Source: UNIVERSITY OF WASHINGTON submitted to NRP
CLIMATE WARMING AND FOREST INSECT OUTBREAK DYNAMICS IN THE PACIFIC NORTHWEST
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
1023787
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
(N/A)
Project Start Date
Sep 16, 2020
Project End Date
Sep 15, 2021
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
UNIVERSITY OF WASHINGTON
4333 BROOKLYN AVE NE
SEATTLE,WA 98195
Performing Department
Forest Ecology
Non Technical Summary
Forest insect outbreaks are often catastrophic events that lead to large-scale tree mortality over a relatively short period of time, and cascading negative effects including reductions in timber quality, changes in wildlife habitat, and increased carbon emission. Consequently, understanding forest insect outbreak dynamics is a critical ingredient in efforts to maintain forest health in the face of potentially converging threats to forests and the ecosystem services they provide. This project aims to measure changes in the spatial and temporal dynamics of forest insect outbreaks in Pacific Northwestern conifer forests from 1960-2019, and to measure the role of natural enemies in western and eastern Washington on the dynamics of two economically important forest insect pests, the Douglas-fir beetle and the western spruce budworm. The results of this project will inform and improve integrative forest pest management strategies.
Animal Health Component
25%
Research Effort Categories
Basic
75%
Applied
25%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
1230612106034%
1320699107033%
2113110113033%
Goals / Objectives
Forest insect outbreaks are economically and ecologically devastating, and can leave long lasting disturbance legacies due to the extensive and resulting tree mortality. Outbreaks can also overwhelm budgetary and logistical resources allocated to mitigate their impacts. This project will improve our understanding of forest insect outbreaks in the Pacific Northwest through long-term analyses, and to the State of Washington through field-based studies aimed at understanding the factors that enable or prevent the development of forest insect outbreaks.Pacific Northwestern forests are under increasing threats due to climate change, fire, introduction of non-native invasive species, and increased outbreak frequency and intensity from native insects. The proposed one-year project addresses the timely issue of biotic disturbances in the Pacific Northwest. It also leverages existing funds from the National Science Foundation through the Graduate Research Fellowship Program, which is providing 3 years of funding to the PhD student funded by this project.Objective 1: Quantify the spatial and temporal patterns in forest insect outbreaks using historical aerial detection survey data from Oregon, Washington, and British Columbia from 1960-2019 to determine if outbreak patterns in insect pest species are changing.Objective 2: Quantify the role of stand conditions and natural enemies in affecting the population dynamics of two economically-important forest insect pest species, Douglas-fir beetle and western spruce budworm, in eastern and western Washington to determine how populations are regulated in different stand and weather conditions.
Project Methods
Objective 1: Quantify the spatial and temporal patterns in forest insect outbreaksWe will use aerial detection survey data collected by the USDA Forest Service, the Canadian Forest Service, and the British Columbia Ministry of Forests, from 1960 to 2019.We will use the ncf package (Bjørnstad 2020) in R (R Core Team 2018) to measure spatial autocorrelation, and the temporal auto and cross -correlation. The spatial autocorrelation is a measure of how a variable relates to itself as distance increases, and by measuring spatial autocorrelation through time (by decade, for example), we can determine if the mean autocorrelation has changed. Increases in spatial autocorrelation would suggest that forest insect outbreaks are increasing in spatial extent, and can be used to determine if areas within the study region are becoming more or less prone to forest insect outbreaks. We will also measure spatial auto- and cross-correlation through time for interacting species from between different guilds (i.e., folivores to bark beetles), and between specific insects from the same guild (i.e., Douglas-fir tussock moth and western spruce budworm) or different guild (i.e., Douglas-fir beetle and western spruce budworm) when interacting on the same host tree. Increases in the spatial and/or temporal overlap between interacting species could indicate areas in which biotic disturbance 'hotspots' are developing; biotic disturbance hotspots refer to the spatial and temporal overlap of different biotic disturbance agents, which could pose additional challenges to forest health if these hotspots are occurring at levels greater than historical levels. If there are increasing interactions between spatial patterns in folivores and bark beetles, compared to the early years (i.e., 1960s, 1970s), then it is likely that forest structure, communities, and associated ecosystem services will change.Objective 2: Quantify the role of stand conditions and natural enemies in affecting the population dynamics of Douglas-fir beetle and western spruce budwormAt each study site, we will install two transects with four plots in each transect in Douglas-fir dominated stands. The starting point of all transepts will be randomly selected based on the presence of Douglas-fir and depending on permission from the appropriate land owner. Plots within a transect will be separated by ~100 m, and transects will be >1 km apart. Within each plot, we will measure and identify all stems >5cm within a 15 m radius of the center of the plot. We will compile forest composition metrics in each plot (e.g., stand density, basal area, stand age) and compile data on the distance of plots from previous outbreaks, recent insect pest management activities, and background environmental variables (e.g., long-term weather data from PRISM/Oregon State University; elevation, aspect, and larger-scale forest composition data from the USGS landcover dataset and the U.S. Forest Service-Forest Inventory Analysis). At the center of plot, we will deploy one Lindgren multifunnel trap baited with a Douglas-fir beetle lure, and one trap baited with a western spruce budworm lure to assess background population levels for each insect.Within each plot, we will fell 1-2 Douglas-fir trees (~35 cm DBH), and/or or deploy 5-10 Douglas-fir bolts (approximately 1 m in length from a ~35 cm DBH tree), and/or sampling from the bark (~25´25 cm) from recently attacked trees (as noted by the presence of fresh pitch or frass). This level of sampling is designed to measure Douglas-fir beetle fitness and development, and to quantify egg, larval, and pupal predators and parasitoids. Multiple techniques are proposed due to restrictions at study sites (i.e., at some sites, due to fire risk or conservation purposes, felling a tree is not feasible or allowable, but bolt and bark sampling is). Samples will be taken by early spring prior to emergence, and placed in emergence containers under laboratory conditions to quantify adult beetle emergence, and the natural enemy community. Following emergence, samples will be dissected to quantify bark beetle oviposition, which will be used to measure adult emergence success rate, and to measure the dimensions of larval galleries, which is a sign of larval feeding success.Also, within each plot, we will deploy 2nd instars of western spruce budworm as sentinel prey immediately after larvae have terminated diapause. Larvae will be deployed in mesh covered buckets (to exclude vertebrate predators) containing freshly clipped Douglas-fir foliage from terminal branches, and used to measure invertebrate predators and parasitoids. Sentinel larvae will be supplemented weekly over the 6-8 weeks corresponding to the larval and pupal period. All larvae and pupae will be collected and placed in diet cups under laboratory conditions to measure adult emergence, predators, and parasitoids.Most prior work on the natural enemy communities of Douglas-fir beetle and western spruce budworm was conducted >40 years ago (Walters 1956, Furniss and Carolin 1977), which provides an excellent resource for the natural enemy community in the recent past, and aligns well with the historical aerial detection survey data from 1960 that we are addressing under Objective 1. The proposed research, along with data collected from 2019 and 2020, will be used to determine if the composition of the natural enemy community, as well as the dominant natural enemies, have changed over time. We will also use our field-collected data from all sites (including data from traps, tree/bolt/bark samples, and sentinel larvae) to quantify the composition of natural enemies using Shannon's diversity index and Pielou's evenness index (Southwood 1978). We will use these two indices to compare the composition of natural enemies between western and eastern Washington and determine the role of natural enemies in affecting the outbreak dynamics from eastern Washington, and the lack of outbreaks in western Washington. Lastly, we will measure the effect of forest composition metrics in each plot, distance from previous outbreaks, recent insect pest management activities in each plot, and background environmental variables including weather variables and larger-scale forest composition data on natural enemy diversity and evenness. Data will be analyzed using a linear mixed effects model using lme4 (Bates et al. 2015) in R (R Core Team 2018) with study site included as a random effect.

Progress 10/01/20 to 09/15/21

Outputs
Target Audience:Over the course of the project, we have engaged forest health professionals from the City of Seattle, Washington State Department of Natural Resources, and the USDA Forest Service, who manage the lands on which field sites were located. Results of the project will specifically benefit forest insect pest management by identifying areas within Pacific Northwestern coniferous forests that are more (or less) vulnerable to forest insect outbreaks, and those areas that are more (or less) likely to be affected by multiple biotic disturbance agents over a relatively short time period. Changes/Problems:There were no major changes or problems encountered. Despite COVID-19, we were still able to access field sites though it did force the student funded on the project to work independently, which is not ideal when conducting field work. Check-in procedures and a field safety plan for working under COVID-19 were implemented and approved by the University of Washington prior to conducting field work to ensure student safety. Due to lab safety procedures due to COVID-19, the student was required to process sampled data from the field independently as it was not possible to recruit undergraduate help, which prolonged the processing of data. We also were unable to deploy western spruce budworm larvae as part of our second objective as the rearing lab that supplies life stages of this insect was not able to fulfill our order due to COVID-19. However, we were successfully able to use an alternate sampling method to measure the natural enemy community, which was a method based on prior research in this study system. What opportunities for training and professional development has the project provided?The project funded and provided training for a PhD Candidate (Alex Pane) during the penultimate year of his degree program. The student's career goal is to work as a scientist at a land managing government agency, such as the USDA Forest Service. Training activities under the project included the sampling efforts to measure populations of the Douglas-fir bark beetle, competitor wood boring beetles, and natural enemies across western and eastern Washington. In concert with these efforts included techniques that quantified stand structure and composition. Skills gained from the field components of the project included insect taxonomy. In addition, the student used a long-term dataset, collected from 1960-2019 over an area that included Oregon, Washington, and British Columbia, to investigate the spatial and temporal patterns in forest insect outbreaks based on historical aerial detection survey data. In this objective, the student gained valuable experience using ArcGIS and complete computer code in the statistical software package R. The two objectives under this project collectively provided the student will useful field experiment and data analysis skills. How have the results been disseminated to communities of interest?Aspects of this work has been presented to both scientific agencies, such as the Entomological Society of America, and Ecological Society of America. In addition, this work has been presented to the local Ecological Restoration Society of Washington. Unfortunately, meeting cancellations and postponements due to COVID-19 prevent the dissemination of this project to more end-user groups during the project period. What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? In the first objective of the project, we quantified the spatial and temporal patterns in forest insect outbreaks in the Pacific Northwest over the last 6 decades (1960-2019). We were especially interested to understand if forest insect outbreaks in the region had become more intense and/or frequent over the study period. We used aerial detection survey data collected by the USDA Forest Service, the Canadian Forest Service, and the British Columbia Ministry of Forests. These data consisted of maps that characterize biotic and abiotic disturbance for each year. Using ArcGIS (Environmental Systems Research Institute, Redlands, CA) we recorded the area of insect disturbance areas within 5´5 km cells across the study region for each year and specific species, and within feeding guilds (i.e., all bark beetles, all folivores).We also recorded these values over a 10-year moving window. We used host tree data from rasterized tree species distributions at a 1km resolution to determine forested polygons suitable for biotic disturbance. To analyze the dataset, we used the ncf package the statistical software package R to measure spatial autocorrelation, and the temporal auto and cross-correlation. We also measured spatial auto- and cross-correlation through time for interacting species from between different guilds (i.e., folivores to bark beetles), and between specific insects from the same guild (i.e., Douglas-fir tussock moth and western spruce budworm) or different guild (i.e., Douglas-fir beetle and western spruce budworm) when interacting on the same host tree. Our analysis showed that the spatial extent of outbreaks by insect folivores, such as Douglas-fir tussock moth and western spruce budworm, has remained relatively constant over the entire study period; however, in recent decades, and especially beginning in 2000, there has greater local spatial autocorrelation in folivore outbreaks, suggesting a greater intensity in defoliation at local spatial scales. For bark beetle outbreaks, we detected both increases in the spatial extent of the outbreak, and increased intensity of tree mortality at local spatial scales, in recent decades (i.e., 2000-present) relative to prior decades (i.e., 1960-1990). Overall, this suggests that in both bark beetles and defoliators, the area damaged by each has become more concentrated at local spatial scales, while the overall area damaged by bark beetles during outbreaks has increased in recent years. We note that we observed these patterns in bark beetles when including or excluding areas damaged by the mountain pine beetle, which underwent an unprecedented outbreak between 2000-2012. Thus, this increase in the intensity and spatial extent of bark beetle outbreaks is not limited to mountain pine beetle. Both changes in climate and changes in forest structure are possible drivers of the changes in forest insect outbreak dynamics. In the second objective, we conducted a field-based study to quantify the role of stand conditions and natural enemies in affecting the population dynamics of Douglas-fir beetle and western spruce budworm, which are a representative bark beetle and folivore that feed on a common host tree (Douglas-fir). We used study sites previously established that were located west and east of the Cascade Mountains in Washington. These sites were (1) University of Washington Center for Sustainable Forestry at Pack Forest, Eatonville, WA (western Washington); (2) City of Seattle Cedar River Municipal Watershed, North Bend, WA (western Washington); Washington Department of Natural Resources, Middle Fork Snoqualmie Natural Resources Conservation Area, North Bend, WA (western Washington); (4) Washington Department of Natural Resources, North Mountain Area, Darrington, WA (western Washington), and (5) four sites within the Okanogan-Wenatchee National Forest; two sites near the Cle Elum, WA area and two sites near the Mazama, WA (eastern Washington). At each study site, we deployed Lindgren multifunnel traps baited with a Douglas-fir beetle lure and ethanol lure, and UNI-traps baited with a western spruce budworm lure to assess background population levels for each insect. We also felled trees and deployed Douglas-fir bolts at each site to measure Douglas-fir bark beetle natural enemies, many of which were also trapped in the Lindgren multifunnel traps. We were not able to deploy western spruce budworm larvae, as we proposed, for use in measuring their natural enemies, as the rearing lab that supplies life stages for this insect was unable to fulfill our order due to COVID-19. Thus, we instead deployed malaise traps in the vicinity of deployed UNI-traps to quantify its natural enemy community. Although we are still in process of taxonomically identifying natural enemies, a process that has been delayed due to COVID-19 and the inability to recruit undergraduate research assistants due to strict limits on the number of personnel allowed in the laboratory at a time, our preliminary analysis indicates that sites in eastern Washington, where outbreaks of both Douglas-fir beetle and western spruce budworm are common, have a much greater natural enemy presence in terms of both abundance and diversity. The natural enemy community for both pest insects is far reduced in western Washington, where outbreaks are rare. Thus, the natural enemy community does not appear to be the reason for the lack of outbreaks in western Washington, or the presence of outbreaks in eastern Washington. Rather, we hypothesize that stand conditions and especially climatic conditions in dry eastern sites, are driving the outbreak dynamics. Understanding the role that of the natural enemy community and stand condition play in the possible suppression of Douglas-fir beetle and western spruce budworm outbreaks informs and greatly enhances forest integrated pest management practices.

Publications

  • Type: Conference Papers and Presentations Status: Other Year Published: 2020 Citation: Pane, A.M., B.J. Harvey, A.L. Carroll, and P.C. Tobin (2020). Spatial patterns of forest insect outbreaks across the Pacific Northwest. Remote oral presentation at the Entomological Society of America conference.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2020 Citation: Pane, A.M., B.J. Harvey, A.L. Carroll, and P.C. Tobin (2020). Spatiotemporal dynamics of forest insect outbreaks across the Pacific Northwest. Remote oral presentation at the Ecological Society of America conference.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2020 Citation: Pane, A.M (2020). Trends in native forest insect pests; the Pacific Northwest as a case study. Remote oral presentation at the Ecological Restoration Symposium


Progress 09/16/20 to 09/15/21

Outputs
Target Audience:Over the course of the project, we have engaged forest health professionals from the City of Seattle, Washington State Department of Natural Resources, and the USDA Forest Service, who manage the lands on which field sites were located. Results of the project will specifically benefit forest insect pest management by identifying areas within Pacific Northwestern coniferous forests that are more (or less) vulnerable to forest insect outbreaks, and those areas that are more (or less) likely to be affected by multiple biotic disturbance agents over a relatively short time period. Changes/Problems:There were no major changes or problems encountered. Despite COVID-19, we were still able to access field sites though it did force the student funded on the project to work independently, which is not ideal when conducting field work. Check-in procedures and a field safety plan for working under COVID-19 were implemented and approved by the University of Washington prior to conducting field work to ensure student safety. Due to lab safety procedures due to COVID-19, the student was required to process sampled data from the field independently as it was not possible to recruit undergraduate help, which prolonged the processing of data. We also were unable to deploy western spruce budworm larvae as part of our second objective as the rearing lab that supplies life stages of this insect was not able to fulfill our order due to COVID-19. However, we were successfully able to use an alternate sampling method to measure the natural enemy community, which was a method based on prior research in this study system. What opportunities for training and professional development has the project provided?The project funded and provided training for a PhD Candidate (Alex Pane) during the penultimate year of his degree program. The student's career goal is to work as a scientist at a land managing government agency, such as the USDA Forest Service. Training activities under the project included the sampling efforts to measure populations of the Douglas-fir bark beetle, competitor wood boring beetles, and natural enemies across western and eastern Washington. In concert with these efforts included techniques that quantified stand structure and composition. Skills gained from the field components of the project included insect taxonomy. In addition, the student used a long-term dataset, collected from 1960-2019 over an area that included Oregon, Washington, and British Columbia, to investigate the spatial and temporal patterns in forest insect outbreaks based on historical aerial detection survey data. In this objective, the student gained valuable experience using ArcGIS and complete computer code in the statistical software package R. The two objectives under this project collectively provided the student will useful field experiment and data analysis skills. How have the results been disseminated to communities of interest?Aspects of this work has been presented to both scientific agencies, such as the Entomological Society of America, and Ecological Society of America. In addition, this work has been presented to the local Ecological Restoration Society of Washington. Unfortunately, meeting cancellations and postponements due to COVID-19 prevent the dissemination of this project to more end-user groups during the project period. What do you plan to do during the next reporting period to accomplish the goals? Nothing Reported

Impacts
What was accomplished under these goals? In the first objective of the project, we quantified the spatial and temporal patterns in forest insect outbreaks in the Pacific Northwest over the last 6 decades (1960-2019). We were especially interested to understand if forest insect outbreaks in the region had become more intense and/or frequent over the study period. We used aerial detection survey data collected by the USDA Forest Service, the Canadian Forest Service, and the British Columbia Ministry of Forests. These data consisted of maps that characterize biotic and abiotic disturbance for each year. Using ArcGIS (Environmental Systems Research Institute, Redlands, CA) we recorded the area of insect disturbance areas within 5´5 km cells across the study region for each year and specific species, and within feeding guilds (i.e., all bark beetles, all folivores).We also recorded these values over a 10-year moving window. We used host tree data from rasterized tree species distributions at a 1km resolution to determine forested polygons suitable for biotic disturbance. To analyze the dataset, we used the ncf package the statistical software package R to measure spatial autocorrelation, and the temporal auto and cross-correlation. We also measured spatial auto- and cross-correlation through time for interacting species from between different guilds (i.e., folivores to bark beetles), and between specific insects from the same guild (i.e., Douglas-fir tussock moth and western spruce budworm) or different guild (i.e., Douglas-fir beetle and western spruce budworm) when interacting on the same host tree. Our analysis showed that the spatial extent of outbreaks by insect folivores, such as Douglas-fir tussock moth and western spruce budworm, has remained relatively constant over the entire study period; however, in recent decades, and especially beginning in 2000, there has greater local spatial autocorrelation in folivore outbreaks, suggesting a greater intensity in defoliation at local spatial scales. For bark beetle outbreaks, we detected both increases in the spatial extent of the outbreak, and increased intensity of tree mortality at local spatial scales, in recent decades (i.e., 2000-present) relative to prior decades (i.e., 1960-1990). Overall, this suggests that in both bark beetles and defoliators, the area damaged by each has become more concentrated at local spatial scales, while the overall area damaged by bark beetles during outbreaks has increased in recent years. We note that we observed these patterns in bark beetles when including or excluding areas damaged by the mountain pine beetle, which underwent an unprecedented outbreak between 2000-2012. Thus, this increase in the intensity and spatial extent of bark beetle outbreaks is not limited to mountain pine beetle. Both changes in climate and changes in forest structure are possible drivers of the changes in forest insect outbreak dynamics. In the second objective, we conducted a field-based study to quantify the role of stand conditions and natural enemies in affecting the population dynamics of Douglas-fir beetle and western spruce budworm, which are a representative bark beetle and folivore that feed on a common host tree (Douglas-fir). We used study sites previously established that were located west and east of the Cascade Mountains in Washington. These sites were (1) University of Washington Center for Sustainable Forestry at Pack Forest, Eatonville, WA (western Washington); (2) City of Seattle Cedar River Municipal Watershed, North Bend, WA (western Washington); Washington Department of Natural Resources, Middle Fork Snoqualmie Natural Resources Conservation Area, North Bend, WA (western Washington); (4) Washington Department of Natural Resources, North Mountain Area, Darrington, WA (western Washington), and (5) four sites within the Okanogan-Wenatchee National Forest; two sites near the Cle Elum, WA area and two sites near the Mazama, WA (eastern Washington). At each study site, we deployed Lindgren multifunnel traps baited with a Douglas-fir beetle lure and ethanol lure, and UNI-traps baited with a western spruce budworm lure to assess background population levels for each insect. We also felled trees and deployed Douglas-fir bolts at each site to measure Douglas-fir bark beetle natural enemies, many of which were also trapped in the Lindgren multifunnel traps. We were not able to deploy western spruce budworm larvae, as we proposed, for use in measuring their natural enemies, as the rearing lab that supplies life stages for this insect was unable to fulfill our order due to COVID-19. Thus, we instead deployed malaise traps in the vicinity of deployed UNI-traps to quantify its natural enemy community. Although we are still in process of taxonomically identifying natural enemies, a process that has been delayed due to COVID-19 and the inability to recruit undergraduate research assistants due to strict limits on the number of personnel allowed in the laboratory at a time, our preliminary analysis indicates that sites in eastern Washington, where outbreaks of both Douglas-fir beetle and western spruce budworm are common, have a much greater natural enemy presence in terms of both abundance and diversity. The natural enemy community for both pest insects is far reduced in western Washington, where outbreaks are rare. Thus, the natural enemy community does not appear to be the reason for the lack of outbreaks in western Washington, or the presence of outbreaks in eastern Washington. Rather, we hypothesize that stand conditions and especially climatic conditions in dry eastern sites, are driving the outbreak dynamics. Understanding the role that of the natural enemy community and stand condition play in the possible suppression of Douglas-fir beetle and western spruce budworm outbreaks informs and greatly enhances forest integrated pest management practices.

Publications

  • Type: Conference Papers and Presentations Status: Other Year Published: 2020 Citation: Pane, A.M., B.J. Harvey, A.L. Carroll, and P.C. Tobin (2020). Spatial patterns of forest insect outbreaks across the Pacific Northwest. Remote oral presentation at the Entomological Society of America conference.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2020 Citation: Pane, A.M., B.J. Harvey, A.L. Carroll, and P.C. Tobin (2020). Spatiotemporal dynamics of forest insect outbreaks across the Pacific Northwest. Remote oral presentation at the Ecological Society of America conference.
  • Type: Conference Papers and Presentations Status: Other Year Published: 2020 Citation: Pane, A.M (2020). Trends in native forest insect pests; the Pacific Northwest as a case study. Remote oral presentation at the Ecological Restoration Symposium


Progress 09/16/20 to 09/30/20

Outputs
Target Audience: Nothing Reported Changes/Problems: Nothing Reported What opportunities for training and professional development has the project provided?Initial training of the PhD student occurred during the 2-week reporting period. How have the results been disseminated to communities of interest? Nothing Reported What do you plan to do during the next reporting period to accomplish the goals?The funded project will be completed during the next reporting year. This includes both Objective 1, using historical aerial detection survey data to measure changes in spatial synchrony and forest insect outbreak periodicity over time, as well as Objective 2, quantifying the role of natural enemies in affecting the population dynamics of Douglas-fir beetle and western spruce budworm in eastern and western Washington Douglas-fir stands.

Impacts
What was accomplished under these goals? The PhD student funded to work on this project, Alex Pane, wasintroduced to the project and project goals during the 2-week reporting period.

Publications