Progress report for GNE22-282
Project Information
The recent reintroduction of industrial hemp (Cannabis sativa L.) as a crop for food, grain, oil and fiber in Pennsylvania has provided an opportunity for farmers to expand their operations to include this high-value commodity. While projected benefits from the National Hemp Association for job creation, rural economic growth and annual financial gains are impressive, there is much we need to know about this crop to ensure its success in the Pennsylvania farmscape. In particular, insect pests are of global concern in agriculture, contributing to significant crop losses annually. Due to the novelty of this crop and the strict regulations on pesticidal inputs, it becomes fundamentally important to provide information about insect pests that could contribute to crop losses. These losses can be caused both directly, through pests consuming plants, and indirectly by contributing to disease transmission and altering plant metabolites which could affect yield and profitability. Finally, we must also understand the extent to which native biological control agents (predatory arthropods and parasitoids) act to regulate pest insects. To increase our basic understanding of the system and contribute to the development of sustainable control strategies, this project will: 1) Determine the composition of insect pests and biological control agents throughout the crop growing cycle; 2) Evaluate the impact of insect pests on plant defensive metabolites and yield; and 3) Evaluate the efficacy of biological control agents on pest management. Together, this work will provide information that supports decision-making and the development of sustainable control strategies in industrial hemp.
- Determine the composition of insect pests and biological control agents throughout the crop growing cycle in Pennsylvania.
Essential to our success in developing integrated pest management strategies in novel cropping systems is our understanding of the organisms that interact with the crop plant. I will determine not only what pest species are common on industrial hemp plants, but also what biological control agents (predators and parasitoids) utilize these plants to find prey resources on three commonly grown hemp cultivars (cv. Joey, Henola and Bialobrzeskie). In doing this, we can start to build a pest management framework that catalogs our pests throughout the growing period and the potential for biological control to mitigate their damage. Importantly, this will fill an immense knowledge gap that exists in the Northeastern region.
- Evaluate the impact of insect pests on plant defensive metabolites in three industrial hemp cultivars.
Insect pests can contribute to dramatic plant defoliation in cropping systems, leading to crop loss. I will evaluate the damage that common pests on industrial hemp cause and assess how feeding by herbivorous pests might affect plant defenses, which could contribute to crop loss through increased plant metabolites that are federally regulated (THC, Tetrahydrocannabinol). The federal government strictly regulated the level of THC in industrial hemp to a level below 0.03% and testing crop plants is required of farmers before harvest. If plants exhibit THC levels > 0.03%, then the entire crop must be destroyed as it is then considered a Schedule 1 Drug. Understanding which pests induce high levels of THC at which phenological stages is essential for farmers so they can avoid devastating loss of income and livelihood. By understanding these dynamics, we can begin to forecast and predict when THC levels might increase based on pests present in the system, the cultivar of hemp being grown, and the time of season.
- Evaluate the efficacy of biological control agents on pest management.
The value of beneficial biological control agents can contribute tremendously to pest management. Because pesticidal input is limited in industrial hemp, I will assess the efficacy of common biological control agents in reducing populations of target pests identified in Objective 1. We can use this information to conserve or augment biological control agents in hemp farms to achieve pest control.
The purpose of this project is to determine the community of insect pests on industrial hemp, elucidate their impact on this high-value commodity, and develop an understanding of how pest management can be achieved in this new system.
In Pennsylvania, industrial hemp is a novel crop; the state government distributed the first commercial grow permits in 2019. Though the expansion of industrial hemp in Pennsylvania is relatively new, crop acreage has been increasing. During 2021, planted area for fiber, seeds, grain, CBD and oils reached over 350 acres (National Agricultural Statistics Service - NASS 2022) and is expected to rise in the coming years. The versatility of this crop and the high value of hemp products has increased the interest of farmers who seek alternative crops to increase their income and livelihood.
Like all plants, hemp hosts a variety of arthropod herbivores that have the potential to become important pests. Evidence of the diversity of insect pests in this crop is mounting with ~20 recognized herbivorous pests identified, including generalist herbivores such as the corn earworm, tarnished plant bug, hemp russet mite, and specialist herbivores such the cannabis aphid (Schreiner and Cranshaw 2020; Ajayi and Samuel-Foo 2021). However, current pest lists come largely from Southern and Western United States. Because Pennsylvania farmers have only been growing hemp for 3 years, there is much to learn about this system, including what pests will be found that represent a threat for hemp production and the income of farmers. Additionally, novel crops like hemp face extensive restrictions in terms of pesticidal input as they wait for safety and efficacy research results on various chemicals. It is clear that alternative management strategies, like biological control, will be essential for the success of this crop and the development of those strategies relies on an intimate understanding of the pests present.
This project will advance our current knowledge and benefit sustainable agriculture by determining not only the herbivorous pests found in industrial hemp fields in Pennsylvania, but also by evaluating how insect pests damage the plants in ways that impact yield directly – via feeding – or indirectly, by altering important and highly regulated plant metabolites like THC (Tetrahydrocannabinol), which if upregulated can lead the plant to “go hot”, a term used to describe a plant that exceeds the legal limit of THC (0.03%). If this happens, the farmer must then destroy the crop in its entirety which would be a devastating financial loss. Every year, an estimated 20% of hemp farms in the U.S. are non-compliant with THC levels which represents a challenge that we must understand in Pennsylvania (Cowee 2019).
Altogether, the results of this study will allow us to begin defining a sustainable integrated pest management plan for farmers growing this novel crop, that is specific to our region, by revealing important pests and their seasonality through crop stages, their influence on crop health, important plant metabolites (THC) and the potential for predatory insects and parasitoids to manage pest populations via biological control.
Research
1. Determine the composition of insect pests and biological control agents throughout the crop growing cycle in Pennsylvania
To evaluate the community of arthropod organisms in industrial hemp, weekly sampling of the herbivorous insects and potential biological control agents (predators and parasitoids) will be taken in 10 commercial plantings of industrial hemp across Pennsylvania. Sampling will take place throughout the growing season, from first sign of vegetation until harvest (~June – Oct). Sampling throughout the season will allow us to determine pest and biological control agent population fluctuations over time. The industrial hemp farms chosen will represent commercial farming practices, be geographically distinct from one another, and contain our three hemp varieties of interest (cv. Joey, Henola, and Bialobrzeskie). During each sampling, 30 plants per farm will be visually surveyed, counted, and all arthropods present on the plant will be recorded and collected for further identification. Collected individuals will be captured manually, with buccal aspirator or net, and transferred to the Lab of Arthropod Ecology and Trophic Interactions at Penn State for identification, pinning and kept as vouchers. All individuals collected will be identified to the functional group, family level and where is possible to genus or species level using taxonomic keys. In addition to visual sampling, yellow sticky traps and pitfall traps will be used to sample aerial and ground arthropods, respectively. Pitfalls and sticky traps will be changed out weekly. Plant height and phenology at each farm will be recorded, and plant tissue will be reserved from candidate individuals at the beginning (vegetative state), middle (flowering) and end of season (post-flowering) for plant metabolite analysis. Landscape and habitat context data (habitat type, acreage of farm, age of farm, other crops adjacent, evidence of insect damage on plants, weather conditions) will also be collected for each of the sites.
I will explore and visualize similarities or dissimilarities of the community composition between the three hemp cultivars, crop stages and locations using PCoA (Principle Coordinates Analysis) and will statistically assess the differences in community composition using PERMANOVA for both pests and biological control agents. This will allow us to determine if one cultivar harbors more or fewer pests or beneficial biological control agents than others, if plant phenology influences insect community composition, and if insect community composition is consistent over geographic space.
In addition, this observational survey will result in a table that consists of all the pests and beneficial biological control agents in Pennsylvania industrial hemp, the seasonality of herbivore pests throughout the crop cycle and the description of pest damage, which I will turn into an extension bulletin for growers in our state.
2. Evaluate the impact of insect pests on plant defensive metabolites and yield in three industrial hemp cultivars
Understanding how insect pests alter plant defenses in industrial hemp is crucial to ensure minimal crop losses and expanding our knowledge of insect-plant interactions in this new farming system. Direct consumption of leaf material and floral buds can directly affect yield by diminishing plant resources and eliminating marketable portions of the plant. Insect herbivory is also known to affect a myriad of plant traits, including plant metabolites. While these changes typically have no true influence in crop production, modification of plant metabolites in industrial hemp could be devastating for farmers. This is because industrial hemp is federally regulated and one particular metabolite, Tetrahydrocannabinol (THC), must remain under the threshold of 0.03%. If during the required testing a farmer’s crop is found above the 0.03% threshold, they must destroy the crop in its entirety – leading to a complete loss of revenue. Recent work suggests that herbivory by the corn earworm, Helicoverpa zea, can increase levels of THC above legal limits in some varieties of hemp grown for CBD (Jackson et al. 2021), highlighting the importance of understanding these dynamics across commonly grown hemp cultivars (Jackson et al. 2021). This early work suggests that hemp cannabinoids may act as defensive compounds and it is suspected that other herbivorous pest can similarly alter the levels of these important compounds. Further research will be needed to understand the potential impact of the different insect pest and natural enemies present in Pennsylvania hemp varieties.
Here I hypothesize that pest damage will induce plant defenses in industrial hemp that will change the composition and concentration of plant metabolite compounds, and that the impact of herbivory on plant defense may differ based on the plants phenological stage (vegetative, flowering, post-flowering).
To evaluate these hypotheses, I will measure chlorophyll content as proxy for plant health and yield and cannabinoids to understand the influence of herbivory on plant metabolites such as THC. Experiments will be done on the three aforementioned hemp cultivars which will be exposed to pest insects (infested treatment) or pest-free (non-infested treatment) during the various phenological stages (vegetative, flowering and post-flowering). I will focus on two major pests of industrial hemp that are projected to be problematic in this system: the cannabis aphid (Phorodon cannabis) and the corn earworm (Helicoverpa zea) (Lagos-Kutz et al. 2018; Ajayi and Samuel-Foo 2021). A colony of P. cannabis was established in the Arthropod Ecology and Trophic Interactions Lab in 2021 and a colony of H. zea will be field collected or purchased commercially and established in the laboratory.
The three commercial varieties of hemp will be grown in a walk-in growth chamber (24C, 18:4 L:D photoperiod) for three weeks before running the experiment. The infested treatment will receive 5 pest individuals, either P.cannabis aphids or H. zea larvae, inoculated at either the vegetative stage, flowering stage or the post-flowering stage, whereas the non-infested controls will remain pest-free. Vegetative infestation will occur three weeks after planting, growth (n=20), flowering infestation will occur once flower buds appear (n=20), and post-flowering infestation will occur once flowers senesce, and seed set begins (n=20). At each phenological stage, I will also have 20 non-infested control plants (N=120 experimental plants / pest species / cultivar).
Photosynthesis measurements will be taken with a fluorometer three days post-infestation on the uppermost extended leaves to assess chlorophyll content of the plant when experiencing herbivory by insect pests. On the same day, the composition and concentration of cannabinoid compounds, including Cannabidiol (CBD), Cannabiniol (CBN) and THC, will be evaluated using High Performance Liquid Chromatography (HPLC) in the Center for Chemical Ecology Core Facility at Penn State. Sample leaves will be taken from each plant, 3-days post infestation, from the uppermost developed leaves. For the extraction of Cannabinoids, leaf tissue will be flash frozen with liquid nitrogen and stored at -80 °C until further processed. Processing will begin with leaf tissue ground using a Geno/Grinder 2000 (SPEX Sample Prep, Metuchen, NJ) with 6mm stainless steel balls under cryogenic conditions. A 100 mg aliquot of this ground tissue will then be transferred to a 2 mL microcentrifuge tube containing 0.6 g of 2 mm zirconia beads and will receive 1.5 mL of extraction solvent consisting of ethanol with 2 mg/mL 4-biphenyl carboxylic acid (BPCA) as an internal standard. Samples will then be homogenized for 6 minutes using a FastPrep homogenizer (MP Biomedicals) and then centrifuged for 5 min at 10,000 rpm. An aliquot of the supernatant will then be removed and filtered through a 0.2 µm syringe filter for analysis by HPLC.
HPLC Analysis of Cannabinoids: Cannabinoids present in the leaf extracts will be separated using 5 µL injections onto a Shimadzu Prominence HPLC system fitted with a reverse-phase Restek Raptor ARC-18 column (150 mm x 4.6 mm x 2.7 µm) maintained at 40 °C with a flow rate of 1.5 mL-min. Mobile phase A will consist of HPLC-grade water with 5 mM ammonium formate and 0.1% formic acid; mobile phase B will be HPLC-grade acetonitrile with 0.1% formic acid. An isocratic hold for 7 min at 77% B will be followed by a linear gradient to 95% B over 2 min, a 1 min hold at 95% B, and then a 4 min re-equilibration at 77% B. Full spectra will be recorded from 190-400 nm by UV-DAD, with quantification at 228 nm using relative responses to the internal standard and external calibration to neutral and carboxylate cannabinoid standards of cannabidvarin (CBDV and CBDVA), cannabidiol (CBD and CBDA), cannabigerol (CBG and CBGA), tetrahydrocannabivarin (THCV and THCVA), cannabichromene (CBC and CBCA), as well as cannabinol (CBN), ∆9-tetrahydrocannabinol (∆9-THC), ∆8-tetrahydrocannabinol (∆8-THC), tetrahydrocannabinolic acid A (THCA-A), Cerilliant (Round Rock, TX)
The concentration of chlorophyll and the main cannabinoids (THC, CBN, CBD) will be assessed as a function of treatment, pest species, and cultivar using generalized linear models. The results will illustrate the potential impact of two pest species on plant defensive chemistry at different plant stages. Importantly, this study will provide insight into whether herbivory by these herbivorous pests could render the crop unmarketable by increasing THC levels.
3. Evaluate the efficacy of biological control agents on pest management
Functional response tests will be performed on colony-reared P. cannabis and H. zea and generalist predators to explore the efficiency of these predators as density-dependent mortality factors. For each pest, an appropriate predator was chosen based on ubiquity across the Pennsylvania landscape and the propensity to consume the prey. The lady beetle, Harmonia axyridis, a generalist predator well known for its capacity to feed on several species of aphids will be used in trials with P. cannabis. Podisus maculiventris, a generalist stink bug predator, will be used in experiments with H. zea as it is commonly found feeding on lepidopteran larvae. Colonies of both of H. axyridis and P. maculiventris have been established in the Arthropod Ecology and Trophic Interactions lab since 2019, adding wild-caught individuals annually, and will be used in the experiments.
To evaluate the predation potential of each of these predators, four life stages of H. axyridis, first instar, second instar, third instar, adult female and male will be evaluated by exposing them to different number of prey aphids (10, 20, 40, 80, 100). Three larval stages (2nd, 3rd, 4th) as well as the adult stage of P. maculiventris will exposed to H. zea larvae at various densities (1, 3, 5, 7, 10). Predators will be isolated in 16 oz deli cups and starved for 24 h prior to experiments. Experiments will begin at the same time every day, beginning once a predator is introduced into the experimental arena. The experimental arena will consist of fresh hemp leaves, placed on moistened filter paper in petri dishes and infested with different number of P. cannabis or H. zea. Predators will be removed from arenas after 24 h with no prey replacement occurring during the experiment.
The experiment will be replicated 10 times in a randomized complete block design with ten blocks representing time and five treatments. A one-way analysis of variance (ANOVA) will be used to compare differences in the mean attack rate (prey remaining after 24 hours) at each prey density. A t-test will then be used to compare average predation rates between sexes and instars of each predator. Consumer-resource interactions (i.e. the functional response) will be evaluated in R Core Team (2020) where selecting, fitting and comparing functional response models will be done using the package “FRAIR”.
- The composition of insect pests and biological control agents throughout the crop growing cycle in Pennsylvania.
The evaluation of the arthropod community within industrial hemp fields throughout the 2022 growing season, was conducted weekly in seven commercial plots situated across six counties in the Central and Southeastern regions of Pennsylvania. Four plots grew industrial hemp for fiber and grain production while the remaining three farms grew hemp for CBD extracts. The selected plots contained either individual varieties or a mix of varieties within the same plot, depending on the growers' preferences. The number of samplings conducted at each farm varied based on harvest time (See Table 1).
To enhance the scope of our research, we conducted a second year of insect sampling throughout the 2023 growing season in the Central and Southeastern counties of Pennsylvania. We included twenty individual variety plots established within two experimental and three commercial farms to explore variations in the insect community composition among cultivars, locations, and hemp types. This expansion increased the number of sampling sites and reduced the sampling frequency, enabling a more comprehensive collection of samples across geographic areas. At each of the experimental farms, we selected the same six fiber/grain varieties for surveying, resulting in a total of 12 sampling sites. In the commercial farms, we had no control over variety matching among locations, six plots were established with different CBD cultivars, while 2 of the plots featured fiber varieties (See Table 2).
Table 1. Location of field sites, hemp type, and number of samplings conducted during the 2022 insect surveys in Pennsylvania hemp crops.
Site |
Location |
County |
Hemp type |
Variety |
Number of samplings |
1. Shaffer Farm |
Central PA |
Clearfield |
CBD |
Stormy Daniels |
11 |
2. Lazy Moon |
Central PA |
Blair |
CBD CBG |
Mix Hawaiian Haze and White |
14 |
3. Russell E. Larson Agricultural Research Center |
Central PA |
Center |
CBD |
Mix of varieties |
10 |
4. Russell E. Larson Agricultural Research Center |
Central PA |
Center |
Fiber/grain |
Sour kush, OG |
9 |
5. Coexist |
Southeast PA |
Berks |
Fiber |
Bialobrzesky |
7 |
6. Cedar Meadow Farm |
Southeast PA |
York |
Fiber/grain |
Henola, Yuma |
10 |
7. Southeast Agricultural Research and Extension Center |
Southeast PA |
Lancaster |
Fiber |
Bialobrzesky |
9 |
Table 2. Location of field sites, hemp type, and number of samplings conducted during the 2023 insect surveys in Pennsylvania hemp crops.
Site |
Location |
County |
Purpose |
Hemp Type |
Variety Plot |
Number Of Samplings |
1. Rhodes Farm |
Central PA |
Clinton |
Commercial |
CBD |
1. Merlot 2. Box 3. Trinity |
7 |
2. Russell E. Larson Agricultural Research Center |
Central PA |
Center |
Experimental |
Fiber |
1. Bialobrzesky 2. Carmenecta 3. Fedora 17 4. Futura 83 5. Henola 6. Orion 33 |
5 |
3. Southeast Agricultural Research And Extension Center |
Southeast PA |
Lancaster |
Experimental |
Fiber |
1. Bialobrzesky 2. Carmenecta 3. Fedora 17 4. Futura 83 5. Henola 6. Orion 33 |
5 |
4. Cedar Meadow Farm |
Southeast PA |
York |
Commercial |
Fiber
CBD
|
1. Yuma S 2. Green Cherry 3. Hawaiian Haze 4. Fifth Element |
5
7
|
5. Coexist |
Southeast PA |
Berks |
Commercial |
Fiber |
1. Bialobrzesky |
5 |
Insect survey 2022:
During the visual sampling conducted in the 2022 growing season, 20,915 arthropods were recorded and identified including both insects and arachnids. This diverse group of arthropods was systematically classified into 10 orders, 42 families, 62 morphospecies, and a separate category for unclassified insects. Hemiptera, Coleoptera, Thysanoptera, Araneae, Diptera, and Hymenoptera were the most predominant orders among the specimens observed, encompassing both herbivores and natural enemies (Table 3). When categorized by functional groups, herbivore insects emerged as the most abundant group representing 90% of the specimens collected, followed by natural enemies with 9% of representation, while incidental species accounted for 1% and pollinators contributed to less than 1% (Fig 1)
Table 3. Summary of specimens observed during the 2022 visual sampling in hemp crops across Pennsylvania, classified by orders, families, and morphospecies.
Order |
Families |
Morphospecies |
Number of specimens |
HEMIPTERA |
10 |
17 |
17,469 |
COLEOPTERA |
8 |
16 |
1,200 |
THYSANOPTERA |
2 |
5 |
751 |
ARANEAE |
5 |
5 |
429 |
DIPTERA |
6 |
7 |
277 |
HYMENOPTERA |
3 |
3 |
263 |
LEPIDOPTERA |
4 |
5 |
155 |
NEUROPTERA |
1 |
1 |
104 |
ORTHOPTERA |
2 |
2 |
82 |
OPILIONES |
1 |
1 |
47 |
Unclassified Insects |
- |
- |
138 |
Total |
42 |
62 |
20,915 |
Herbivore Insects
Within the herbivorous pest category, Aphididae (aphids), Thripidae (thrips), Chrysomelidae (leaf beetles), Cicadellidae (leafhoppers), Pentatomidae (stink bus), and Miridae (plant bugs) were the insect families with the largest number of specimens observed (Table 4). Aphids, particularly the cannabis aphid (P. cannabis), emerged as predominant pests, constituting 86% of the herbivore species feeding on hemp. These sap-sucking insects were detected in both CBD and fiber crops since the vegetative phase of the crops and were commonly present in the sampling sites across central and southeast counties of Pennsylvania. In the case of fiber cultivars, aphid populations were higher during the flowering stage while conversely, for CBD hemp, there was a population decline during the flowering period, followed by a substantial surge throughout the post-flowering stage until the harvest. Typically, the production cycle for CBD is longer than for fiber resulting in an extended period of vulnerability for CBD plants where aphid infestations can be problematic, highlighting the importance of understanding their impact on crop yield and plant metabolites such as THC (Table 5).
Table 4. List of herbivore insects and their relative abundance observed during the 2022 visual sampling in CBD and fiber hemp crops across Pennsylvania field sites.
Insect pest |
Orden |
Family |
CBD Hemp |
Fiber Hemp |
Total Hemp |
Relative Abundance |
Aphids |
HEMIPTERA |
Aphididae |
14833 |
1295 |
16128 |
85.897 |
Thrips |
THYSANOPTERA |
Thrypidae |
478 |
228 |
706 |
3.760 |
Leaf Beetles |
COLEOPTERA |
Chrysomelidae |
428 |
97 |
525 |
2.796 |
Leaf Hoppers |
HEMIPTERA |
Cicadellidae |
297 |
44 |
341 |
1.816 |
Stink Bugs |
HEMIPTERA |
Pentatomidae |
176 |
100 |
276 |
1.470 |
Non Classified Bugs |
HEMIPTERA |
Other herbivore hemipterans |
71 |
146 |
217 |
1.156 |
Plant Bugs |
HEMIPTERA |
Miridae |
68 |
46 |
114 |
0.607 |
Grasshoppers |
ORTHOPTERA |
Acrididae |
75 |
2 |
77 |
0.410 |
Herbivore Beetles |
COLEOPTERA |
Other herbivore coleopterans |
50 |
21 |
71 |
0.378 |
Caterpillars |
LEPIDOPTERA |
Other Caterpillars |
25 |
40 |
65 |
0.346 |
Japanese Beetles |
COLEOPTERA |
Scarabaeidae |
2 |
54 |
56 |
0.298 |
Geometrid Moths |
LEPIDOPTERA |
Geometridae |
39 |
0 |
39 |
0.208 |
Tiger Moths |
LEPIDOPTERA |
Arctidae |
34 |
1 |
35 |
0.186 |
White Flies |
HEMIPTERA |
Aleyrodidae |
30 |
0 |
30 |
0.160 |
Leaf Miners |
DIPTERA |
Agromyzidae |
29 |
0 |
29 |
0.154 |
Frog Hoppers |
HEMIPTERA |
Cercopidae |
16 |
0 |
16 |
0.085 |
Corn Earworms |
LEPIDOPTERA |
Noctuidae |
12 |
2 |
14 |
0.075 |
Tree Hoppers |
HEMIPTERA |
Membracidae |
12 |
1 |
13 |
0.069 |
Weevils |
COLEOPTERA |
Curculionidae |
10 |
1 |
11 |
0.059 |
Click Beetles |
COLEOPTERA |
Elateridae |
5 |
1 |
6 |
0.032 |
Fruit Flies |
DIPTERA |
Thephritidae |
4 |
1 |
5 |
0.027 |
Moths |
LEPIDOPTERA |
Erebidae |
2 |
0 |
2 |
0.011 |
|
Total |
16696 |
2080 |
18776 |
100 |
The second most prevalent group of herbivores found in hemp crops were thrips comprised mainly of three generalist species: onion thrips (Thrips tabacci), western flower thrips (Frankliniella sp.), and soybean thrips (Neohydratothrips sp.). These rasping-sucking insects extract cell contents from the leaves producing punctures and scraping signs that may affect the appearance of the foliage and render the plant susceptible to pathogens (Gill et al. 2015). Thrips can overwinter in the soil, plant debris, or weeds and were observed causing potential impacts in hemp crops beginning in the early vegetative stage.
Various chrysomelid species, including flea beetles from the genus Altica sp. And Crepidodera sp., along with cucumber beetles (Diabrotica undecimpunctata), were more abundant in CBD than in fiber varieties and were frequently observed chewing small holes in the foliage throughout the flowering stage of the crops. Among the hemipterans, leafhoppers, stink bugs, and plant bugs (Lygus sp.) represented the most prevalent families within this insect group. Although no significant damage was observed in the crops, leafhoppers might pose a threat to hemp since reports have associated them with plant virus transmission in Colorado and Arizona states (Giladi et al. 2020; Hu et al. 2021; Stats et al. 2023). Other species like Japanese beetles (Popillia japonica) were less abundant but when present, they were observed causing significant defoliation and skeletonization in fiber/ grain cultivars which could lead to reduced photosynthetic capacity of the plant and reduced crop yield. They were also observed in mating aggregations on male flowers, suggesting that hemp could become a hospitable host for these damaging beetles. Japanese beetles can feed on a wide variety of plants and are commonly present across the Eastern United States. During the 2022 growing season, the corn earworm (Helicoverpa zea), recognized as a significant pest for hemp crops, did not exhibit any notable impact due to its low abundance (Tables 4 and 5).
Table 5. The abundance of the most common insect pests throughout the crop growing cycle during the 2022 visual sampling of CBD and fiber hemp across Pennsylvania.
Insects Pest |
Damage Type |
Hemp Type |
Vegetative stage |
Flowering stage |
Post-flowering stage |
Aphids |
Piercing-Sucking |
CBD |
1242 |
731 |
12860 |
Fiber |
154 |
645 |
496 |
||
Thrips |
Scraping and Piercing-Sucking |
CBD |
104 |
217 |
157 |
Fiber |
167 |
33 |
28 |
||
Flea Beetles |
Chewing |
CBD |
76 |
211 |
93 |
Fiber |
45 |
31 |
20 |
||
Cucumber Beetles |
Chewing |
CBD |
4 |
14 |
30 |
Fiber |
0 |
0 |
1 |
||
Leaf Hoppers |
Piercing-Sucking |
CBD |
63 |
164 |
70 |
Fiber |
10 |
31 |
3 |
||
Stink Bugs |
Piercing-Sucking |
CBD |
2 |
53 |
121 |
Fiber |
1 |
14 |
85 |
||
Plant Bugs |
Piercing-Sucking |
CBD |
28 |
21 |
19 |
Fiber |
10 |
22 |
14 |
||
Japanese Beetles |
Chewing |
CBD |
2 |
0 |
0 |
Fiber |
30 |
22 |
2 |
||
Grasshoppers |
Chewing |
CBD |
6 |
31 |
38 |
Fiber |
1 |
1 |
0 |
||
Corn Earworm |
Chewing |
CBD |
0 |
0 |
12 |
Fiber |
1 |
0 |
1 |
Natural Enemies
Among the predominant families of natural enemies, Coccinellidae (lady beetles) constituted 28% of the total observed predators, showcasing a diverse assembly of native species such as the pink lady beetle (Coleomegilla maculata) and the 14-Spot lady beetle (Propylea quatuordecimpunctata). Additionally, the introduced Multicolored Asian lady beetle (Harmonia axyridis) was abundantly represented in our samples. All these ladybeetle species are generalist predators, feeding on a variety of insect pests and arthropods including aphids, scale bugs, mites, small larvae, and insect eggs. Collectively, the spider families Thomicidae (carb spiders), Salticidae (jumping spiders), Araneidae (orb weaver spiders), Cheiracanthiidae (sac spiders), and Opiliones (harvestmen) contributed to an additional 26% of the total natural predator population. Their abundance and diversity highlight their important role in the regulation and stability of ecosystems due to their multiple ecological functions. Minute pirate bugs (Athocoridae) ranked as the third most crucial general predator, constituting 14% of beneficial control agents. These voracious insects were observed throughout the entire hemp growing season preying on thrips and aphids. Ants (Formicidae), hoverflies (Syrphidae), lacewings (Chrysopidae), and different families of parasitic wasps were equally represented in terms of relative abundance (Table 6). In the group of parasitic wasps, we found the first specimens of Aphelinus maculatus reported for Pennsylvania attacking P. cannabis. Overall, CBD hemp exhibited higher individual abundance across these species compared to fiber/grain cultivars. The presence of these beneficial arthropods holds promising implications for biological control in this new crop system with their potential to mitigate the impact of detrimental herbivores. Moreover, their representation serves as valuable indicators of ecosystem health, fostering the adoption of sustainable farming practices.
Table 6. Total and relative abundance of predator families observed during the 2022 visual sampling in CBD and fiber hemp crops across Pennsylvania.
Order |
Family |
Natural enemy |
CBD Hemp |
Fiber Hemp |
Total Hemp |
Relative Abundance |
COLEOPTERA |
Coccinellidae |
Lady beetles |
401 |
124 |
525 |
28.47 |
HEMIPTERA |
Anthocoridae |
Minute Pirate Bugs |
155 |
115 |
270 |
14.64 |
ARANEAE |
Thomicidae, Salticidae, Araneidae, Cheiracanthiidae, Opiliones and Other Spiders |
Spiders and Harvestmen |
393 |
83 |
476 |
25.81 |
HYMENOPTERA |
Formicidae |
Ants |
86 |
40 |
126 |
6.83 |
DIPTERA |
Syrphidae |
Hoover Flies |
109 |
5 |
114 |
6.18 |
HYMENOPTERA |
Parasitic Wasps |
Parasitic Wasps |
97 |
17 |
114 |
6.18 |
NEUROPTERA |
Chrysopidae |
Lacewings |
95 |
9 |
104 |
5.64 |
THYSANOPTERA |
Aeolothripidae |
Predatory Thrips |
14 |
31 |
45 |
2.44 |
HEMIPTERA |
Pentatomidae |
Predatory Stink Bug |
37 |
0 |
37 |
2.01 |
HEMIPTERA |
Nabidae |
Damsel Bugs |
22 |
0 |
22 |
1.19 |
HEMIPTERA |
Reduviidae |
Wheel Bugs |
4 |
1 |
5 |
0.27 |
COLEOPTERA |
Lampiridae |
Fireflies |
4 |
0 |
4 |
0.22 |
COLEOPTERA |
Staphilinidae |
Rove Beetles |
1 |
0 |
1 |
0.05 |
COLEOPTERA |
Carabidae |
Carabids |
1 |
0 |
1 |
0.05 |
Total |
1419 |
425 |
1844 |
100 |
We used non-metric multidimensional scaling - NMDS to visualize differences in the communities of arthropods on hemp plantings. First, we visualized observed communities across each sampled field site (Figure 2). While each site seems to have distinct communities, there are a few that overlap (CBD plots). From this, we visualized the communities of organisms by hemp type and see that the community composition is distinct between fiber and CBD (Figure 3). These dissimilarities in insect communities were assessed between the two types of hemp cultivars using the permutational multivariate analysis of variance (PERMANOVA). The analysis revealed that the composition of insect species significantly varied between CDB and fiber crops (F= 8.5261, p=0.001). Because the communities of arthropods across our fiber plots did not overlap, we ran a PERMANOVA which revealed that they are indeed significantly different from one another (F= 5.6232, p=0.001), indicating that other factors are shaping the insect communities between those sample sites (Fig. 3).
The Shannon-Weiner Diversity Index was computed for the arthropod functional group (herbivores versus natural enemies) and hemp type, revealing a higher diversity and more even distribution of herbivore species in fiber hemp (4.168) compared to CBD hemp (1.813). Conversely, in the predator group, a greater diversity of species was observed in CBD hemp (10.07) compared to fiber hemp (6.247) (See Table 7). In summary, for both types of hemp, natural enemy communities demonstrated greater diversity and more balanced distribution compared to insect pests.
Table 7. Total Shannon- Weiner Diversity Index for insect functional groups observed in CBD and fiber hemp during the 2022 visual survey in Pennsylvania.
Functional Group |
CBD |
Fiber |
Herbivores |
1.813 |
4.168 |
Predators |
10.07 |
6.247 |
The diversity index estimated at each sample event reveals the functional group dynamics for each type of hemp over time. In the case of CBD hemp, the diversity of herbivores and predators displays a consistent increase until the end of the flowering stage. During post-flowering the dominance exhibited by few herbivores (e.g. aphids) might have reduced the diversity of this group. Presumably, certain predatory species may assume greater dominance in response to pest behavior (Fig. 4a). For fiber hemp, the dynamic of diversity across time exhibited opposite trends between herbivores and predators indicating possible interactions between those communities (Fig. 4b).
To enhance our comprehension of the dynamics influencing interactions between predator and herbivore communities, and to determine the major players in the crops, further analysis will be conducted using general linear models.
In addition to the visual samplings, yellow sticky traps were installed to passively sample arthropod communities in the crop, we monitored flying insects by installing yellow sticky traps throughout the 2022 growing cycle. The identification process of the specimens in the sticky cards is in progress.
Throughout the 2023 hemp growing season, we utilized different sampling methods including visual inspections, vacuum sampling, yellow sticky cards, and pitfall traps. The collected samples are currently undergoing processing in the lab for subsequent statistical analysis.
- The impact of insect pests on plant defensive metabolites and yield in industrial hemp cultivars
Laboratory experiments have been conducted on two varieties of fiber hemp, Henola, and Joey to evaluate how the most prevalent insect pest, the cannabis aphid (Phorodon cannabis), affects plant growth and photosynthetic potential in hemp plants during the vegetative and flowering stages by exposing plants to aphid herbivory and comparing them with non-infested plants.
In this research, we are only including a few hemp cultivars where we have found differences in their tolerance response to insect attack. We consider it important to evaluate the susceptibility or resistance to insects and pathogens of the cultivars that are available for growers in the market and to determine how these varieties can be utilized according to each grower’s necessities.
Aphid populations were significantly lower in flowering plants compared to vegetative plants in both varieties indicating that aphid development was affected by the plant phenological stage (Fig. 5). Regarding the photosynthetic potential of hemp plants, there were no differences detected between aphid-infested and aphid-free-infested plants in the Joey variety for any of the phenological stages (Fig. 6a). However, in Henola, only the aphid-infested-flowering treatment plants exhibited a lower photosynthetic yield with no significant differences found between the treatments at the vegetative stage (Fig. 6b). Despite these values of photosynthesis for infested flowering plants in Henola, none of the treatments indicated plant stress. The photosynthetic potential Y(II) values for stressed plants, as determined by the method employed, are lower than 0.7.
Plant biomass was not affected in the Joey variety when both vegetative and flowering plants were infested with aphids. However, in the case of Henola, a significant reduction in dry weight was observed when flowering plants were exposed to aphid infestations for a two-week period (Fig. 7). This variation in response between the two hemp varieties to aphid herbivory suggests that Joy demonstrates better tolerance to high aphid infestations, as evidenced by the absence of a reduction in dry weight. This is particularly important when looking at varieties that could tolerate insect damage.
To identify volatiles emitted by plants in response to P. cannabis herbivory, preliminary experiments have been conducted using vegetative and flowering plants from the Henola variety exposed to aphid herbivory for 14 days, while another set of plants for each stage remained free from aphid infestation.
In general, flowering plants released approximately three times more volatiles than vegetative ones, as illustrated in Figure 8. Chromatograms revealed peaks corresponding to around 16 compounds, encompassing green leaf volatiles, terpenes, and sesquiterpenes, which were consistently present in both phenological stages. Among vegetative plants, distinctions were observed, particularly within the sesquiterpene group, indicating lower concentration peaks in aphid-infested plants (Figure 9). Flowering plants exhibited significant variability in the concentration of the same sesquiterpenes between aphid-infested and aphid-free plants (Figure 10).
Education & Outreach Activities and Participation Summary
Participation Summary:
Outreach is an essential component of farmer support. As researchers in applied entomology and agronomy, our research serves a purpose with a goal of relaying information that enhances the experience and profitability of crops for growers (Akobundu et al. 2004). My proposed research will compile information vital to farmer success by detailing the insect pests that are both present and problematic in this novel cropping system. In addition, I will reveal information about the natural enemies that this crop supports which play a role in pest population regulation. Together, these details will be compiled in informative tables and infographics that can be posted digitally on the Penn State Extension website and distributed to farmers listed through the Pennsylvania Department of Agriculture Hemp Permit listserv as commercial growers of Industrial Hemp. Information presented in this format will be easy to access and digest, which is key when disseminating the results of research activities. I will also attend and participate in the annual Hemp Field Day at the Southeast Agricultural Research & Extension Center where I will have physical copies of my extension bulletin to hand out. Here I will be able to interact with growers in-person, providing context and further information from the various observations I will be able to make in the field. Lastly, the work outlined in this proposal will be prepared for publication in peer-reviewed journals and presented at the Entomology Society of America’s annual conference where collegues from across the United States, working on hemp will convene. Importantly, this will allow us to compare how similar the communities are across the country to forge collaborations and to know if strategies in other regions may benefit Pennsylvania growers.
Project Outcomes
The major contribution of this research is to support the knowledge in pest management of growers that are including hemp in their farms and are entering the market of a great variety of products with the potential to achieve environmental, social, and economic sustainability.
Our visits to the farms included not only the implementation of insect surveys in the hemp plots in central and southeast Pennsylvania but also, we had the opportunity to interact directly with farmers. This allowed us to exchange experiences, know their constraints and expectations in this new system and make them aware of the importance of understanding insect diversity to inform their decisions in pest management. This will be reflected in the quality and safety of future production.
Shaffer and Lazy moon farms in Center County cultivated CBG and CBD varieties for medicinal purposes and were involved in outreach activities with communities that visited their sites. In Lancaster County, Cedar Meadow Farm produced hemp for fiber, seed, grain, and extracts, and usually transforms hemp into cosmetics, medicinal and veterinary products. Coexist farm-produced fiber hemp to build ecological construction materials such as hemp concrete blocks. We worked on each of these farms weekly throughout 2022 to observe and identify potential pest issues and biological control solutions.
To support local growers beyond our sampling sites, we also presented our preliminary findings at two extension events in SE Pennsylvania. During the first event - Hemp Twilight Field Day, we demonstrated our survey work at one of the plots we sampled throughout 2022 and answered questions about hemp pests and the potential for management strategies using natural enemies. We were also able to discuss the potential for some cultivars to have an inherent resistance to herbivorous pests, based on our ongoing laboratory research. During the second networking event held in Lancaster County, Pennsylvania, “A Bio-based Future”, we presented our findings on the potential impact of prevalent insect pests on hemp crops, such as the cannabis aphid, and its effect on two cultivars. We engaged with various stakeholders, including farmers, researchers, entrepreneurs, and organizations within the hemp industry, and shared experiences that encouraged us to continue seeking novel sustainable solutions to challenges such as developing pest management in a new cropping system.
Over the course of the project, we have learned about crop attributes for sustainability in three unique types of hemp agricultural production systems: seed/oil, fiber, and medicinal extracts. Our initial research sites included 4 farms representing diverse cultivation practices. Importantly, we learned, firsthand, the potential for hemp-growing practices to contribute to environmental, social, and economic sustainability. Three additional sampling plots were established and monitored at Penn State Farm facilities across Pennsylvania.
The architecture of the plant and the crop management practices vary widely depending on the crop purpose, whether it is for fiber, grain, or medicinal extracts. Overall, hemp is a low-input crop in terms of pesticides due to the lack of registered, allowable options for growers. Most growers are working to manage their hemp with minimal disturbances and inputs and are excited to learn about the potential problems they could encounter in terms of insect herbivory. The growers expressed a keen curiosity about how the abundance and composition of beneficial natural enemies (predatory and parasitic insects) present in their farms were associated with the pressure of insect pests. Facilitated by this grant, our goal during the 2022 production cycle was to characterize the pests and natural enemies across hemp cultivars and crop purposes and to communicate that information to our various growers. In doing so, we gained grower interest in determining the potential of the biological control agents observed in reducing pest pressure and reducing issues of increased cannabinoid content associated with herbivory. One reason to monitor pest insects is due to their potential to increase cannabinoids, especially the federally regulated THC, to a level that renders their crop unusable and warrants total crop destruction. This devastating outcome of increased THC left one of our growers to destroy a $60,000 crop of hemp for CBD. We have also begun to explore the impact of insect pest herbivory on plant quality and ultimately yield in the lab. Through these communications and observations on farms, we are now more aware of the challenges these growers face as well as the scales and outputs of their operations.
We were also able to secure $ 58,000 in funding from the Pennsylvania Department of Agriculture to increase the impact of our project, including new objectives to support the sustainability of the hemp industry in pest management and we also developed cooperation with growers and researchers that have previous experience in the hemp system.
I appreciate the aims of sustainable agriculture and enjoy helping the growers move toward using those strategies. The role of hemp in relation to sustainable development contributes not only in terms of sustainable agriculture practices but also in terms of their applications to the industry as a whole. This encourages my desire to support and perform future research in sustainable systems that could have a positive impact on the achievement of sustainable development goals.
During the initial stage of this research, one of the main constraints was the dispersal of the sampling sites across the state of Pennsylvania which limited the number of farms that can be covered weekly. With the additional funding we got, we were able to include new sites and more varieties during a second insect sampling during the 2023 hemp growing season to broaden our research questions. This funding allowed us to begin filling the gaps in pest management for the hemp industry in the Northeastern region of the USA.