ORIGINAL RESEARCH article

Front. Agron., 29 June 2022

Sec. Pest Management

Volume 4 - 2022 | https://doi.org/10.3389/fagro.2022.901416

First Year Survey of Arthropods in California Hemp

  • 1. Department of Entomology, University of California Riverside, Riverside, CA, United States

  • 2. University of California Kearney Agricultural Research and Extension Center, Parlier, CA, United States

Abstract

Hemp is a newly (re)introduced crop to United States and California agriculture. A study was initiated in the summer of 2021 to survey the arthropods present in hemp in two regions of California: Fresno County in the Central Valley and Ventura County along the Central Coast. Eight hemp plots were sampled every two weeks from August to mid-October using a combination of D-vac samples, leaf collections, and visual observations. All samples were processed and ultimately recorded as the total number of specimens collected per morphospecies across all sampling dates, further broken down to express the number of specimens collected from the Central Valley and the Central Coast. D-vac sampling was the most reliable method for specimen collection and led to the recovery of arthropods from 11 orders, 69 families, and 157 morphospecies. Approximately 13,000 specimens were collected and processed, half of which were whiteflies (Hemiptera: Aleyrodidae). Of the specimens recovered, Hemiptera was the most representative order (with and without whiteflies), followed by Thysanoptera and then Hymenoptera. The most frequently collected specimen was Engytatus modestus (Hemiptera: Miridae). Very few pest species were recovered, cannabis aphid (Phorodon cannabis) being the only one that was observed in any noticeable density. Many generalist predators and parasitoid wasps were also collected. Findings from this survey provide baseline information on the arthropod species present in California hemp. This survey will be repeated and expanded in future growing seasons.

Introduction

Hemp (Cannabis sativa L., <0.3% THC) has recently had a revival in United States agriculture, and in California in particular. At the federal level, prohibition rendered hemp cultivation illegal for the greater part of the past century, but language in Section 7606 of the 2014 Farm Bill (U.S. H.R. 2642 – Agricultural Act of 2014 113th Congress [2013–2014]) gave justification for universities to conduct hemp research and for commercial production to occur in states where cultivation was allowed. With the subsequent passage of the 2018 Farm Bill (U.S. H.R. 2—115th Congress [115-334]), hemp was federally legalized for commercial production and as of 2022, cultivation is allowed in all 50 states. Effective January 1, 2017, the California Industrial Hemp Farming Act (Senate Bill 566, Chapter 398, Statutes of 2013) authorized commercial production of hemp in California. In 2021, California had the fifth highest acreage for hemp production in the United States (2,650 acres) and was second highest in acreage devoted to floral/cannabinoid hemp production (1,900 acres) (National Hemp Report, 2022).

Arthropod species present in hemp are poorly documented, with no published surveys from California and few for the rest of the United States. The most comprehensive texts thus far are from Cranshaw et al. (2019), which focused on hemp production in Colorado, Virginia, and Tennessee, and McPartland et al. (2000), which collected reports from various locations throughout the world. To date, the only state-specific studies to catalogue arthropods in Cannabis sativa have been from hemp in Colorado (Schreiner and Cranshaw, 2020) and cannabis (Cannabis sativa L., >0.3% THC) in Mississippi (Lago and Stanford, 1989). There are also several state level Extension guides (Britt et al., 2020; Hansen et al., 2020; Kesheimer et al., 2021), but these texts focus exclusively on pest species (arthropods, pathogens, and weeds) in hemp and guidelines for their management. Compilations of plant pathogens and viruses present in hemp also exist (Punja, 2018; Punja et al., 2019; Thiessen et al., 2020; Chiginsky et al., 2021). In California, Wilson et al. (2019) conducted an online survey of cannabis growers to solicit information about many aspects of production, including pest monitoring and management. However, accuracy of identification of arthropods reported in the survey is uncertain since respondents were self-reporting.

Here, a field study was conducted in the summer and fall of 2021 to catalogue the arthropod species present in hemp across two regions of California. With no prior records detailing this information, this study was intended to provide baseline data on the diversity, abundance, and potential pest status of arthropods found on hemp in California.

Materials and Methods

Field Sampling

Eight floral/cannabinoid hemp sites (Table 1) were sampled during the 2021 growing season to catalogue the arthropod community in California hemp. Specimens were collected from two general regions in California: 1) Fresno County in the Central Valley and 2) Ventura County on the Central Coast (Figure 1). Two sites at each location were research institutes and two sites were licensed commercial hemp growers. Sites were sampled twice monthly beginning in August (August 3, Central Valley; August 9, Central Coast) and sampling was terminated just prior to harvest, which was mid-October (October 5, Central Valley; October 12, Central Coast).

Table 1

Site numberRegionLatitudeLongitude2021 sampling datesDescription
1Fresno County
Central Valley
36.6012944-119.5106429August 3
August 17
August 30
September 12
October 5
Research institute
Outdoor
2Fresno County Central Valley36.3419963-120.1082003Research institute
Outdoor
3Fresno County Central Valley36.736907-119.603436Licensed grower
Outdoor, covered shade house
4Fresno County Central Valley36.5187401-119.7078306Licensed grower
Outdoor
5Ventura County Central Coast34.3262566-119.1059995August 9
August 23
September 14
September 28
October 12
Research institute
Outdoor
6Ventura County Central Coast34.2207511-119.1062352Research institute
Outdoor
7Ventura County Central Coast34.163458-119.1212475Licensed grower
Indoor
8Ventura County Central Coast34.223115-119.225269Licensed grower
Indoor nursery

Site number, region, latitude and longitude coordinates, sampling dates, and description of hemp sites sampled in California in 2021.

Figure 1

Sampling Techniques

D-vac type suction sampling was the primary sampling technique used. This consisted of vacuum suctions of hemp plants using a 25-cc gasoline blower/vacuum (Husqvarna, Stockholm, Sweden) fitted with a 5-gallon bucket on the vacuum tube (1 square-foot sampling cone) covered with a fine mesh collection bag. D-vac samples were conducted at three random sample points at each site. For each sample, a transect of hemp plants was vacuumed for a total of 60 seconds while moving at a walking pace; for this study, approximately 50 feet or 15.2 meters were travelled in each 60 second period. All collected arthropod specimens were transferred to a 1-gallon plastic freezer bag and held in a cooler with ice during transport to the laboratory.

Leaf collections were used to sample for mites (hemp russet mite, Aculops cannibicola [Acari: Eriophyidae]; twospotted spider mite, Tetranychus urticae [Trombidiformes: Tetranychidae]; and broad mite, Polyphagotarsonemus latus [Trombidiformes: Tarsonemidae]). At each site, ten leaves were collected at each of three random sample points. Leaves were processed with a mite brush upon returning to the lab.

Visual samples were used to document presence and injury resulting from species that have been classified as injurious to hemp (Cranshaw et al., 2019), including corn earworm (Helicoverpa zea, Lepidoptera: Noctuidae) (Britt et al., 2021), twospotted spider mite (Trombidiformes: Tetranychidae), and cannabis aphid, Phorodon cannabis (Hemiptera: Aphididae) (Cranshaw et al., 2018). At each site, apical sections of ten hemp buds were examined at each of three random sample points.

Lab Processing and Taxonomic Identification

In the laboratory, D-vac samples were sorted into morphologically distinct groupings, or morphospecies, and identified to family or lowest taxonomic level possible. Family level identifications were made using keys from Triplehorn et al. (2005) and Marshall (2006), followed by comparisons to specimen photographs from the web portals BugGuide1 and iNaturalist2. Voucher specimens of each morphospecies were pinned or preserved and are currently housed at the University of California’s Kearney Agricultural Research and Extension Center in Parlier, CA.

Results and Discussion

In total, the D-vac sampling effort led to the recovery of arthropods from 11 orders, 69 families, and 157 morphospecies (Table 2). A total of 12,937 specimens were processed, half of which were whiteflies (Hemiptera: Aleyrodidae) (6,209). Other than whiteflies, the most frequently collected specimens were: Engytatus modestus (Hemiptera: Miridae), 366 specimens; Aphididae morphospecies 1 (Hemiptera: Aphididae), 270 specimens; Anthocoridae morphospecies 1 (Hemiptera: Anthocoridae), 240 specimens; Scelionidae morphospecies 1 (Hymenoptera: Scelionidae), 231 specimens; Ephydridae morphospecies 1 (Diptera: Ephydridae), 219 specimens; Lygus lineolaris (Hemiptera: Miridae), 149 specimens; Empoasca sp. (Hemiptera: Cicadellidae), 142 specimens; and Cicadellidae morphospecies 2c (Hemiptera: Cicadellidae), 132 specimens (Table 3). Order Hemiptera had the greatest number of specimens collected overall (8,470), even when the whitefly specimens were excluded (2,261), followed by Thysanoptera (2,051), and Hymenoptera (998).

Table 2

Central ValleyCentral CoastCombined
OrderSpecimensMorphospeciesSpecimensMorphospeciesSpecimensMorphospecies
Araneae60not sorted17not sorted77not sorted
Coleoptera130141551728525
Collembola4not sorted15not sorted19not sorted
Diptera602162861888826
Hemiptera
(No whiteflies)
1555–706–2261–
Hemiptera524847322237847061
Hymenoptera844201542599837
Lepidoptera20not sorted7not sorted27not sorted
Neuroptera421212632
Orthoptera001111
Psocodea50284585
Thysanoptera1983not sorted68not sorted2051not sorted
TOTAL8983100395410412937157

Summary of specimens collected from hemp in California in 2021, grouped by Order.

Unsorted orders were counted as 1 morphospecies in the total morphospecies counts. Nematoceran flies were not sorted and counted as 1 morphospecies. Chalcidoid wasps were not sorted and counted as 1 morphospecies.

Table 3

Specimens collected
OrderFamilyMorphospeciesTotalCentral ValleyCentral Coast
Araneae776017
ColeopteraAnthicidaeNotoxus sp.45450
2110
ChrysomelidaeSystena blanda34331
Epitrix hirtipennis25232
Chaetocnema sp.990
Diabrotica balteata71071
5514
Altica sp10010
Diabrotica undecimpunctata101
Diachus auratus101
CoccinellidaeHarmonia axyridis202
Cycloneda sp.404
Subfamily Scymninae770
4707
Hippodamia convergens211
611–
Corylophidae1303
Cryptophagidae1101
Latridiidae1909
Melyridae1101
Mordellidae1110
Ptilidae1220
Staphylinidae122121
2321
CollembolaAll specimens19415
DipteraAgromyzidae146388
Anthomyiidae1101
Suborder Brachycera (unidentified)1367
Ceratopogonidae158580
2550
Chaemaemyiidae1615
Chloropidae1413
2101
3110
Dolichopodidae1523
Drosophilidae1220
Ephydridae12192190
2221111
Heliomyzidae110010
Muscidae112111
Suborder Nematocera (unidentified)378181197
Phoridae1431
2303
Psychodidae1202
Syrphidae1303
Tachinidae1330
Tephritidae110010
Ulidiidae115150
HemipteraAleyrodidae1496430061958
2642425217
Anthocoridae124021426
Aphididae127023238
Phorodon cannabis831370
3853
412120
5440
Berytidae1330
Chloropidae1101
Cicadellidae1110
2a39390
2b14140
2c13210824
2d412714
3220
Empoasca sp.14227115
5312
6404
7101
837370
912111
10101
11440
12110
13101
Cixiidae1615
Delphacidae1220
2220
GeocoridaeGeocoris punctipes69681
Lygaeidae1110
Membracidae11046
2110
MiridaeLygus lineolaris1491409
210100
Engytatus modestus366178188
4342212
Spanagonicus albofasciatus844
6440
7471037
8808
91578
10110
Nabidae1523
Pentatomidae1101
Thyanta pallidovirens110
Piesmatidae1330
Psocodea1220
Psylloidea1202
2404
3101
4101
Reduviidae110100
Rhopalidae1110
2110
3352015
Liorhyssus hyalinus47344
5101
Tingidae1110
HymenopteraArgidae139390
BraconidaeSubfamily Euphorinae110
Subfamily Opiinae76706
Subfamily Aphidiinae17413
Subfamily Microgastrinae606
Subfamily Alysiinae101
Subfamily Meteorinae303
Subfamily Cheloninae110
Subfamily Braconinae110
Subfamily Hormiinae101
Ceraphronidae140400
2550
3110
Chalcidoidea (unidentified)43737463
Cynipidae1101
DryinidaeAphelopus sp.404
2110
FigitidaeMelanips sp.101
Subfamily Eucoilinae473710
Subfamily Anacharitinae101
FormicidaeSubfamily Formicinae1019
Subfamily Myrmicinae23230
Ichneumonidae1101
2101
3303
Megaspilidae1202
Platygastridae1101
Scelionidae123121714
255–
3312
Lepidoptera27720
NeuropteraChrysopidae1463115
Hemerobiidae1202
Psocodea149490
2211
3101
4101
5105
Thysanoptera2051198368

Summary of all specimens collected in hemp at 2 sample regions in California during 2021.

Arranged by arthropod order, family, and morphospecies. Where further identification was possible, genus and/or species is listed in the morphospecies column. Total number of specimens collected for each morphospecies is listed as well as the number of specimens collected in each sampling region.

Potential Pests

A few major pests of hemp include corn earworm (Britt et al., 2021), cannabis aphid (Cranshaw et al., 2018), hemp russet mite (McPartland and Hillig, 2003), and twospotted spider mite (McPartland et al., 2000; Cranshaw et al., 2019). Cannabis aphid was found in both sampling regions and is the only one of the pest species that was observed in any kind of noticeable density. Recently, it has been confirmed that cannabis aphid is a vector of potato virus y (Pitt et al., 2022) in hemp in Colorado. Similarly, in the past, cannabis aphid was documented as a vector of alfalfa mosaic virus and confirmed to transmit cucumber mosaic virus (Schmidt and Karl, 1970). However, it should be noted that other aphid morphospecies were also found in both regions and in higher numbers.

Very few lepidopteran larvae were collected in D-vac samples and hardly any corn earworm larvae were documented with visual observations. Additionally, no sites had considerable presence of or suspected injury resulting from any of these species of concern, so there are no visual data to report. Very few to no mites were recovered from leaf collections in this study, so there are also no mite results to report.

Generalist Predators and Parasitoids

Notable in this study was the large number of natural enemies collected, including Anthocoridae (minute pirate bugs, Hemiptera), Reduviidae (assassin bugs, Hemiptera), Nabidae (damsel bugs, Hemiptera), Coccinellidae (lady beetles, Coleoptera), Chrysopidae (lacewings, Neuroptera). Additionally, a considerable number of Hymenopteran parasitoid families were also collected (Braconidae [107 specimens], Ceraphronidae [46 specimens], Cynipidae [1 specimen], Dryinidae [5 specimens], Figitidae [49 specimens], Ichneumonidae [5 specimens], Megaspilidae [2 specimens], Platygastridae [1 specimen], and Scelionidae [239 specimens]).

Beet Leafhopper

Several leafhopper morphospecies were collected during this survey. Although the species was not confirmed in this study, beet leafhopper, Circulifer tenellus (Hemiptera: Cicadellidae), is a species of concern for hemp in California since it can transmit beet curly top virus (Severin, 1931). So far, beet curly top virus has been confirmed in hemp in Arizona (Hu et al., 2020), Colorado (Giladi et al., 2020), and Oregon (Rivedal et al., 2021). Symptoms in hemp include stunted growth and yellowing of leaves (Giladi et al., 2020), potentially leading to yield loss. Beet curly top virus is problematic in California (Wintermantel et al., 2003) and several different strains have been confirmed in various California crops such as tomatoes (Chen et al., 2010), peppers (Chen et al., 2017), basil (Chen et al., 2014), and others. Signs and symptoms of beet curly top virus were noted at one of the research sites in the Central Valley, so this is something to monitor in future studies where leafhoppers (particularly beet leafhopper) are present.

Species Not Recovered

Bees have been observed in hemp, but these reports have been from pollen producing fiber or grain varieties of the crop (O’Brien and Arathi, 2019; Flicker et al., 2020). The floral/cannabinoid varieties sampled in this study do not produce pollen. Several species of stink bugs have been readily observed in hemp (Cranshaw et al., 2019) although crop injury resulting from feeding has not been documented (Britt et al., 2019). Only two stink bugs total were recovered from 2021 surveys.

Study Limitations

Lepidopteran larvae and mites are known to be associated with hemp (Lago and Stanford, 1989; McPartland et al., 2000; McPartland and Hillig, 2003; Cranshaw et al., 2019; Schreiner and Cranshaw, 2020; Britt et al., 2021) but this survey recovered very few of both these groups. D-vac sampling is unlikely to recover arthropods which strongly adhere to substrate or are embedded in plant tissue which could include larvae of lepidopterans and others, such as coleopterans (lady beetles) and neuropterans (lacewings). Aphids and other soft-bodied specimens were captured by the D-vac, so the suction was likely strong enough to collect mite specimens if they were present. Because visual sampling targeting these mites and lepidopteran larvae also recovered very few observations of either arthropod group, it is likely that there were not very many lepidopteran larvae or mites present at the study sites.

Conclusions and Future Directions

This study provided baseline information regarding the arthropod community present in California hemp. Many species were present, including a variety of generalist predators and parasitoids. This work will continue and expand in the coming years to incorporate sampling from more regions in California to additionally express seasonal phenology of each observed species. At most of the sites sampled, 2021 was the first year hemp was cultivated. It is likely that the arthropod community will change in the coming years as the crop is more regularly cultivated throughout California.

Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Statements

Data availability statement

The original contributions presented in the study are included in the article/supplementary material. Further inquiries can be directed to the corresponding author.

Author contributions

KB and HW designed the study. KB arranged sampling with growers and research centers and conducted field sampling. SM and VM conducted specimen ID. All authors contributed to the article and approved the submitted version.

Acknowledgments

We are incredibly grateful to the growers who allowed us to sample from their hemp plots, as well as the agriculture operations personnel at the University of California research stations who handled initial planting and plot maintenance throughout the 2021 growing season. We also thank Dmitri A. Dmitriev who is currently assisting with Cicadellidae identification.

Conflict of interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

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Summary

Keywords

arthropod, survey, hemp (cannabis sativa L), California (USA), first year

Citation

Britt KE, Meierotto S, Morelos V and Wilson H (2022) First Year Survey of Arthropods in California Hemp. Front. Agron. 4:901416. doi: 10.3389/fagro.2022.901416

Received

21 March 2022

Accepted

30 May 2022

Published

29 June 2022

Volume

4 - 2022

Edited by

Zamir Punja, Simon Fraser University, Canada

Reviewed by

Sean Michael Prager, University of Saskatchewan, Canada; Cynthia Diane Scott-Dupree, University of Guelph, Canada

Updates

Copyright

*Correspondence: Kadie E. Britt,

This article was submitted to Pest Management, a section of the journal Frontiers in Agronomy

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