- Research note
- Open Access
Grass is not always greener: rodenticide exposure of a threatened species near marijuana growing operations
BMC Research Notes volume 11, Article number: 94 (2018)
Marijuana (Cannabis spp.) growing operations (MGO) in California have increased substantially since the mid-1990s. One environmental side-effect of MGOs is the extensive use of anticoagulant rodenticides (AR) to prevent damage to marijuana plants caused by wild rodents. In association with a long-term demographic study, we report on an observation of brodifacoum AR exposure in a threatened species, the northern spotted owl (Strix occidentalis caurina), found freshly dead within 669–1347 m of at least seven active MGOs.
Liver and blood samples from the dead northern spotted owl were tested for 12 rodenticides. Brodifacoum was the only rodenticide detected in the liver (33.3–36.3 ng/g) and blood (0.48–0.54 ng/ml). Based on necropsy results, it was unclear what role brodifacoum had in the death of this bird. However, fatal AR poisoning has been previously reported in owls with relatively low levels of brodifacoum residues in the liver. One likely mechanism of AR transmission from MGOs to northern spotted owls in California is through ingestion of AR contaminated prey that frequent MGOs. The proliferation of MGOs with their use of ARs in forested landscapes used by northern spotted owls may pose an additional stressor for this threatened species.
The number and extent of marijuana (Cannabis spp.) growing operations (MGO) in California have increased substantially since the mid-1990s, with a mix of illegal clandestine operations and those growing for medical or, recently, recreational use [1,2,3]. California is the largest producer of marijuana in the U.S., with Humboldt, Trinity and Mendocino Counties the epicenter for production . There are ~ 15,000 documented MGOs in Humboldt County  and an estimated 4428 of these were visible outdoor MGOs on private lands (either as greenhouses, crop fields, or both) in 53.6% of the watersheds . One environmental side-effect of marijuana production in California is the extensive use of anticoagulant rodenticides (AR) to prevent damage to plants caused by wild rodents [6, 7]. Oftentimes, substantial amounts of AR (up to ~ 25 kg) are found at illegal MGOs on public lands [6,7,8,9]. Although a large number of MGOs on private lands are quasi-legal in California, the distinction between illegal and legal operations for enforcement purposes is difficult. Because marijuana is still federally illegal, no pesticides are registered for its use as an agricultural crop . For these reasons, regulatory compliance on quasi-legal MGOs is uncertain and assumed to be low. Enforcement of regulations by government agencies is minimal because of the sheer number of unpermitted MGOs and remoteness of these operations [3, 10, 11]. For example, only 15% of MGOs in Humboldt County have applied for permits with only 0.6% approved, suggesting that over 85% of MGOs in the county have not applied to be under regulatory compliance . Thus, AR use on MGOs in California is probably ubiquitous, regardless of legality, because of the perceived threat of wild rodent damage to marijuana crops on MGOs and the lack of permitting and enforcement [12, 13].
Secondary poisoning of non-target wildlife (species unintentionally exposed to AR) from ARs has become a re-emerging threat in California, especially around outdoor MGOs on or near public lands, which are considered a primary source of AR in wild environments [6, 7, 9, 14]. For example, dead wildlife from AR poisoning were found at 21.9% of 41 MGOs investigated in Humboldt, Trinity, and Siskiyou counties; these included bears, foxes, fisher (Pekania pennant), squirrels, deer, and passerine birds . In addition, liver residues in wild rodents at MGOs also tested positive for ARs . Although raptors found dead with signs of AR poisoning were not found at MGOs, they prey on rodents affected by AR at MGOs and possibly die elsewhere. ARs in prey presents a risk to owls that subsequently bioaccumulate ARs in tissues, especially the liver , taking up to 15 days to produce lethal concentrations. Thus, owls are at high-risk for secondary AR poisoning because of their specialization on rodent prey . For example, 62–90% of carcasses from three owl species in western Canada had detectable residues from ≥ 1 AR, even death from AR poisoning was determined in only 2–12% of cases .
Of particular concern is the threat of secondary AR poisoning in northern spotted owls (Strix occidentalis caurina), a threatened species under the Endangered Species Act  currently experiencing 2.3–3.0% annual population declines in California due to a number of stressors . MGOs occur within areas used by northern spotted owls, which have the potential to be exposed to ARs through their primary prey in northern California, dusky-footed woodrats (Neotoma fuscipes). Dusky-footed woodrats are also perceived by growers as a threat to marijuana plants because they forage on young plants in the spring and use the plants to build nests [12, 13]. Recently, 70% of northern spotted owls found dead had evidence of being exposed to ARs, with the hypothesis that increased MGOs on the landscape were the primary source . However, AR use on MGOs has not been explicitly linked with northern spotted owl exposures.
In association with a long-term demographic study, we report on brodifacoum exposure in a northern spotted owl found freshly dead in the vicinity of at least 7 active MGOs on private inholdings within a National Forest (Fig. 1) during a routine survey to detect owls. Finding a freshly dead northern spotted owl in the woods is a very rare event; this is the first time we have encountered a recently deceased adult during 9216 foot surveys on 95 spotted owl territories over a 33-year study. Thus, this observation is important in establishing a potential linkage that warrants further research to determine the magnitude of this threat to northern spotted owl populations.
A female northern spotted owl was found dead 5 April 2017 in a territory that had been monitored since 1985  south of Willow Creek, Humboldt County, California. The female was marked with a USGS numbered band and a unique colored band in 2008 and had occupied the territory since 2016. The female was estimated to be dead ≤ 24 h because (1) the carcass was fresh with the eyes not sunken, (2) there were no fly larvae on the carcass, and (3) the male owl attempted to deliver a mouse to the carcass for ~ 5 min.
The carcass was collected and shipped chilled to the USGS National Wildlife Health Center (NWHC), Madison, WI for necropsy. Liver and blood samples were taken and sent for AR residue analysis at the USDA-APHIS National Wildlife Research Center, Fort Collins, CO.
The liver and blood samples were subsequently tested for 11 anticoagulant rodenticides (coumafuryl, coumatetralyl, pindone, warfarin, coumachlor, diphacinone, chlorophacinone, bromadiolone, difenacoum, brodifacoum, difethialone) and 1 neurotoxicant rodenticide metabolite (desmethyl bromethalin) (see Additional file 1 for exact methods).
To identify potential sources of AR, we first delineated the potential foraging area for northern spotted owls on this particular territory using night and day locations of northern spotted owls detected during surveys conducted from 1985 to 2017 during our demography study . Following , we scanned high-resolution satellite imagery from May 2016 in Google Earth® (www.google.com/earth/) around the polygon formed by the owl locations to search for visible AR sources, such as residences and MGOs, within this particular owl territory. We also included locations of illegal MGOs found by law enforcement agencies (M. Gabriel, unpublished data). All MGOs were known to local law enforcement authorities. We were unable to determine whether the MGOs identified were using ARs. As one study noted , most landowners with MGOs are unwilling to allow visitors to their operation and it is usually dangerous for researchers to approach them. All locational data was entered into a geographic information system (ArcGIS 10®) to develop maps (e.g., Fig. 1) and measure distances from the owl mortality site and potential sources of AR poisoning. Because of legal restrictions, specific locational information for either the spotted owl or MGOs on private lands cannot be provided.
Results and discussion
The necropsy found that the female was reproductively active with developing follicles in the ovary, was emaciated, and heavily parasitized with large numbers of Leucocytozoon spp. protozoa in red blood cells and Elmeria spp., coccidia and Capillariid spp. in the intestine. The female weighed 490 g when found, which was 73.9% of the mean weight for female northern spotted owls ; no baseline weight had been taken for this individual when first captured in 2008. No other abnormalities, including trauma, were detected. The owl tested negative for avian influenza viruses, West Nile virus, and exposure to lead. Brain cholinesterase levels were not depressed, suggesting no acute exposure to cholinesterase-inhibiting toxicants, such as organophosphate or carbamate pesticides. Proximate cause of death was diagnosed as emaciation and parasitism.
Brodifacoum was the only rodenticide detected in the liver (33.3–36.3 ng/g) or the blood (0.48–0.54 ng/ml) (Table 1). In this case, exposure to brodifacoum was not the primary cause of death of the northern spotted owl examined here, as there was no sign of internal hemorrhage indicative of AR poisoning. However, the levels of brodifacoum residues found in the owl’s liver have been associated with lethal AR poisoning in other owl species, such as great horned owls (Bubo virginianus) with liver residues as low as 10 ng/g . Two northern spotted owls submitted to the NWHC in the 1990s had brodifacoum liver residues of 50.0 and 100 ng/g and signs of hemorrhaging (NWHC Case Numbers 10128 and 13799). Although not directly linked as the cause of mortality, exposure to brodifacoum in the owl we found may have resulted in a sub-lethal exposure. While sub-lethal effects of brodifacoum on non-target wildlife are poorly understood, they are hypothesized to include anemic lethargy that impairs hunting ability leading to loss of body mass, and increased susceptibility to disease [26, 27]. For example, sub-lethal exposures to brodifacoum slowed growth in Japanese quail  and was associated with an outbreak of notoedric mange in bobcats (Lynx rufus), which led to a 64% reduction in survival . Combined with the northern spotted owl’s reproductive status and heavy parasitism, brodifacoum may have been an additional contributor to the owl’s death.
Brodifacoum is commonly used in household, industrial and agricultural settings and is often found at illegal clandestine MGOs [5,6,7,8] to prevent rodents from damaging the stalks of marijuana plants where it is applied at plant bases and around MGO perimeters . The dead northern spotted owl was found within 669–1347 m of at least 7 active MGOs on private inholdings within a National Forest (Fig. 1). In 2015, an illegal clandestine MGO with ~ 23 kg of brodifacoum-laced bait was discovered 450 m from the recovery location of this dead owl (M. Gabriel, unpublished data, Fig. 1), indicating that other undetected MGOs may have been nearby. Given the documented use of brodifacoum on MGOs, it is highly likely that the source of the brodifacoum residues found in the dead owl were from one or more of the MGOs within its territory (Fig. 1); we were unable to identify any other potential sources.
One probable mechanism of AR transmission from MGOs to northern spotted owls in this region of California is through ingestion of dusky-footed woodrats, which are a dominant prey of spotted owls in this area . Dusky-footed woodrats are abundant in early-seral stages, such as openings created by fire, timber harvests, or (presumably) MGOs, and have specialized gut microbiomes that allow them to digest toxic secondary plant compounds and fibrous plant material , typical of marijuana plants. In addition, dusky-footed woodrats incorporate plants with high monoterpene content [32, 33], such as California bay (Umbellularia californica), into their nests, with evidence that these plants act as larvicides and repellants against fleas [34, 35]. Cannabis contains similar monoterpenes and can also act as a larvicide against mosquito and other insect larvae [36,37,38]; anecdotal observations indicate that woodrats incorporate marijuana stalks into their nests . Both California bay and marijuana plants are aromatic [34, 39] and woodrats may be able to detect these on the landscape through olfactory cues. Northern spotted owls in California also tend to forage near edges of openings when woodrats predominate in their diet . In forested landscapes in Humboldt County, California, MGOs have generated increased edge with forest areas and increased patch shape complexity , landscape elements that also contribute to high-quality habitat for northern spotted owls .
Based on this, we propose a mechanistic hypothesis on the linkage between MGOs and secondary AR poisoning of northern spotted owls (Fig. 2), where woodrats are attracted to MGOs by the presence of marijuana plants for food and larvicidal nest material and encounter ARs in rodent baits while foraging on MGOs. Northern spotted owls are also attracted to MGOs because of the edge habitat created by MGOs and increased prey movement across those edges. This edge becomes the area where owls then prey on AR-contaminated woodrats.
The observation of a northern spotted owl with AR residues in proximity to numerous MGOs further suggests the potential linkage between MGOs and AR exposure for this threatened species as another additive stressor. Thus, outdoor MGOs in forested landscapes may provide resources for prey and foraging opportunities for northern spotted owls but with potentially lethal consequences for both.
We were unable to definitely identify MGOs as the source for the brodifacoum found in the dead northern spotted owl. However, we were not able to identify any other potential sources of AR within the territory used by this particular owl. Thus, our case study provides evidence to support the hypothesis that MGOs may constitute an additional threat to northern spotted owl populations in northwestern California, a hypothesis that should be examined with further research.
marijuana (Cannabis sp.) growing operation
USGS National Wildlife Health Center
U. S. Geological Survey
Bauer S, Olson J, Cockrill A, van Hattem M, Miller L, Tauzer M, Leppig G. Impacts of surface water diversions for marijuana cultivation on aquatic habitat in four northwestern California watersheds. PLoS ONE. 2015;10:e0120016.
Carah JK, Howard JK, Thompson SE, Short Gianotti AG, Bauer SD, Carlson SM, Dralle DN, Gabriel MW, Hulette LL, Johnson BJ, et al. High time for conservation: adding the environment to the debate on marijuana liberalization. Bioscience. 2015;65:822–9.
Butsic V, Brenner JC. Cannabis (Cannabis sativa or C. indica) agriculture and the environment: a systematic, spatially-explicit survey and potential impacts. Environ Res Lett. 2016;11:044023.
Corva D. Requiem for a CAMP: the life and death of a domestic U.S. drug war institution. Int J Drug Policy. 2014;25:71–80.
Ascent Environmental. Final environmental impact report for the amendments to Humboldt County code regulating commercial Cannabis activities SCH# 2017042022. Eureka: Humboldt County Planning & Building Department; 2018.
Gabriel MW, Woods LW, Poppenga R, Sweitzer RA, Thompson C, Matthews SM, Higley JM, Keller SM, Purcell K, Barrett RH, et al. Anticoagulant rodenticides on our public and community lands: spatial distribution of exposure and poisoning of a rare forest carnivore. PLoS ONE. 2012;7:e40163.
Gabriel MW, Woods LW, Wengert GM, Stephenson N, Higley JM, Thompson C, Matthews SM, Sweitzer RA, Purcell K, Barrett RH, et al. Patterns of natural and human-caused mortality factors of a rare forest carnivore, the fisher (Pekania pennanti) in California. PLoS ONE. 2015;10:e0140640.
Gabriel MW, Wengert GM, Higley JM, Krogan S, Sargent W, Clifford DL. Silent forests? Rodenticides on illegal marijuana crops harm wildlife. Wildl Prof. 2013;7:46–50.
Thompson C, Sweitzer R, Gabriel M, Purcell K, Barrett R, Poppenga R. Impacts of rodenticide and insecticide toxicants from marijuana cultivation sites on fisher survival rates in the Sierra National Forest, California. Conserv Lett. 2014;7:91–102.
Stone D. Cannabis, pesticides and conflicting laws: the dilemma for legalized states and implications for public health. Regul Toxicol Pharmacol. 2014;69:284–8.
Short Gianotti AG, Harrower J, Baird G, Sepaniak S. The quasi-legal challenge: assessing and governing the environmental impacts of cannabis cultivation in the North Coastal Basin of California. Land Use Policy. 2017;61:126–34.
Kemp K. Protecting pot (and other plants) without using rodenticides. In: Lost coast outpost. 2013. https://lostcoastoutpost.com/2013/jun/17/rodenticide/. Accessed 1 Mar 2018.
Williamson A. The everything marijuana book. Avon: Simon and Schuster; 2010.
Daniels D. Second generation anticoagulant rodenticide assessment. Sacramento: California Department of Pesticide Regulation; 2013.
Gabriel MW, Wengert GM, Higley JM, Clifford DL, Poppenga RH, Woods LW, McMillian S, Torres S. Science with solutions: documentation, reclamation and monitoring of the ecological impacts of marijuana cultivation on endangered species. Blue Lake: Integral Ecology Research Center; 2017.
López-Perea JJ, Mateo R. Secondary exposure to anticoagulant rodenticides and effects on predators. In: van den Brink NW, Elliott JE, Shore RF, Rattner BA, editors. Anticoagulant rodenticides and wildlife. Cham: Springer International Publishing; 2018. p. 159–93.
Albert C, Wilson L, Mineau P, Trudeau S, Elliott J. Anticoagulant rodenticides in three owl species from western Canada, 1988–2003. Arch Environ Contam Toxicol. 2010;58:451–9.
U. S. Fish and Wildlife Service. 50 CFR Part 17 Endangered and threatened wildlife and plants; determination of threatened status for the northern spotted owl; final rule. Fed Reg. 1990;55:26114–94.
Dugger KM, Forsman ED, Franklin AB, Davis RJ, White GC, Schwarz CJ, Burnham KP, Nichols JD, Hines JE, Yackulic CB, et al. The effects of habitat, climate, and barred owls on long-term demography of Northern spotted owls. Condor. 2016;118:57–116.
Gabriel MW, Diller LV, Dumbacher JP, Wengert GM, Higley JM, Poppenga RH, Mendia S. Exposure to rodenticides in Northern spotted and barred owls on remote forest lands in northwestern California: evidence of food web contamination. Avian Cons Ecol. 2018;13:2.
Franklin AB, Gutiérrez RJ, Noon BR, Ward JP Jr. Demographic characteristics and trends of northern spotted owl populations in northwestern California. Stud Avian Biol. 1996;17:83–91.
Franklin AB, Anderson DR, Forsman ED, Burnham KP, Wagner FW. Methods for collecting and analyzing demographic data on the northern spotted owl. Stud Avian Biol. 1996;17:12–20.
Bauss CL. Mapping marijuana cultivation sites and water storage in the Redwood Creek watershed, southern Humboldt County. Calif Geogr. 2017;56:29–52.
Blakesley JA, Franklin AB, Gutierrez RJ. Sexual dimorphism in northern spotted owls from northwest California. J Field Ornithol. 1990;61:320–7.
Stone WB, Okoniewski JC, Stedelin JR. Poisoning of wildlife with anticoagulant rodenticides in New York. J Wildl Dis. 1999;35:187–93.
Rattner BA, Lazarus RS, Elliott JE, Shore RF, van den Brink N. Adverse outcome pathway and risks of anticoagulant rodenticides to predatory wildlife. Environ Sci Technol. 2014;48:8433–45.
Rattner BA, Mastrota FN. Anticoagulant rodenticide toxicity to non-target wildlife under controlled exposure conditions. In: van den Brink NW, Elliott JE, Shore RF, Rattner BA, editors. Anticoagulant rodenticides and wildlife. Cham: Springer International Publishing; 2018. p. 45–86.
Butler SE. The sub-lethal effects of second generation anticoagulant rodenticides on birds. Dissertation. Leicester: University of Leicester; 2010.
Riley SPD, Bromley C, Poppenga RH, Uzal FA, Whited L, Sauvajot RM. Anticoagulant exposure and notoedric mange in bobcats and mountain lions in urban southern California. J Wildl Manag. 2007;71:1874–84.
Franklin AB, Anderson DR, Gutiérrez RJ, Burnham KP. Climate, habitat quality, and fitness in northern spotted owl populations in northwestern California. Ecol Monogr. 2000;70:539–90.
Atsatt PR, Ingram T. Adaptation to oak and other fibrous, phenolic-rich foliage by a small mammal, Neotoma fuscipes. Oecologia. 1983;60:135–42.
Casano S, Grassi G, Martini V, Michelozzi M. Variations in terpene profiles of different strains of Cannabis sativa L. Acta Hortic. 2011;925:115–21.
Booth JK, Page JE, Bohlmann J. Terpene synthases from Cannabis sativa. PLoS ONE. 2017;12:e0173911.
Hemmes RB, Alvarado A, Hart BL. Use of California bay foliage by wood rats for possible fumigation of nest-borne ectoparasites. Behav Ecol. 2002;13:381–5.
Hart BL. Behavioural defences in animals against pathogens and parasites: parallels with the pillars of medicine in humans. Philos Trans Roy Soc B Biol Sci. 2011;366:3406–17.
Pavela R. Larvicidal property of essential oils against Culex quinquefasciatus Say (Diptera: Culicidae). Ind Crops Prod. 2009;30:311–5.
Pavela R. Essential oils for the development of eco-friendly mosquito larvicides: a review. Ind Crops Prod. 2015;76:174–87.
McPartland JM. Cannabis as repellent and pesticide. J Inter Hemp Assoc. 1997;4:87–92.
Meisel J. Hidden in plain sight: cannabis cultivation in the emerald triangle. Calif Geogr. 2017;56:1–26.
Zabel CJ, McKelvey K, Ward JP Jr. Influence of primary prey on home-range size and habitat-use patterns of northern spotted owls (Strix occidentalis caurina). Can J Zool. 1995;73:433–9.
Wang IJ, Brenner JC, Butsic V. Cannabis, an emerging agricultural crop, leads to deforestation and fragmentation. Front Ecol Environ. 2017;15:495–501.
ABF and KEH conceived the study and ABF drafted the initial manuscript. PCC, AR, JTR, DG and EC conducted field work and contributed additional information. RJD and VIS-B oversaw the necropsy while SFV conducted the laboratory analyses to detect rodenticides. MWG provided insights into marijuana production and additional information. All authors edited draft manuscripts and provided additional material. All authors read and approved the final manuscript.
We thank the Analytical Chemistry Project at the USDA National Wildlife Research Center and the USGS National Wildlife Health Center for providing logistical support. The use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U. S. Government.
The authors declare that they have no competing interests.
Availability of data and materials
Locations of northern spotted owls and private lands are not available because of threatened species restrictions and private land policies of USDA, respectively. Reports on necropsies and analyses for rodenticides are available from the USGS National Wildlife Health Center and the corresponding author.
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Ethics approval and consent to participate
This study was approved by the Institutional Animal Care and Use Committee of Colorado State University (Protocol #16-6968A) and the Quality Assurance Unit of the National Wildlife Research Center (Protocol #QA-2287).
Overall funding was provided by USDA Forest Service Region 5. The USGS National Wildlife Health Center provided funding for the necropsy.
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Franklin, A.B., Carlson, P.C., Rex, A. et al. Grass is not always greener: rodenticide exposure of a threatened species near marijuana growing operations. BMC Res Notes 11, 94 (2018). https://doi.org/10.1186/s13104-018-3206-z
- Spotted owl
- Secondary poisoning