most recent President’s budget and existing law. It is up to those of us who are not, or at least no longer, executive branch employees to advocate for plans unbound by those constraints.

In that spirit, I offer eight recommendations to improve invasive species management. Four are within existing authorities; four more are outside the current budgetary and statutory framework. Many more ideas are without a doubt worth pursuing.

*Opuntia* (prickly pear) cactus – common plant in western National parks and on Bureau of Land Management lands; under threat by cactus moth

First, within existing funding and legal authorities, the Department has unfinished business that it can act on now.

Secure approval of the package of categorical exclusions under the National Environmental Policy Act (NEPA) — now awaiting approval by the President’s Council on Environmental Quality (CEQ). Over many years agencies have documented how invasive species control improves, rather than harms, the environment. Absent an applicable NEPA categorical exclusion approved by CEQ, though, each such action needs to run the time- and money-consuming gauntlet of NEPA compliance. In the meantime, the invasive plants germinate, the invasive animals reproduce, and what might have been a localized and inexpensive problem has expanded geographically and in terms of cost and complexity. In the Fall of 2020 Interior submitted hundreds of pages of documentation on numerous practices proven to control invasive species without harming the environment. Due to time and staffing constraints at CEQ, these categorical exclusions still await action. Interior and CEQ should take prompt steps to finish them.

Allocate to the US Geological Survey at least $10 million of the roughly $90 million remaining available to the Secretary in CARES Act appropriations for research on invasive zoonotic diseases. These are diseases like COVID-19 and West Nile virus that can move from one species to another. Many zoonotic diseases fit the definition of invasive species, since they are not native to the United States and endanger human health. In the case of COVID-19 funding is available to the Secretary of the Interior, without need for further Congressional action, from funds appropriated by the CARES Act. The availability of these funds will expire at the end of September 2021, so Interior should provide this research funding to USGS as soon as possible.

Join the existing Memorandum of Understanding between the Western Governors Association (WGA) and the US Department of Agriculture’s Forest Service. These groups have established “a framework to allow the U.S. Forest Service (USFS) and WGA to work collaboratively to accomplish mutual goals, further common interests, and effectively respond to the increasing suite of challenges facing western landscapes.” This provides a forum to improve coordination between the States and the federal government on the management of invasive species, and Interior needs to be part of that team.

Interior should work with USDA to accelerate and intensify efforts to systematically improve coordination between the interagency Wildland Fire Leadership Council and the interagency National Invasive Species Council. Both Councils have member agencies that practice vegetation management using similar tools and techniques, although for different purposes. The two Councils should identify a select number of initiatives in FY21 where their efforts would benefit both wildland fire management and invasive plant management .

swamp bay trees in Everglades National Park killed by laurel wilt; photo by Tony Pernas

Four steps to implement the strategic plan outside the scope of current law and the President’s Fiscal Year 2021 budget. I offer the following:

Improve implementation of the Lacey Act program to list injurious species. There are both legislative and administrative elements to this proposal.

In a federal District Court decision on May 19, 2015, on a lawsuit filed by the Association of Reptile Keepers, the Court undid the longstanding Fish and Wildlife Service policy that the Lacey Act allowed FWS to ban interstate transport of injurious species. On April 7, 2017, the D.C. Circuit Court of Appeals upheld the District Court’s view. These rulings mean that FWS authority only applies to international commerce. Unfortunately, the court’s interpretation of the law and legislative history are reasonable, so Congress needs to amend the law to make it clear that FWS is explicitly authorized to regulate interstate commerce in injurious species. The Department of the Interior should work with the Department of Justice and the Office of Management and Budget to develop the necessary bill language and submit it to Congress.

At the same time, the FWS injurious species listing process is notoriously slow, even causing Congress to occasionally list species legislatively. The fact that these legislative initiatives have sometimes been promoted by Members of Congress who normally are opposed to more federal regulation signals just how awkward the current FWS process is. Thus there might well be strong bipartisan support to amend the Lacey Act on the interstate commerce matter. Acting on its own authority, FWS should procure an independent third party review of the injurious species listing process and ask the contractor to make suggestions for “business process reengineering” to improve and streamline current practices, along with evaluating whether higher funding or new technology is needed.

The Bureau of Reclamation, Department of the Interior, and the Office of Management and Budget should develop legislative language to submit to Congress for the 2022 Water Resources Development Act, that explicitly authorizes an aquatic nuisance species program in the Bureau of Reclamation. It could parallel the relatively new authority enjoyed by the Army Corps of Engineers and mandate increased coordination between the two water agencies.

Any climate change legislation pursued by Congress and the Administration should include provisions for addressing invasive species. Climate change will make some North American habitats more suitable for foreign organisms, as cold-intolerant species might be able to survive in more northern latitudes in the U.S. than previously was the case. Second, the disruptive effect of climate change on North American ecosystem structure and trophic relationships at any latitude will make those ecosystems more vulnerable to invasion. Finally, the spread of invasive species may in and of itself exacerbate climate change, such as through the increased carbon dioxide emissions from rangeland wildfires aggravated by the dominance of invasive cheatgrass.

The Senate Committee on Environment and Public Works and the House Natural Resources Committee should each hold oversight hearings on how best to help state and local governments detect and respond to new invasive species that are not within the statutory purview of USDA/APHIS. This is a complex topic, important for both ecological and financial reasons. Over the years several attempts to address it have failed. A thoughtful review by Congress and the Administration, which perhaps would lead to passage of new statutory authority and funding, is worth exploring.

The Author:

Scott Cameron recently left the federal government, where he had served as Acting Assistant Secretary for Policy, Management and Budget at the U.S. Department of the Interior. In that capacity he oversaw Department-wide budget, invasive species, natural resource damage assessment and restoration, environmental compliance and numerous administrative functions of this $14 billion agency with 65,000 employees. Previously, Scott held other civil service job (e.g., at the White House Office of Management and Budget) & political appointments in the federal government, on the staff of the Governor of California, and on Congressional staffs. While not in government, Scott led formation of the Reduce Risk from Invasive Species Coalition.

CISP welcomes 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.

Further information on the plant pests mentioned in the photo captions can be obtained at www.dontmovefirewood.org; click the “invasive species” button.

Invasive Plants in National parks – Progress?

Japanese stiltgrass in Shenandoah National Park; photo by Jake Hughes, NPS

The recent appearance of a study by National Park Service (NPS) scientists quantifying the threat posed by invasive plants prompted me to seek updates on this issue. In May 2018, I blogged about NPS’ Invasive Plant Program Strategic Plan, which was issued in 2016. At the time, I got the impression that the program was struggling to gain support from NPS leadership in Washington, as well as leaders of individual parks. Has the situation improved since then?

The recent study, by Kathryn Miller and colleagues, focuses on National parks in the East, from Virginia to Maine. (I provide a full reference at the end of this blog.) I look forward to a planned follow-up article that will try to clarify drivers of invasion.

The Miller study appears to have been undertaken to partially fulfill one of the goals of the NPS’ 2016 Invasive Plant Program Strategic Plan. One of the actions under Goal 1 in the Plan was to quantify the invasive plant threat, the effort needed to manage it, and then to communicate the gap between needs and available resources. Miller et al. have quantified the threat to National parks in one region (not the entire country). However, they have communicated the gap between effort and need in only the most general way.

Protecting the forests in eastern National parks is valuable from many perspectives. The forests in these parks are older and have higher stand-level tree diversity than surrounding unprotected forests. Protecting their long-term condition also corresponds to the National Park Service’s (NPS) stated mission, as established in its Organic Act.

The study relied on National Park Service Inventory and Monitoring Program data from 1,479 permanent forest plots covering 39 eastern NP units located from Virginia to Maine. The data were collected over 12 years, in three survey cycles (2007–2010, 2011–2014, and 2015–2018).

The authors note that in forest ecosystems, invasive plants can reduce native diversity, alter forest structure, suppress tree regeneration, alter nutrient cycling, and modify disturbance regimes. Some – the shrubs and vines – also threaten human health by promoting increases in tick populations and associated Lyme disease risks.

Unsurprisingly, the data showed invasive plants to be widespread, and increasing. In 80% of the park units, there was a significant increase in at least one trend measuring abundance. Any decrease in plant invaders tended to be in herbaceous or graminoid species; that decrease was often counterbalanced by an approximately equivalent increase in invasive shrubs or vines. In 35 of the park units, more than half of the plots had at least one invasive plant species when the 2015-2018 survey began. In 10 parks (a quarter of those surveyed), every plot had at least one.

The most widespread species is Japanese stiltgrass (Microstegium vimineum). It is present in more than 75% of all park units and 30% of all 1,400 plots. This dominance is true despite the fact that stiltgrass does not extend north of Roosevelt-Vanderbilt National Historic Site in New York state (41^o N latitude). Stiltgrass is also the most aggressive invader.

The second most widespread invaders are a group of shrubs and vines, including most notably Japanese barberry (Berberis thunbergii), Japanese honeysuckle (Lonicera japonica), multiflora rose (Rosa multiflora), and wineberry (Rubus phoenicolasius). I note – although the articles does not – that several of these have been deliberately planted – either to “enhance” ecosystems (multiflora rose) or as ornamentals (barberry). [Lehan et al. 2013 (full reference at end of blog) found that 95% of 125 shrub species introduced to the U.S. were introduced deliberately.] I know of no examples of deliberate planting of Japanese stiltgrass.

The most frequently detected non-grass herbaceous species is garlic mustard (Alliaria petiolata), which was detected in 20% of plots. Garlic mustard is found throughout the study area (Virginia to Maine). Tree-of-heaven (Ailanthus altissima) is the most common invasive tree. It is found in only 9% of plots and does not grow north of Roosevelt-Vanderbilt NHS. Again, both were intentionally introduced – and not noted as such in the article.

Because they could not identify the source populations for each plot, the study could not directly measure rates of establishment and expansion. The data did allow tracking rough trends in each park.

Parks with the highest abundance tended to be near densely populated areas. However, this pattern was not universal. For example, Prince William Forest Park in the outer Virginia suburbs of the District of Columbia metro area was one of two of the least invaded park units.

(note the prevalence of beech – I fear for the arrival of beech leaf disease!)

Total invasives increased significantly in 21 of the 39 parks for at least one metric. In 10 parks (a quarter of all parks), total invasives increased significantly in two of the three metrics. Antietam National Battlefield experienced the steepest increases.

The authors note that invasive plants continue to establish and expand, even in already heavily invaded forests. Thus they found little evidence of saturation. This finding conflicts with invasion theory. They also found antagonistic interactions between invasive species to be common.

The authors said managers should prioritize efforts to control Japanese stiltgrass and the shrubs and vinesdue to their widespread occurrence, rapid expansion, ability to suppress tree regeneration and understory diversity, and – in the case of the shrubs and vines, link to ticks.

The authors noted the need to better understand the drivers and impacts of invasive plants in eastern forests. They mentioned the overabundance of white-tailed deer (Odocoileus virginianus), latitude, climate change, fragmentation and urbanization. I have urged them to include analysis of deliberate planting of various species on lands within the park units or nearby. They have said that they will do so in the planned follow-up article.

The authors propose that deferred management of natural resources receive attention and sustained commitment on par with the attention to deferred maintenance of the park units’ infrastructure. The maintenance backlog has been addressed through recent legislation: the Great America Outdoors Act which provided $6.5 billion over five years to address deferred maintenance projects in all 419 national park units. I believe that these projects will not address invasive species, which are managed under the “Natural Resources” budget account, not “Maintenance”. Some “Maintenance” projects probably will include control of invasive plants. A former Interior Department official has suggested that resource management activities might be funded under another section of the legislation, which provides $900 million under the Land and Water Conservation program. I hope this is true.

National Park Service’ Overall Invasive Plant Program Now

In response to the mandate in the John D. Dingell, Jr. Conservation, Management, and Recreation Act (Public Law 116-9), the Department of Interior has issued a department-wide invasive species strategy. Will issuance of the new strategy provide impetus to the NPS to seek funding to implement its 2016 invasive plant strategic plan? Will Congress provide funds for this purpose?

Finding out the current status of National Park Service took a little effort. The NPS’ website has “popular” information about the efforts of individual regional Invasive Plant Management Teams (see links at the end of this blog). These posts provide only the briefest overview of program achievements and do not compare those accomplishments to the goals in the 2016 plan.

However, Terri Hogan, Invasive Plant Program Manager in the Biological Resources Division, provided following information:

NPS leadership now supports the agency’s invasive plant effort. The national Invasive Plant Program (IPP) contributes to the annual Natural Resource Stewardship and Science Directorate (NRSS)’ Biological Resource Division (BRD) work plan. All is guided by the “Four Pillars to Guide Natural Resource Activities and Investments”, adopted in 2016.

It is not clear that invasive species have the highest priority under this regime. The four “pillars” are

Holding the line – includes conserving biodiversity by removing invasive plants
Managing amid Continuous Change – includes conducting risk assessment and taking other actions to contain future exotic species
Leveraging for Conservation at Scale
Enhancing Stewardship and Science Access and Engagement

Cooperation with owners of neighboring private lands has been enhanced by engagement of the Western Governors Association and state and local political leaders. Many parks participate in Partnerships for Invasive Species Management (PRISMs), CISMS, and Cooperative Weed Management areas (CWMAs). This collaboration has been strengthened by adoption of the John D. Dingell, Jr. Act (see above).

In practice, the focus appears to still be on the Invasive Plant Management Teams (IPMTs). There are now 17 teams. Fifteen are funded through the national office. One is funded by an individual park; one funded through a regional office. Annual reports have been published for FYs 2017 and 2018. The FY19 report has been held up but should be posted soon.

The reports provide brief description of the overall program and vignettes of particular activities. There are more detailed – but still anecdotal – reports for each of the teams. It is difficult to determine whether there has been overall progress. For example, the reported total infested acreage increased from 133,658 acres in FY17 to 301,195 acres in FY18. This presumably reflects more intense monitoring as well as a probable increase in real infections. (The infested acreage figures do not address intensity of invasion on these acres.) The teams cumulatively treated 8,937 acres in FY 2017; 8,331 acres in FY 2018. They carried out inventory and monitoring projects on 169,057 acres in FY17, 210,000 acres in FY18.

Since the Miller article concerns the region from Virginia to Maine, I checked the FY17 and FY 18 reports from the Invasive Plant Management Teams from the Mid-Atlantic, National Capital Area, and Northeastern regions. The Mid-Atlantic team emphasized work on wavyleaf basketgrass and meadows in parks established to protect cultural or historic sites. The National Capital Area team emphasized partnerships and success eradicating Giant Hogweed (Heracleum mantegazzianum) on private land neighboring Rock Creek Park. The Northeastern Team serves 25 parks; the report emphasized leveraging resources and testing efficacy of pre-emergent herbicide for control of Japanese stiltgrass. With this exception, the teams do not appear to be prioritizing the species recommended for action by the Miller study.

Brief, “popular” articles about the NPS’ invasive plant effort are available here

Invasive Plant Management Teams – Biological Resources Division (U.S. National Park Service) (nps.gov)

NPS 20 Years of Invasive Plant Management

20 Years of Action in 2020: Invasive Plant Management Teams

20th Years of Action – The NPS IPMT Program

SOURCES

Lehan, N.E., J.R. Murphy, L.P. Thornburn, and B.A. Bradley. 2013. Accidental Introductions are an Important Source of Invasive Plants in the Continental United States. American Journal of Botany 100(7): 1287–1293. 2013.

Miller, K. M., B. J. McGill, A. S. Weed, C. E. Seirup, J. A. Comiskey, E. R. Matthews, S. Perles, & J. Paul Schmit. 2020. Long-term trends indicate that invasive plants are pervasive and increasing in eastern national parks. Ecology. 00(00):e02239. 10.1002/eap.2239

Posted by Faith Campbell

Bureau of Customs Strengthens Programs Aimed at Preventing Insect Introductions in Wood Packaging

This February marks 15 years since USDA began full implementation of ISPM#15. It is 22 years since the U.S. and Canada began requiring China to treat wood packaging (in response to introductions of the Asian longhorned beetle). Nevertheless, numerous shipments containing wood packaging that does not comply with the international regulations continue to arrive at our borders – and to bring pests. During Fiscal Years 2010 through 2019, CBP detected 7,900 shipments of wood packaging that harbored a pest significant enough to be in a regulated taxonomic group. In 2020, 16.6 million TEU from Asia entered the U.S. (Mongelluzzo Jan 21). If pest approach rates are the same now as 10 years ago, perhaps 6,000 or more of these containers bore wood packaging infested by tree-killing insects.

The Bureau of Customs and Border Protection (CBP), in the Department of Homeland Security, has taken steps to strengthen its programs aimed at getting insects out of the wood packaging pathway (described here).

I wish USDA APHIS took a similarly active stance. You can help by contacting your Congressperson and senators to urge their support effective actions, such as those I suggested in my blog in January.

CPB’s 2017 Improvement

Until November 1, 2017, CBD allowed importers to escape punishment until they had been caught using wood packaging that did not comply with ISPM#15 five times in one year. On that date, CBD began issuing a penalty under Title 19 United States Code (USC) § 1595a(b) or under 19 USC § 1592 to any party responsible for a shipment with a documented wood packaging violation. At the time, I praised CBP’s action. I have tried to find out how many times over the past three years CBP has used that new provision to issue penalties, but CBP staff have not replied to my question.

CPB’s 2020 Improvement

CBD took another step forward in 2020. The agency incorporated measures to clean up solid wood packing material (SWPM) into its Customs-Trade Partnership Against Terrorism (CTPAT) program. I had been urging this since 2016. It took a while – but CBP used that time to ensure that its action would be integrated into the program and so stay in effect.

CTPAT is a voluntary public-private sector partnership engaging the principle participants in international supply chains — importers, carriers, consolidators, licensed customs brokers, and manufacturers.

By signing on, they agree to help CBP ensure the highest level of cargo security. Specifically, when an entity joins CTPAT, it agrees to work with CBP to protect the supply chain, identify security gaps, and implement specific security measures and best practices.

CTPAT member companies receive several benefits in return. Because they are considered to be of low risk, their shipments are less likely to be examined and delayed at a U.S. port of entry. When they are subjected to inspection, they go to the front of the line – again, reducing costly delays. The CTPAT web-based Portal system provides a library of training materials. (Information from the CBP website; full citation at end of the blog.)

At present, more than 11,400 certified partners have joined the program. These include U.S./Canada highway and rail carriers and Canadian manufacturers – who are not subject to the U.S.’ wood packaging regulation per se. Thus, CBD’s action seems to extend pest-prevention protection to a group of suppliers previously exempted from this phytosanitary program. Inclusion of many Mexican carriers and manufacturers is also welcome, since Mexican suppliers have always ranked high in numbers of shipments that violate the ISPM#15 requirements.

Specific Minimum Security Criteria

CBP’s action took the form of adding a long list of critical new agricultural components to the Minimum Security Criteria (MSC) it already used. These include:

Having written procedures for both security and agricultural inspections.
Carrying out CTPAT approved security and agricultural inspections of all conveyances and empty Instruments of International Traffic (e.g., shipping tanks, lift vans) prior to loading. The inspection must ensure that they are not contaminated with visible agricultural pests.
If visible pest contamination is found during the inspection, the partner business must wash or vacuum the conveyance to remove such contamination. The company must retain documentation demonstrating compliance for one year.
Vessels that visited Asian Gypsy Moth (AGM) high-risk areas during periods when the moths are flying must present a pre-departure AGM inspection certificate from an approved entity stating that the vessel is free of AGM life stages. The AGM inspections must be performed at the regulated port as close to vessel departure time as possible. CTPAT sea carriers must provide CPB with two-year port-of-call data at least 96 hours before arrival at a U.S. port.
Cargo staging areas, and the immediate surrounding areas, must be inspected on a regular basis to ensure these areas remain free of visible pest contamination.
CTPAT Members must have written procedures designed to prevent visible pest contamination to include compliance with ISPM#15 regulations. Visible pest prevention measures must be adhered to throughout the supply chain.
Members must establish and maintain a security training and awareness program to recognize and foster awareness of the security vulnerabilities to facilities, conveyances, and cargo at each point in the supply chain. The training program must be comprehensive and cover all of CTPAT’s security requirements. Personnel in sensitive positions must receive additional specialized training geared toward the responsibilities that the position holds.
Drivers and other personnel that conduct security and agricultural inspections of empty conveyances and Instruments of International Traffic (IIT) must be trained to inspect their conveyances/IIT for both security and agricultural purposes.
Training must be provided to applicable personnel on preventing visible pest contamination. Training must encompass pest prevention measures, regulatory requirements applicable to wood packaging materials, and identification of infested wood.

The actual Minimum Security Criteria can be found here.

Training Powerpoints are here.

(The summary of these criteria was provided by Stephen Brady, Senior Agriculture Operations Manager, Agriculture Programs and Trade Liaison, U.S. Customs and Border Protection.)

Inclusion of wood packaging in the CTPAT program should result in more efficient efforts to detect infested wood packaging before shipment — before the insect can reach North America. I believe it is fair to importers in that it requires action based on visible pest presence or damage. I applaud Customs and Border Protection for making the effort – internally and with the shipping industry — to add this protection.

I think fairness would be further served by CBP and APHIS adopting a program to inform importers which foreign suppliers of wood packaging have a record of providing “clean” vs. “infested” wood packaging. The U.S. importers would then be better able to avoid both contributing to the pest risk and being exposed to violation-associated delays.

SOURCES:

CBP website

Mongelluzzo , B. US imports from Asia hit record December level. Jan 19, 2021

Posted by Faith Campbell

APHIS funding of programs targetting tree pests (& some others)

spotted lanternfly; photograph by Holly Ragusa, Pennsylvania Department of Agriculture

Since Fiscal Year (FY)2009, APHIS has had access to a program that has permanent funding, not subject to the vagaries of annual budgeting and appropriations. The Plant Pest and Disease Management and Disaster Prevention Program established by 7 U.S.C. Section 7721. The program was initially funded at $12 million for FY2009; $45 million in FY2010; $62.5 million in 2014-2017; and $75 million since FY2018.

Funds are provided under a competitive grants program to universities, states, Federal agencies, nongovernmental organizations, non-profits, and Tribal organizations “to conduct critical projects that keep U.S. crops, nurseries, and forests healthy, boost the marketability of agricultural products within the country and abroad, and help us do right and feed everyone.” [USDA press release “USDA Provides $66 Million in Fiscal Year 2019 to Protect Agriculture and Natural Resources from Plant Pests and Diseases” February 15, 2019]

By my calculation, total funding of tree pests projects during the period Fiscal Year (FY09) through FY20 was about $94 million. This represented 15.6% of nearly $600 million in total funding under the program during this period.

In the initial years, forest pest projects received about 10-12% of total funds. In later years, the proportion has been higher – e.g., 30% in FY19, 13.8% in FY20. The early years were dominated by management of the sudden oak death pathogen (SOD), Phytophthora ramorum. In FY09, SOD projects receive $7.5 million, or 8% of all tree pest funding. This funding helped set up the National Ornamental Nursery study center (NORS-DUC); later years paid for research projects on SOD management issues and nursery surveys.

In the most recent years, funding has been dominated by detection, management, and research on spotted lanternfly – which is not primarily a forest pest. Thus, in FY 19, 56.8% ($10,339,126) of $18,195,000 allocated to tree pests; in FY20, 30% ($2,606,094) of the $8,705,920 allocated to all tree pests.

The FY2019 program also provided $1,107,965 in 14 states and nationally for P. ramorum survey, diagnostics, mitigation, probability modeling, genetic analysis, and outreach (USDA press release 2019). This was appropriate considering the shipment of SOD-infected plants to nurseries in 18 states in spring 2019.

Current Year Funding

APHIS has released the list of projects funded under the Plant Protection Act Section 7721 in FY2021. Link to website APHIS funded 354 projects in 49 states, Guam, Puerto Rico and the District of Columbia, at a total cost of $63.225 million. APHIS is retaining ~ $14 million to allow responses to pest and plant health emergencies. Total funding for forest pests – by my calculation – was $8,715,046 (13.7% of the total).

My analysis finds that in FY21, 13 states had no funded projects that applied to tree pests: Arizona, Colorado, District of Columbia, Guam, Hawaii, Idaho, Nebraska, New Jersey, New Mexico, North Dakota, Rhode Island, South Dakota, and Utah.

Most commonly funded projects:

Surveys and other efforts addressing wood borers: 37 projects, including
- Thousand cankers disease: 4 (all surveys)
- Emerald ash borer: 6 projects (surveys and management, including biocontrol)
- Asian longhorned beetle: 3, of which 2 are outreach
- Laurel wilt disease: 1 project
- Detection tools for wood-borers, including citrus longhorned beetle, Sirex noctilio, Agrilus biguttatus, and Australian Cerambycids
Phytophthora ramorum: 20 projects, primarily nursery surveys but including a few management projects. The projects were in 18 states.
Surveys for Asian defoliating moths in the Lymantra genus: 15 projects
Surveys and control efforts targetting spotted lanternfly: 13 projects in 6 states. These included research conducted by the APHIS Otis laboratory in Massachusetts. The grants totaled $2,788,010, or 32% of total forest pest funding.

APHIS funded 16 outreach projects (there is some overlap with above), including three specifically mentioning firewood. The latter included principal funding for the “Don’t Move firewood” national campaign.

Other projects that I find interesting:

2 projects targetting hemlock woolly adelgid
1 targetting red palm weevil
4 projects targetting Asian giant hornet in Washington and Oregon and the APHIS Otis laboratory. California has a project relating to a wider range of hornets that was also funded in FY20.
Biocontrol of several invasive plant species in Florida – Australian pine/Casuarina, Brazilian pepper, and Ailanthus

Harrisia cactus attacked by the mealybug; photo by Yorelyz Rodríguez-Reyes

As readers of this blog know, I also care deeply about threats to our native cacti – especially flat-padded Opuntia and tubular cacti endemic to Puerto Rico. Over the 13 years of program, funded following projects for cacti:

FY11 $244,368 for efforts to develop sterile insect methodology to control cactus moth
FY17 develop biocontrol for Harissia cactus mealybug $210,000
FY19 Harissia cactus mealybug – $355,774; cactus moth $216,243
FY20 Harrisia cactus mealybug $301,930
FY 21 cactus moth biocontrol $175,659 and $352,236 for Harrisia cactus mealybug biocontrol

Clearly, having access to $75 million that is not subject to the limits imposed by Administration budget priorities or Congressional appropriations has allowed considerable freedom. The fund has allowed APHIS to support work on pests that have not been designated “quarantine pests,” e.g., walnut canker disease of walnut, the polyphagous and Kuroshio shot hole borers, hemlock woolly adelgid, and the cactus pests. The program also funded many projects targetting the spotted lanternfly (SLF) – both before and after the lanternfly became a formal APHIS program (which occurred after it was detected outside Pennsylvania). Now that SLF has been found in several states, funding has partially shifted to appropriated funds. The FY21 appropriation included an additional $4 million for management of SLF; this was incorporated in the “specialty crops” line item.

So far, there has been no funding for beech leaf disease through this program; I don’t know whether any of the people working on this disease had applied.

Posted by Faith Campbell

Rising Pest Danger to New Regions Parallels Rise in Imports

container ship in Savannah harbor- capacity 6,188 containers; photo by F.T. Campbell

As I have blogged recently U.S. imports have soared since the summer. US imports from Asia during the first 11 months of 2020 were 2% higher than the figure from the first 11 months of 2019, despite the crash in imports in the spring.

The increased volume is not distributed evenly. Asian imports moving through the twin ports of Long Beach and Los Angeles (LA/LB) were 26.5% higher in November 2020 compared to November 2019. As a result, the ports’ marine terminals, longshore labor force, drayage truckers, and import distribution centers cannot keep up. As of early January, 62 container ships were at LA/LB – 29 being offloaded and 33 ships at anchor awaiting berths. Nineteen additional arrivals were scheduled within a few days. This is the largest backup in Southern California since the disruptions associated with the 2014-15 West Coast longshore labor dispute (Mongelluzzo, B. January 4, 2021).

As a result of the long delays at LA/LB, plus port expansion under way at other ports, the volume of imports entering elsewhere is rising – with a commensurate increase in the pest risk associated with wood packaging material there.

Imports from Asia through the Northwest Seaport Alliance (NWSA) of Seattle and Tacoma increased 9.9% in November 2020 compared to November 2019. Imports through Oakland were up 2.2% year over year (Mongelluzzo, B. January 4, 2021). These ports’ proportion of imports from Asia should rise even higher in the future. One company has begun a premium service from China directly to Oakland and Seattle. Shippers are expected to welcome this as an opportunity to avoid the congestion at LA/LB. Oakland also offers access to the large and affluent San Francisco Bay area, as well as rail transport to inland hubs such as Chicago, Memphis, Dallas, and Kansas City.

The principal disadvantage is that these ports can handle only ships carrying 3,500 to 6,500 TEU capacity [twenty-foot equivalent units; a standard measurement that counts incoming volume as though contained in twenty-foot-long containers] (Mongelluzzo, B. January 04, 2021). Other ports, e.g., LA/LB and Savannah, routinely handle ships carrying 10,000 or more TEUs.

As I have noted in earlier blogs, US Gulf Coast ports are expanding capacity significantly to handle vessels larger their current10,000 TEU limit. The Port of Houston is adding a new deepwater container berth and expanding its ship channel. At New Orleans, the U.S. Army Corps of Engineers is dredging the lower reaches of the Mississippi River. The Port of Mobile also has a dredging project under way. Tampa Bay plans to double its capacity over the next five years (Angell, January 4, 2021).

The Port of Savannah currently has 9 berths served by 36 cranes. The Port plans to increase capacity by 45% over the next decade – from 5.5 million TEUs to 8 million TEUs per year (https://gaports.com/facilities/port-of-savannah/).

Government Agencies’ Involvement

These port expansions are partially funded by U.S. government agencies. The Department of Transportation funds development of onshore facilities, while the U.S. Army Corps of Engineers carries out dredging of the waterways. We should insist that the environmental impact statements evaluating these projects include consideration of the invasive species risks associated with increased ship traffic. Potential harm comes from a wide range of organisms, which put an equally wide range of ecosystems at risk. For example, ship traffic has brought our country ruinous aquatic invertebrates in ballast water and sessile organisms on hulls; as well as costly Asian gypsy moths on ships’ superstructures and a series of tree-pest larvae in wooden dunnage and other packaging material (e.g., Asian longhorned beetle, emerald ash borer, redbay ambrosia beetle, possibly the invasive shot hole borers …).

The surge in imports from Asia has continued through the first half of 2021. Over this period, imports from Asia to the California ports of Los Angeles and Long Beach totaled 9,523,959 TEU, up 24.5% from the 7,649,095 TEU in the same period of 2019 (Mongelluzzo, B. July 12, 2021).

SOURCES

Angell, M. Outlook 2021: US Gulf Coast ports moving forward with major capacity expansions. Journal of Commerce January 04, 2021 https://www.joc.com/port-news/us-ports/outlook-2021-us-gulf-coast-ports-moving-forward-major-capacity-expansions_20210104.html?utm_campaign=CL_JOC%20Port%20Newsletter%201%2F6%2F21__e-production_E-85987_TF_0106_0900&utm_medium=email&utm_source=Eloqua

Mongelluzzo, B. CMA CGM’s new Asia service to give Oakland long-sought first call. Journal of Commerce January 04, 2021 https://www.joc.com/maritime-news/container-lines/cma-cgm%E2%80%99s-new-asia-service-give-oakland-long-sought-first-call_20210104.html?utm_source=Eloqua&utm_medium=email&utm_campaign=CL_JOC%20Daily%201%2F5%2F21%20_JOC%20Daily%20Newswire_e-production_E-85981_TF_0105_0617

Mongelluzzo, B. Strong US imports from Asia in June point to a larger summer surge. July 12, 2021.

https://www.joc.com/maritime-news/container-lines/strong-us-imports-asia-june-point-larger-summer-surge_20210712.html?utm_source=Eloqua&utm_medium=email&utm_campaign=CL_JOC%20Daily%207%2F13%2F21_PC00000_e-production_E-106057_KB_0713_0617

Posted by Faith Campbell

Decision!! California Department of Food & Agriculture Upgrades Ranking of Phytophthora occultans

In January 2021, the California Department of Food and Agriculture announced the pest rating for Phytophthora occultans, one of two species of Phytophthora it was reviewing. (Once at the website, click on “comment” – next to name Heather Sheck.)

I blogged about this action in December.

Five people or organizations submitted comments. The most comprehensive comments were submitted by Elizabeth Bernhardt, Ph. D. and Tedmund Swiecki Ph.D. of Phytosphere Research. Another scientist was Tyler Bourret, who had been the first to detect P. occultans in California when working as a student in 2015-16. The third scientist was Jennifer Parke, a plant pathologist at Oregon State University who has worked with Phytophthora species in agriculture and wildland settings for 36 years. Additional comments were submitted by the Phytophthoras in Native Habitats Work Group and me.

All commenters raised some issues. First was the lack of information on the true distribution of P. occultans in California. CDFA restated that it that relies on official records and survey information, and that those records support a “low” rating.

Several issues relate to the definitions that CDFA applies in assigning ranks. They are so restrictive that – in my view – they result in underestimates of pathogens’ potential impacts.

One example is how CDFA recognizes first detections of a pathogen. As Bernhardt and Swiecki point out, CDFA’s consideration of only “official” samples prevents timely action to protect California’s agriculture and native vegetation. In the case of P. occultans, CDFA took no action for two years after the pathogen was first reported in the state. This detection had been confirmed by a CDFA laboratory.

A second example is host range. CDFA says it assigns a host range rating of “wide” (rating of “3”) only to pathogens that have host ranges of hundreds of species. This means that pathogens with dozens of known hosts across several plant families are given a ranking of “moderate” (2). Furthermore, the agency considers only “official” samples in defining hosts. This approach precludes consideration of the high probability that additional hosts would be found in future, including federally listed species in the genera Ceanothus and Arctostaphylos. Bernhardt and Swiecki named two additional hosts based on field work. CDFA responded to the second point by adding a reference to the likely expansion of the host range in the “Uncertainty” section of the document.

Similarly, CDFA gives a reproductive potential rating of “3” only to pathogens spread by a vector or that infect seeds.

CDFA staffers who manage specific pests lack authority to change these too stringent ranking criteria. The agency leadership need to adopt more realistic criteria.

CDFA responded by accepting many of the additional factors raised primarily by Bernhardt and Swiecki. This resulted in raising the overall score from 11 to 14, and changing the ranking from “C” to “B”.

Posted by Faith Campbell

APHIS Deregulates Emerald Ash Borer – Now it is up to the States

APHIS formally proposed to stop regulating movement of firewood, nursery stock, and other articles that can transport the emerald ash borer (EAB) in 2018; I blogged in opposition to this proposal at the time. Now APHIS has evaluated the 2018 comments on its proposal and has decided to proceed with its plans.

I recently blogged about the current and probable future status of ash. A study confirmed that robust regeneration of ash seedlings and saplings seen in various invaded areas will not result in recovery of mature ashes that can perform their ecological role.

APHIS received 146 comments on the proposal. Twenty-five supported the proposal as written; 121 raised concerns. Many of the latter were a few sentences without supporting information. These comments and the final rulemaking can be read here.

How has APHIS responded to the serious questions raised? Dismissively.

I certainly concede that EAB has been difficult to manage and has spread rapidly. However, I continue tobelieve that maintaining the quarantine serves important purposes and the analysis APHIS provides does not justify terminating of the regulatory program. I remain concerned.

Neither the proposal nor the final regulation tells us how much money and staff resources have been dedicated to detection or enforcement of the regulations in recent years. Therefore we don’t know how many resources are now available for supporting other activities that the agency thinks are more effective. APHIS also refuses to provide specific information on how it will allocate the freed-up resources among its (minimal) continuing efforts. For example, APHIS has supported resistance-breeding programs. Will it help them expand to additional species, e.g., black and Oregon ash?

How Does APHIS Propose to Curtail EAB Spread?

APHIS states in the final rule that it is ending the domestic quarantine regulation so that it can allocate resources to more effective strategies for managing and containing EAB. The agency wants to reallocate funds “to activities of greater long-term benefit to slowing the spread of EAB … These activities include further development and deployment of EAB biocontrol organisms; further research into integrated pest management of EAB that can be used at the local level to protect an ash population of significant importance to a community; and further research, in tandem with other Federal agencies, into the phenomenon of “lingering ash … ”

However, APHIS has not funded detection efforts since 2019. (Detection methods were only partially effective, but they gave us some information on where EAB had established.) APHIS is now ending regulation of the movement of vectors. APHIS concedes that biocontrol agents cannot be effective in preventing pest spread. So – what efforts – other than continued support for the “Don’t Move Firewood” campaign – will APHIS make to slow the spread of EAB?

Environmental and Economic Impacts: Not Adequately Assessed

Second, APHIS still has not analyzed the economic or environmental impact of the more rapid spread of EAB to the large areas of the country that are not yet infested – especially the West Coast – that are likely to result from deregulation. As even APHIS concedes, the EAB is currently known to occupy only 27% of the range of native Fraxinus species within conterminous US. There are additional large ash populations in Canada and Mexico – although neither country commented on the proposal — unfortunately!

Instead, APHIS largely restates its position from the proposal that it is too difficult to calculate such impacts. Furthermore, that it is APHIS’ “experience that widely prevalent plant pests tend, over time, to spread throughout the geographical range of their hosts …” In other words, APHIS denies the value of delaying invasions – yet that has always been a premise underlying any quarantine program.

The final regulation refers to an updated economic analysis, but no such document is posted on the official website. The rule does not mention costs to homeowners, property owners, municipal governments, etc. I believe it would not be so difficult to estimate costs to these entities by applying costs of tree removal in the Midwest to tree census data from major West Coast cities. Also, it might have been possible to provide some estimate of the ecological values in riparian forests by analogy to data from the Midwest developed by Deborah McCullough and others.

Biological Control: Effective – or Not

In the final regulation, APHIS concedes that the biocontrol agents currently being released have geographic and other limitations. However, APHIS does not address concerns raised by me and others about their efficacy. APHIS does say explicitly that it has not [yet?] begun efforts to find biocontrol agents that might be more effective in warmer parts of the ash range, especially the Pacific Northwest and riparian areas of the desert Southwest. However, APHIS has conceded that these areas are almost certain to be invaded – so should it not take precautionary action?

APHIS states several times that it cannot promise specific funding allocations among program components or strategies – such as resistance breeding – that might be pursued in the future. The agency stresses the value of flexibility.

U.S. Forest Service biologists have higher expectations; see their podcast here.

I wish to clarify that I do not oppose use of biocontrol; I strongly supported then APHIS Deputy Administrator Ric Dunkle’s decision to initiate biocontrol efforts for EAB early in the infestation. My objections are to overly optimistic descriptions of the program’s efficacy.

Firewood: Outreach Only, No National Regulation

As noted, APHIS has promised to continue support for public outreach activities, especially the “Don ‘t Move Firewood” campaign. The program’s message will continue to encourage the public to buy firewood where they burn it and to refrain from moving firewood from areas that are under Federal quarantine for other pests of firewood (e.g., Asian longhorned beetle). This campaign and the new National Plant Board guidelines link stress that firewood is a high-risk pathway for many pests of national or regional concern; they do not focus on any particular species. Leigh Greenwood, director of Don’t Move Firewood, thinks this is a good approach.

In 2010, the National Firewood Task Force recommended that APHIS regulate firewood at the national level. APHIS does explain why the agency did not do so. The agency says national regulations would be overly restrictive for some states and that requiring heat treatment would not be feasible in the winter for producers in Northern states. Finally, a Federal regulation would not address a significant non-commercial pathway – campers. [I have serious questions about APHIS’ assertion that it can regulate only commercial movement of vectors across state lines. Contact me directly for details on this.]

Perhaps APHIS is not required to analyze the probable overarching efficacy of the several efforts of 50 states. Given the states’ many perspectives and obvious difficulty in coordinating their actions on phytosanitary and other policies, I fear a scattered approach that will result in faster spread of EAB. I hope the National Plant Board guidelines on firewood regulation and outreach can overcome the history.

Most federally-managed recreation areas adopted an education campaign on firewood in autumn 2016; I blogged about it then.

Imported Wood Will be Minimally Regulated

APHIS clarifies that it will take enforcement actions against imports of ash wood only if inspectors detect larvae but can identify them just to family level and not below. APHIS will allow the importation if the larvae can be identified as EAB specifically. This policy reflects international standards, which do not allow a country to erect restrictions targetting a pest from abroad if that pest is also present inside the country and is not under an official control program. (See my discussion of the WTO Agreement on Sanitary and Phytosanitary Standards in Chapter 3 and Appendix 3 of Fading Forests II, available here.)

APHIS does not discuss how it will react to pests identified to the genus – several other Agrilus also pose pest risks. (See here and here.)

APHIS recommends that states leery of accepting yet more EAB-infested wood from abroad petition the agency under the Federally Recognized State Managed Phytosanitary Program (FRSMP) program, under which APHIS would take action to prevent movement of infested material to that particular state.

Lessons Learned

Finally, one commenter asked whether APHIS would analyze the program to learn what could have improved results. APHIS replies that the agency “tend[s] to reserve such evaluations for particular procedures or policies in order to limit their scope …” I hope APHIS is serious about “considering” doing a “lessons learned” evaluation. It is important to understand what could have been done better to protect America’s plant resources.

My take: the EAB experience proves, once again, that quarantine zones must extent to probable locations – beyond the known locations. The pest is almost always more widely distributed than documented. This has been true for EAB, sudden oak death, ALB, citrus canker … Failure to regulate “ahead” of the pest guarantees failure. I recognize that adopting this stance probably requires a change in the law (or at least understanding of it) and of current international standards adopted by the International Plant Protection Convention (IPPC). However, absent a more aggressive approach, programs are doomed to be constantly chasing the pest’s posterior.

Finally, let us mourn the loss of ash so far, the future losses … and opportunities missed.

Posted by Faith Campbell

Let’s shape the Biden Administration’s & New Congress’ Policies on Non-Native Forest Pests!

We have a great opportunity to shape future efforts to counter non-native forest pests and diseases. Administration officials are most open to new ideas when they first take office. The same is true of new Congressional leadership.

So now is the time to suggest needed changes!

The USDA Secretary-designate is Tom Vilsack. Of course, he was USDA Secretary during the Obama Administration … so he is not entirely “new” to the issues. However, perspectives and priorities have changed, so now is a good time to urge him to consider new approaches. Furthermore, the Senate Agriculture Committee will hold confirmation hearings for him; we can ask the Senators to advocate for our views during this proceeding.

The House Agriculture Committee has a new Chair, David Scott – from the suburbs of Atlanta, Georgia. Again, this provides an opportunity to suggest new approaches and topics for hearings.

I assume you all are knowledgeable about the numbers and impacts of non-native forest insects and pathogens in the United States, and of the pathways by which they are introduced and spread. If you are not, peruse my blogs about wood packaging or plants as vectors (click on the appropriate “categories” listed at the bottom of the archive of blogs). Or read Fading Forests III (see the link at the end of this blog) and the article I coauthored early this year on improving forest pest management programs.

On the basis of my long experience, I suggest that you encourage USDA Secretary-designate Vilsack, Senators on the Agriculture Committee, and House Agriculture Committee Chair David Scott to consider the following recommendations:

Actions Congress could take

Congress could amend the Plant Protection Act [7 U.S.C. §7701, et seq. (2000)] to prioritize the protection of natural and agricultural resources over the facilitation of trade. This might be done by amending the “findings” section of the statute to give higher priority to pest prevention.
The Agriculture Committees of both the House and Senate could hold hearings on the importation of forest pests. They could determine if the USDA is doing an adequate job protecting the country from insect pests and diseases, and how our defenses could be strengthened. One component of the hearings could focus on whether current funding levels and mechanisms are adequate to support vigorous responses to new pest incursions.
Congress could commission a study of the feasibility, costs and benefits of establishing a “Center for Forest Pest Control and Prevention” to coordinate research and policy on this issue.
Congress could increase funding for the appropriate USDA APHIS and Forest Service programs and activities to enable vigorous containment and eradication responses targeting introduced forest pests and diseases.
Congress could increase funding for USDA research on detection of insects and pathogens in shipping; insect and disease monitoring/surveillance; biological control; alternatives to packaging made from wooden boards; management of established pests; and resistance breeding to enable restoration of impacted tree species.

Actions Secretary-designate Vilsack could initiate without legislative action (once he is confirmed)

Introductions of pests in the wooden crates, pallets, etc., goods come in

APHIS could take emergency action to prohibit use of wood packaging by importers of goods from countries with a record of poor compliance with ISPM#15. This action is allowed under authority of the Plant Protection Act [7 U.S.C. §7701, et seq. (2000)] and Article 5.7 of the World Trade Organization’s Agreement on the Application of Sanitary and Phytosanitary Measures.
APHIS could strengthen enforcement of current regulations by aggressively prosecuting repeat offenders. For instance, APHIS could begin imposing administrative financial penalties on importers each time their wood packaging is non-compliant with ISPM#15.
APHIS could work with Department of Homeland Security Bureau of Customs and Border Protection (CBP) to improve information available to U.S. importers about which foreign suppliers of SWPM and shippers have good vs. bad records of compliance with ISPM#15.
DHS CBP could release information on country of origin and treatment facility for ISPM#15-stamped SWPM that is found to be infested with pests.
USDA APHIS could begin a phased transition from solid wood packaging to alternative materials that cannot carry wood-boring pests. APHIS could initiate a pest risk assessment to justify making such an action permanent. Imports could be packaged in alternative materials, e.g., manufactured wood products (e.g. plywood), metal, or plastic.

Nursery Plant (“Plants for Planting”) Pathway

APHIS could apply authorities under NAPPRA and other existing authorities to curtail imports of plants that pose a high risk of introducing insects and pathogens that would threaten tree species that are important in natural and urban forests in the U.S. At a minimum, APHIS should restrict imports of live plants that are in the same genus as native woody plants of the U.S.
APHIS could work with the Agriculture Research Service and National Institute of Food and Agriculture to determine which taxa of woody vegetation native to the U.S. are vulnerable to pathogens present in natural systems of trade partners. Particularly important would be the many Phytophthora species found by Jung and colleagues in Vietnam, Taiwan, Chile, and other countries. Once the studies are sufficiently complete, APHIS could utilize authority under NAPPRA to prohibit importation of plants from those source countries until effective phytosanitary measures can be identified and adopted.

Other Actions

APHIS could develop procedures to ensure the periodic evaluation of pest approach rates associated with wood packaging and imports of “plants for planting” and highlight areas of program strengths and weaknesses. A good place to start would be to update the study by Haack et al. (2014), which estimated the approach rate in wood packaging a decade ago.
The USDA could expand early detection systems for forest pests, such as the APHIS CAPS program and the Forest Service EDRR program. These programs should be better coordinated with each other and should make better use of citizen observations collected through smartphone apps, professional tree workers such as arborists and utility crews, and university expertise in pest identification and public outreach. An effective program would survey for a broad range of pests as well as for suspicious tree damage, and would be focused on high-risk areas such as forests around seaports, airports, plant nurseries, and facilities such as warehouses that engage in international trade.
The USDA could initiate a “Sentinel Plantings“ network of US tree species planted in gardens abroad and monitored for potential pests and diseases.

Posted by Faith Campbell