Bacillus thuringiensis (Bt) is a naturally occurring soil bacterium that is used for its insecticidal action. When the Bt bacterium produces spores, it also creates protein crystals which it releases with the spores. The crystals and spores settle on surfaces in the environment such as plant leaves. The crystals dissolve in the insect's gut when it eats them. This activates the proteins. The proteins destroy the insect's gut cells and kill the insect. The spores germinate into new bacteria, which feed on the dead insect.1
This fact sheet describes Bt genes specifically used in genetically modified crops. These crops are also known as transgenic or bioengineered crops. For more information about Bt used on its own as an insecticide, please refer to our fact sheet on Bacillus thuringiensis (Bt).
What are genetically modified crops and plant-incorporated protectants?
Genetically modified crops have a gene inserted into the crop plant. The gene is usually from another organism. This is frequently done to make the plant resistant to insects, herbicides, or both.2 Some crops have been genetically modified to produce the substances found in Bt that are toxic to insects.
Plant-incorporated protectants, or PIPs, are one form of genetically modified crops.3 The plants have bits of Bt DNA inserted into their own DNA so that they make the Bt toxins in their own cells.4 The Bt toxin kills the insect when it feeds on the plant. Crops that have been genetically modified with Bt include corn, cotton, potatoes, and soybeans. The U.S. Environmental Protection Agency (U.S. EPA) regulates the proteins of the Bt toxin and the genes that help the plant produce the toxins. They do not regulate the modified plants.5
The part of the plant that produces the Bt toxins depends on two factors. First, it depends on where scientists insert the Bt gene into the plant's DNA. This is called the insertion event. Second, it depends on the promoter, or "genetic switch" scientists use. This affects where and how much Bt toxin will be made. Different combinations of insertion events and promoters create different varieties of Bt plants.6 Plant leaves, pollen, and root tissue may create Bt toxins.6,7,8
The first genetically modified crops with Bt were registered by the U.S. EPA in 1995. Genetically modified crops may include more than one Bt toxin. This helps prevent insects from developing resistance to the Bt toxins.9 These crops may also have more than one trait inserted into them. For example, a crop may be both resistant to herbicides and contain genes for Bt toxins as well.10
What happens to Bacillus thuringiensis (Bt) crops when they enter the body?
The U.S. EPA evaluated potential risks to human health. They concluded that eating crops that have been genetically modified to create Bt toxins is not expected to be harmful to people. This is because Bt toxins are proteins, and humans digest proteins quickly. Normal food processing also breaks down proteins.11,12
In addition, the toxins are activated when eaten by insects, which have alkaline guts with a pH of 9.0-10.5.13 Humans and other mammals have much more acidic conditions in their stomachs. Acid destroys the toxins.14
The U.S. EPA requires data from manufacturers to show that the Bt proteins are not likely to act as a food allergen. Studies also show that Bt proteins do not cause toxicity even when fed to test animals at very high doses. The information is meant to show that the Bt toxins will act like any other dietary protein.11
Scientists have exposed mice to very high doses of different Bt toxins in many different studies. The scientists saw no effects in mice that ate 576 to over 5000 mg/kg Bt toxins. The amount the mice ate depended on the specific study and Bt toxins used.15 See the text box about mg/kg.
What is mg/kg?: "Mg/kg" is a way to measure a chemical dose. This can tell us how toxic a chemical is. "Mg" means milligrams of a chemical. "Kg" means one kilogram of an animal's body weight. Something that is highly toxic may kill a person with a very small amount of chemical. If something is very low in toxicity, it may take much more for that same person to become very sick or die.
Scientists fed dairy cows a diet with 35% Bt corn for five weeks. They did not find the toxin proteins from the Bt corn in the muscles, milk, liver, or blood of the cows.16
Are children more sensitive to Bt than adults?
Children may be especially sensitive to pesticides compared to adults. However, there are currently no data showing that children are at increased risk specifically to Bt.11
Is consuming Bt crops likely to contribute to the development of cancer?
The toxin produced by Bt is a protein. Research has shown that eating proteins has not led to cancer, genetic mutations, or birth defects.15
Has anyone studied non-cancer effects from long-term exposure to eating crops that have been genetically modified to contain Bt?
Overall, there is no evidence that eating Bt crops has led to negative health effects in either test animals or humans.
Scientists reviewed studies that had exposed animals to Bt crops in their food for over 90 days or across generations. No effects were found in dairy cows, sheep, chickens, rats, or mice.17
Scientists have examined the effects of feeding Bt corn to pigs. Most studies on pigs found that Bt corn had no effects on them.18,19,20,21
- Scientists fed sows diets of 86% Bt corn through pregnancy until their piglets weaned at 28 days. The sows and their piglets weighed the same as sows and piglets eating non-Bt corn diets.19
- Mother pigs fed 75-87% Bt corn had piglets that in turn were fed Bt corn in their diets for 115 days. The piglets were as healthy and heavy as piglets raised on non-Bt corn.21
- Other scientists fed Bt corn to pigs for up to 110 days and found no effects on the pigs.20
- In another study, pigs that ate 39% Bt corn in their diets for one month needed more food than pigs who ate non-Bt corn. The pigs also gained less weight.18
Studies on rodents fed Bt corn found no effects on their health or reproduction. However, some studies showed small effects on the rodents' kidneys, livers, or body weight.22,23
- Scientists fed rats diets with no corn, 20% non-Bt corn, or 20% Bt corn for three generations. They did not see any effects in any of the newborn rats in each generation. The rats' behavior, health, and reproduction were the same among groups. The scientists saw some small differences in the kidneys and livers of rats fed the corn diets. The livers of rats fed the Bt corn were more affected.22
- Other scientists fed mice diets with either 68% Bt corn or non-Bt corn for five generations. The Bt corn diet did not affect growth, weight, lifespan, or reproduction in the mice. Mice in each generation weighed less than in previous generations no matter which type of corn they ate. Scientists thought that this was from the large amount of corn in their diets.23
Scientists fed four Holstein cows with 35% Bt corn for 5 weeks. They found no differences in milk yield, health, or the cows' rumens (their largest stomachs) compared to cows fed non-Bt corn.16
Chickens ate diets with 61% Bt corn for 12 weeks. Organ weights, body weights, organ health, and egg laying were not affected compared to hens who ate non-Bt corn.24
No scientific studies were found that examined the effects on human health from eating Bt crops. No other reports of negative effects from eating Bt crops were found.
What happens to Bt crops in the environment?
Bt is a naturally occurring soil bacterium, and its spores and the toxic proteins are already found in soils.
Bt crops and non-Bt crops take the same amount of time to break down in the environment.25 Environmental conditions such as rain, temperature, and contact with soil degrade crop residue. Crop residue includes the leaves, stems, and other plant matter remaining after harvest. Environmental factors were more important in how fast corn residue degraded rather than the presence of the Bt protein.26 For example, there was no difference in the breakdown of Bt corn and non-Bt corn in streams near corn fields.27
Farming practices after harvest affect how quickly Bt corn residue breaks down on the soil surface. How much crop residue was left also mattered.26 In one study, scientists measured toxins from Bt corn crop residue in soil in Switzerland. Bt toxins broke down slowly. The breakdown speed depended on temperature. Bt toxins did not break down in winter. After 200 days, in June, less than 1% of the Bt toxin remained in crop residues. In the first month after harvest, the Bt toxins degraded more rapidly when crop residues were left on the soil surface than when they were tilled into the soil.28
In a second study, scientists found that Bt toxins broke down most quickly when the crop residues were incorporated into the soil. They planted a Bt corn variety active against European corn borers. After harvest, they compared crop residue treatments such as no-till and tilling the field. The scientists fed crop residues to the European corn borer larvae 0-24 weeks after harvest. Larvae were 31-48% smaller than larvae eating crop residues from non-Bt corn. Crop residue from Bt corn that was tilled under the soil surface affected the larvae the least.26
Although Bt crops can release Bt toxic proteins from their roots, effects to the soil microbiome seem to be limited.
- In one study, scientists found that the bacteria in the soil around the plant roots were more affected by the plants' ages and field conditions than by the presence of Bt crops.29
- In another study, scientists found that the soil bacteria were affected by Bt cotton compared to non-Bt cotton and wheat. The soil bacteria community overall did not change in abundance. However, the types of bacteria did change relative to each other. This also changed soil functions.30
- Studies have concluded that the toxic proteins produced by Bt crops did not affect soil microorganisms, including protozoa, fungi, bacteria, or larger organisms such as earthworms and nematodes. Farming practices themselves may have large impacts on soil and soil microbial communities.11
Can Bt crops affect birds, fish, and other wildlife?
Although some laboratory studies suggest Bt crops might have negative impacts on non-target insects that are closely related to the target pest, most field studies have not shown effects.31 Scientists reviewed studies looking at the effects of Bt plants on insects, microbes, and worms. Most studies they reviewed did not find any effects on non-target organisms unless the non-target organisms were closely related to the pest controlled by the Bt toxins.32,33
The U.S. EPA concluded that published studies and data submitted by manufacturers showed "minimal to undetectable changes" to non-target insect populations, including beneficial insects.11
Butterflies
At first some scientists were worried that monarch butterfly larvae could be harmed by Bt corn pollen. They concluded in the same study that the risk of exposure to Bt pollen was low for black swallowtail butterflies, another endangered species. However, the scientists thought that other endangered butterflies that are sensitive to Bt and exposed to Bt pollen could be impacted.8 Other scientists determined that the actual risks to monarch butterflies were low because the butterflies would not be likely to encounter the pollen and that current corn hybrids are low in toxicity to the monarch butterflies.34 One type of Bt corn that scientists found may harm monarch butterflies35 is no longer sold.5
Honeybees
Scientists reviewed 64 published studies, and 18 unpublished studies provided to the U.S. EPA. These studies looked at the risk to honeybees from pollen and nectar of Bt crops. The scientists concluded that Bt crops should not affect honeybees.36
Parasitic wasps
Scientists studied whether parasitoid wasps were affected by preying on host insect larvae that ate Bt plants. Parasitic wasps lay their eggs on their host insects. When the eggs hatch, they eat the host. Most studies found no effects. Other scientists in one study found that the wasps did not develop well in hosts that fed on Bt plants. They thought this was because the hosts were not healthy rather than an effect of the Bt toxins on the wasp larvae.8 Another study looked at a parasitic wasp that feeds on southern armyworms. The wasps were not affected when the armyworm larvae ate Bt soy plants.37
Predatory insects
Many scientists have asked whether Bt crops affected predatory insects. Very few studies have shown negative effects.
One scientist reviewed many studies to determine whether Bt crops affected non-target insects such as the predators of pest insects. The scientist found that predatory insects were harmed if a Bt crop was used to control their prey. If the prey insect was not controlled by the Bt crop, the predator was not affected. The review concluded that the predators were not harmed by the Bt toxins directly, but through the loss of their prey.31
One study reported that more ladybug larvae died when they ate prey eggs sprayed with Bt toxins than larvae who ate unsprayed eggs.38 However, another group of scientists fed ladybug larvae with spider mites that had been raised either on Bt corn, regular corn, or sugar spiked with the Bt toxins. Bt corn or sugar did not harm the ladybug larvae. The scientists thought that the previous study had design problems because ladybug larvae do not usually eat the shells of eggs.33
Aquatic insects
Overall, there is little evidence that Bt toxins from crop residue could harm aquatic insects.
Crop residue and pollen from Bt corn crops can be found in streams, where aquatic insects may eat them. Scientists used toxicity data and environmental fate data to model the likelihood that Bt toxins from crops would harm aquatic insects. Even when they modeled worst-case concentrations of Bt toxins in aquatic systems, they found that "there is a reasonable certainty of no harm" in 99% of cases for sensitive species.39 A second risk assessment by other scientists modeling worst-case conditions also concluded that the exposure risks were very low.40
Scientists studied caddisflies in the laboratory and in streams. Caddisflies are aquatic insects whose larvae shred leaves or scrape rocks. Most studies found no effects from Bt crop residue.
- Scientists fed Bt corn crop residue to caddisfly larvae in the laboratory. They grew more slowly than insects fed non-Bt corn crop residue.27 However, the study was criticized because the scientists did not use proper controls.41
- Other scientists who exposed aquatic insects to Bt corn residue did not find effects to the insects from eating the Bt toxins in the residue. The researchers in that study used a better control treatment. Although this study showed negative effects in the insects, the scientists involved felt that other factors were responsible.42
- Caddisflies that shred leaves were not affected by Bt corn residue in streams in Bt corn fields versus non-Bt corn fields. The scientists thought that other environmental factors were more important.43 Another species of caddisfly that scrapes algae from rocks was tested in the laboratory. It was not affected by Bt toxins at levels that were found in streams.27
Earthworms
Earthworms ate Bt corn crop residue for 200 days in the laboratory and in the field. Juvenile worms in the field were not affected. Adult worms in the laboratory gained less weight than control worms after 160 days. The scientists thought that either food quality was lower or that the Bt toxin was finally affecting the worms after they grew up being exposed to it.44
Birds
Japanese quail ate feed with 40-50% Bt corn for 10 generations. Scientists did not see any effects on health, meat or egg quality, laying performance, or egg hatching in any of the generations.45 Another 10-generation feeding study of Japanese quail compared diets of Bt corn, soybeans modified to resist herbicide, and conventional soybeans and corn. The researchers found no differences in hatching, survival, or body weight in quail across treatments. Quail fed Bt corn had slightly heavier breast muscle. More quail in the Bt corn group laid eggs.46
Fish
A review of several studies concluded that Bt corn fed to fish had no effects on development, growth, or survival although some individual fish in the Bt corn groups showed slight signs of stress in their enzymes and blood.47
- A study using Atlantic salmon studied health effects of using Bt maize in the fish's diet. Growth rates among all fish did not differ. The fish fed Bt maize showed changes in white blood cells that may have indicated an immune response.48
- Scientists exposed zebrafish embryos to two different Bt toxins. The Bt toxins did not affect egg hatch rates, development, or body length at hatching.49
- Other scientists fed zebrafish diets including Bt corn for two generations. Half of the offspring were fed Bt corn, and the other half were fed non-Bt corn. Fish in the first generation were not affected by the Bt corn. If both generations of fish ate Bt corn, the second generation grew faster.50
- Researchers tested both soy and Bt corn diets on the growth and development of young Atlantic salmon. They fed the fish these diets for 99 days and tested the fish throughout. Fish had minor changes in their intestine function. The researchers concluded that there were no effects of Bt corn on the general health of the fish.51
For more detailed information about Bt in Genetically Modified Crops please visit the referenced resources below, call NPIC at 800-858-7378, Monday - Friday, 8:00am-12:00pm PT (11:00am-3:00pm Eastern Time) , email us at npic@oregonstate.edu, or visit us at npic.orst.edu. NPIC provides objective, science-based answers to questions about pesticides.
Date Reviewed: March 2025
Please cite as: Gervais, J.; Reyes, P.; Cocks, M.; Mermer, S. 2025. Bacillus thuringiensis (Bt) in Genetically Modified Crops Fact Sheet; National Pesticide Information Center, Oregon State University Extension Services. npic.orst.edu/factsheets/bt-pip.html
- Rudd, S. R.; Miranda, L. S. et al. The Parasporal Body of Bacillus Thuringiensis Subp. Israelensis: A Unique Phage Caspid-Associated Prokaryotic Insecticidal Organelle. Biology 2023, 12 (11), 1421.
- de Vos, C. J.; Swaneburg, M. Health Effects of Feeding Genetically Modifed (GM) Crops to Livestock Animals: A Review. Food Chem Toxicol 2018, 117, 3–12.
- Yu, S. J. Systemic Classification of Insecticides. The Toxicology and Biochemistry of Insecticides; CRC Press, Taylor and Frances Group, 2008; pp 25–86.
- Byrne, P. Genetically Modified (GM) Crops: Techniques and Applications, Fact Sheet No. 0.710; Colorado State University Extension: Fort Collins, CO, 2014.
- Current and Previously Registered Section 3 Plant-Incorporated Protectant (PIP) Registrations; U.S. Environmental Protection Agency, Office of Chemical Safety and Polluntion Prevention, U.S. Government Printing Office: Washington, DC, 2024.
- Peairs, F. B. Managing Corn Pests with Bt Corn. Fact Sheet No. 0.708; Colorado State University Extension: Fort Collins, CO, 2014.
- Fearing, P. L.; Brown, D.; Vlachos, D.; Privalle, L. Quantitative Analysis of Cry1A(b) Expression in Bt Maize Plants, Tissues, and Silage and Stability of Expression over Successive Generations. Mol Breeding 1997, 3, 169–176.
- Clark, B. W.; Phillips, T. A.; Coats, J. R. Environmental Fate and Effects of Bacillus Thuringiensis (Bt) Proteins from Transgenic Crops: A Review. J Agric Food Chem 2005, 53 (12), 4643–4653.
- Sanahuja, G.; Banakar, R.; Twyman, R. M.; Capell, T.; Christou, P. Bacillus Thuringiensis: A Century of Research, Development and Commercial Applications. Plant Biotechnol Journal 2011, 9, 283–300.
- Parker, K. M.; Sander, M. Environmental Fate of Insecticidal Plant-Incorporated Protectants from Genetically Modified Crops: Knowledge Gaps and Research Opportunities. Environ Sci Technol 2017, 51, 12049–12057.
- Biopesticides Registration Action Document: Bacillus Thuringiensis (Bt) Plant-Incorporated Protectants; U.S. Environmental Protection Agency, Office of Pesticide Programs, U.S. Government Printing Office: Washington, DC, 2001.
- Mendelsohn, M.; Kough, J.; Vaituzis, Z.; et al. Are Bt Crops Safe? Nature 2003, 21 (9), 1003–1009.
- Bacillus Thuringiensis Reregistration Eligibility Decision; U.S. Environmental Protection Agency, Office of Prevention, Pesticides, and Toxic Substances, U.S. Government Printing Office: Washington, DC, 1998.
- Drobniewski, F. A. The Safety of Bacillus Species as Insect Vector Control Agents. J Appl Bacteriol 1994, 76, 101–109.
- Koch, M. S.; Ward, J. M.; Levine, S. L.; Baum, J. A.; Vicini, J. L.; Hammond, B. G. The Food and Environmental Safety of Bt Crops. Front. Plant Sci. 2015, 6 (283).
- Yonemochi, C.; Ikeda, T.; Kusama, T.; Hanazumi, M. Influence of Transgenic Corn (CBH 351, Named Starlink) on Health Condition of Dairy Cows and Transfer of Cry9C Protein and cry9C Gene to Milk, Blood, Liver and Muscle. Anim Sci J 2003, 74 (2), 81–88.
- Snell, C.; Bernheim, A.; Berge, J.-B.; Kuntz, M.; Pascal, G.; Paris, A.; Ricroch, A. E. Assessment of the Health Impact of GM Plant Diets in Long-Term and Multigenerational Animal Feeding Trials: A Literature Review. Food Chem Toxicol 2012, 50, 1134–1148.
- Walsh, M. C.; Buzoianu, S. G.; Gardiner, G. E.; Rea, M. C.; Ross, R. P.; Cassidy, J. P.; Lawlor, P. G. Effect of Short-Term Feeding of Bt MON810 Maize on Growth Performance, Organ Morphology and Function in Pigs. Brit J Nutr 2012, 107, 364–371.
- Walsh, M. C.; Buzoianu, S. G.; Gardiner, G. E.; Rea, M. C.; O'Donovan, R. P. R.; Lawlor, P. G. Effects of Feeding Bt MON810 Maize to Sows during First Gestation and Lactation on Maternal and Offspring Health Indicators. Brit J Nutr 2013, 109, 873–881.
- Buzoianu, S. G.; Walsh, M. C.; Rea, M. C.; Cassidy, J. P.; Ross, R. P.; Gardiner, G. E.; Lawlor, P. G. Effect of Feeding Genetically Modified Bt MON810 Maize to 40-Day-Old Pigs for 110 Days on Growth and Health Indicators. Animal 2012, 6 (10), 1609–1619.
- Buzoianu, S. G.; Walsh, M. C.; Rea, M. C.; Cassidy, J. P.; Ryan, T. P.; Ross, R. P.; Gardiner, G. E.; Lawlor, P. G. Transgenerational Effects of Feeding Genetically Modified Maize to Nulliparous Sows and Offspring on Offspring Growth and Health. J Anim Sci 2013, 91, 318–330.
- Kilic, A.; Akay, M. T. A Three Generation Study with Genetically Modified Bt Corn in Rats: Biochemical and Histopathological Investigation. Food Chem Toxicol 2008, 46, 1164–1170.
- Haryu, Y.; Taguchi, Y.; Itakura, E.; Mikami, O. et al. Longterm Biosafety Assessment of a Genetically Modified (GM) Plant: The Genetically Modified (GM) Insect-Resistant Bt11 Corn Does Not Affect the Performance of Multi-Generations or Life Span of Mice. Open Plant Sci J 2009, 3, 49–53.
- Zhong, R. Q.; Gao, L. X.; Zhang, L. L. et al. Effects of Feeding Transgenic Corn with mCry1Ac or maroACC Gene to Laying Hens for 12 Weeks on Growth, Egg Quality, and Organ Health. Animal 2016, 10 (8), 1280–1287.
- Yanni, S. F.; Whalen, J. K.; Ma, B. L. Crop Residue Chemistry, Decomposition Rates, and CO2 Evolution in Bt and Non-Bt Corn Agroecosystems in North America: A Review. Nutr Cycl Agroecosyst 2010, 277–293.
- Yurchak, V.; Leslie, A. W.; Dively, G. P.; Lamp, W. O.; Hooks, C. R. R. Degradation of Transgenic Bacillus Thuringiensis Proteins in Corn Tissue in Response to Post-Harvest Management Practices. Transgenic Res 2021, 30, 851–865.
- Rosi-Marshall, E. J.; Tank, J. L.; Royer, T. V.; Whiles, M. R.; Evans-White, M.; Chambers, C.; Griffiths, N. A.; Pokelsek, J.; Stephen, M. L. Toxins in Transgenic Crop Byproducts May Affect Headwater Stream Ecosystems. P Natl A Sci 2007, 104 (41), 16204–16208.
- Zwahlen, C.; Hilbeck, A.; Gugerli, P.; Nentwig, W. Degradation of the Cry1Ab Protein within Transgenic Bacillus Thuringiensis Corn Tissue in the Field. Mol Ecol 2003, 12, 765–775.
- Baumgarte, S.; Tebbe, C. C. Field Studies on the Environmental Fate of the Cry1Ab Bt-Toxin Produced by Transgenic Maize (MON810) and Its Effect on Bacterial Communities in the Maize Rhizosphere. Mol Ecol 2005, 14, 2539–2551.
- Lv, N.; Guo, T.; Liang, P., et al. The Influence of Bt Cotton Cultivation on the Structure and Functions of the Soil Bacterial Community by Soil Metagenomics. Ecotoxicol Environ Safety 2022, 236, 113452.
- Naranjo, S. E. Impacts of Bt Crops on Non-Target Invertegrates and Insecticide Use Patterns. CAB Rev: Perspectives in Agriculture, Veterinary Science, Nutrition, and Natural Resources 2009, 4, article 011.
- Yaqoob, A.; Shahid, A. A.; Samiullah, T. R.; Rao, A. Q.; Khan, M. A. U.; Tahir, S.; Mirza, S. A.; Husnain, T. Risk Assessment of Bt Crops on the Non-Target Plant-Associated Insects and Soil Organisms. J Food Agr Sci 2016, 96, 2613–2619.
- Alvarez-Alfageme, F.; Bigler, F.; Romeis, J. Laboratory Toxicity Studies Demonstrate No Adverse Effects of Cry1Ab and Cry3Bb1 to Larvae of Adalia Bipunctata (Coleoptera: Coccinellideae): The Importance of Study Design. Trans Res 2011, 20, 467–479.
- Sears, M. K.; Hellmich, R. L.; Stanley-Horn, D. E.; Oberhauser, K. S.; Pleasants, J. M.; Mattila, H. R.; Siegfried, B. D.; Dively, G. P. Impact of Bt Corn Pollen on Monarch Butterfly Populations: A Risk Assessment. P Natl A Sci 2001, 98 (21), 11937–11942.
- Stanley-Horn, D. E.; Dively, G. P.; Hellmich, R. L.; Mattilla, H. R.; Sears, M. K.; Rose, R.; Jesse, L. C. H.; Losey, J. E.; Obrycki, J. J.; Lewis, L. Assessing the Impact of Cry1Ab-Expressing Corn Pollen on Monarch Butterfly Larvae in Field Studies. P Natl A Sci 2001, 98 (21), 11931–11936.
- Ricroch, A., S. Akkoyunlu, J. Martin-Laffon, and M. Assessing the Environmental Safety of Transgenic Plants: Honey Bees as a Case Study. Adv Bot Res 2018, 86, 111–167.
- Bortolotto, O. C.; Silva, G. V.; de Freitas Bueno, A.; Pomari, A. F.; Martinelli, S.; Head, G. P.; Carvalho, R. A.; Barbosa, G. C. Development and Reproduction of Spodoptera Eridania (Lepidoptera: Noctuidae) and Its Egg Parasitoid Telenomus Remus (Hymenoptera: Platygastridae) on the Genetically Modified Soybean (Bt) MON 87701xMon 89788. B Entmol Res 2014, 104, 724–730.
- Schmidt, J. E. U.; Braun, C. U.; Whitehouse, L. P.; Hilbeck, A. Effects of Activated Bt Transgene Products (Cry1Ab, Cry3Bb) on Immature Stages of the Ladybird Adalia Bipunctata in Laboratory Ecotoxicity Testing. Arch Environ Con Tox 2009, 221–228.
- Wolt, J. D.; Peterson, R. K. D. Prospective Formulation of Environmental Risk Assessments: Probabilistic Screening for Cry1A(b) Maize Risk to Aquatic Insects. Ecotoxicol Environ Safe 2010, 73 (6), 1182–1188.
- Carstens, K.; Anderson, J.; Bachman, P.; De Schrijver, A.; Dively, G.; Federici, B.; Hamer, M.; Gielkens, M.; Jensen, P.; Lamp, W.; Rauschen, S.; Ridley, G.; Waggoner, A. Genetically Modified Crops and Aquatic Ecosystems: Considerations for Environmental Risk Assessment and Non-Target Organism Testing. Trans Res 2012, 21, 813–842.
- Beachy, R. N.; Fedoroff, N. V.; Goldberg, R. B.; McHughen, A. The Burden of Proof: A Repsonse to Rosi-Marshall et Al. P Natl A Sci 2008, 105 (7), E9.
- Jensen, P. D.; Dively, G. P.; Swan, C. M.; Lamp, W. O. Exposure and Nontarget Effects of Transgenic Bt Corn Debris in Streams. Environ Entomol 2010, 39 (2), 707–714.
- Chambers, C. P.; Whiles, M. R.; Rosi-Marshall, E. J.; Tank, J. L.; Royer, T. V.; Griffiths, N. A.; Evans-White, M. A.; Stojak, A. R. Responses of Stream Macroinvertebrates to Bt Maize Leaf Detritus. Ecol Appl2010, 20 (7), 1949–1960.
- Zwahlen, C.; Hilbeck, A.; Howard, R.; Nentwig, W. Effects of Transgenic Bt Corn Litter on the Earthworm Lumbricus Terrestris. Mol Ecol 2003, 12, 1077–1086.
- Flachowsky, G.; Halle, I.; Aulrich, K. Long Term Feeding of Bt-Corn - a Ten-Generation Study with Quails. Arch Anim Nutr 2005, 59 (6), 449–451.
- Sartowska, K. E.; Korwin-Kossakowska, A.; Sender, G. Genetically Modified Crops in a 10-Generation Feeding Trial on Japanese Quails - Evaulation of Its Influence on Birds' Performance and Body Composition. Poultry Sci 2015, 94, 2909–2916.
- Venter, H. J.; Bohn, T. Interactions between Bt Crops and Aquatic Ecosystems: A Review. Environ Toxicol Chem 2016, 35 (12), 2891–2902.
- Sagstad, A.; Sanden, M.; Haugland, O.; Hansen, A.-C.; Olsvik, P. A.; Hemre, G.-I. Evaluation of Stress- and Immune-Response Biomarkers in Atlantic Salmon, Salmo Salar L., Fed Different Levels of Genetically Modified Maize (Bt Maize), Compared with Its near-Isogenic Parental Line and a Commercial Suprex Maize. J Fish Dis 2007, 30, 201–212.
- Gao, Y.-J.; Chen, Y.; Li, Y.-H.; Peng, Y.-F.; Chen, X.-P. Safety Assessment of Bacillus Thuringiensis Insecticidal Proteins Cry1C and Cry2A with a Zebrafish Embryotoxicity Test. J Ag Food Chem 2018, 66, 4336–4344.
- Sanden, M.; Ornsrud, R.; Sissener, N. H.; Jorgensen, S.; Gu, J.; Bakke, A. M.; Hemre, G.-I. Cross-Generational Feeding of Bt (Bacillus Thuringiensis)-Maize to Zebrafish (Danio Rerio) Showed No Adverse Effects on the Parental or Offspring Generations. Brit J Nutr 2013, 110, 2222–2233.
- Gu, J.; Bakke, A. M.; Valen, E. C.; Lein, I.; Krogdahl, A. Bt-Maize (MON810) and Non-GM Soybean Meal in Diets for Atlantic Salmon (Salmo Salar L.) Juveniles- Impact on Survival, Growth Performance, Development, Digestive Function, and Transcriptional Expression of Intestinal Immune and Stress Responses. PloS One 2014, 9 (6), e99932.
NPIC fact sheets are designed to answer questions that are commonly asked by the public about pesticides that are regulated by the U.S. Environmental Protection Agency (US EPA). This document is intended to be educational in nature and helpful to consumers for making decisions about pesticide use.