Aquaculture and Its Impact on the Environment

Authors: Brianna Healey, Pre-Veterinary Sciences; Will Dell’Erba, Forestry; Kurt Leavitt, Building and Construction Technology

Americans consume 4.8 billion pounds of seafood annually, and 90% of the fish consumed in the U.S. comes from China and overseas (Fish Watch, n.d.). Recently, seafood consumption has gone up steadily as fish are viewed as a healthy protein source (NOAA, n.d.). While this is good for our personal health, it is causing extreme impacts on ocean fish populations. Scientists predict that if overfishing continues at its current rate, wild populations will be down 90% by the year 2050 (One green planet, n.d.). The pressure must be taken off the ocean and freshwater fish that we love to eat, and a viable solution to this problem is aquaculture. Aquaculture is now necessary to meet the demands for seafood in the United States (Cousteau, 2014). Continue Reading

What is making birds drop from the sky?

Maria Mounsey- Wildlife Ecology

Benjamin Gontijo- Animal Science

Matthew Bieda- BCT

Shoulders hunched, neck lowered, a predator stalks its prey. Long claws imbed into the soft dirt below. One, two, three steps, a slow lower to the ground, stalking, waiting in silence. A long tail trails behind an athletic and deadly body, softly, it playfully swishes back and forth. Wait. wait. Wait. Locking large, round, golden eyes on its target, a slight pur escapes. Next is a flurry of feathers and cries. As the rustling begins to slow, the predator admires its kill, carefully pacing around it, pawing at the spread wingspan. Ruthlessly, the predator claws at the kill, pondering what to do with it, as the feathery mess lets out one last breath. Continue Reading

Impact of Antibiotic use in Concentrated Animal Feeding Operations on Human Health

Jessica Michalek, Pre-Veterinary Sciences

John McCluskey, Plant and Soil Sciences

Kelsey Beauregard, Natural Resource Conservation

Salmonella is a disease that is becoming increasingly more common and dangerous. A young boy named Noah Craten was just 18 months old when he was infected with salmonella. This particular strain of salmonella was antibiotic resistant and very difficult to treat. He had to be hospitalized and undergo brain surgery due to a large mass of blood forming in his brain that nearly killed him. He had a line placed directly in his heart and received antibiotics for seven weeks in order to save his life. As a result  the left side of his face now sags and he has a permanent scar on the top of his skull. He also has cerebral spinal fluid in his brain that must be monitored frequently by a physician. This boy suffered greatly and he is not the only one. This particular salmonella outbreak led to double the normal hospitalization rates due to the antibiotic resistance (Terry, L., 2015).

The effects of foodborne diseases are already serious. In the United States alone, salmonella species infections are responsible for about 1.4 million illnesses, 15,000 hospitalizations and 400 deaths annually (Voetsch et al., 2004). Increased prevalence of a multidrug resistant type of salmonella has been found, this poses a major health concern to humans as it is making it harder to treat (Aarestrup et al., 2007). This type of salmonella is an uncommon cause of salmonella in humans worldwide, however in recent years this type now ranks among the most frequently identified salmonella type in several countries. It was the fifth most common type isolated from retail meat in the United States (Aarestrup et al., 2007). This shows that the acquired drug resistance of salmonella enabled it to survive in new environments. There was a reported increase in the proportion of human infections from this type of salmonella  in Thailand, from 0% in 1992 to 2.4% in 2001 (Aarestrup et al., 2007, p. 726). This is significant as it shows an increase in both prevalence and potency of a bacteria due to drug resistances, and it is a prime example of how antibiotic resistance enabled a once irrelevant type of bacteria to become strong enough to pose a threat to human health.

Noah Craten was infected with salmonella from a package of Foster Farms chicken raised on concentrated animal feeding operation (CAFO). When we think of farms we tend to imagine a lot of land and animals grazing. This is not the case for CAFOs. CAFOs are operations where large groups of animals are fed specific diets and not grazing on the land. These operations must have thousands of animals to be considered concentrated. A poultry CAFO would have over 82,000 animals on site and a swine operation would have over 2500 animals (“Natural Resources Conservation Service”, n.d.). These operations have incredibly large numbers of animals going through them and all these animals are fed a specific diet chosen by the producer. The main goal of these operations is to produce large animals to sell for slaughter.

Since CAFOs have such a high volume of animals the animals are more likely to get sick. In order to avoid this, producers put subtherapeutic levels of antibiotics in the animals feed. Feeding subtherapeutic levels of antibiotics means that the producers are not using them to treat an illness, but to promote growth and production in the animals (Gunther, 2013). When you treat an animal with low levels of antibiotics it wipes out all the weak bacteria but the levels are not high enough to destroy the stronger bacteria. This leads to us selecting for only the strongest bacteria that are naturally resistant and will pass their genes on (Nowakowski, 2015). This is a problem that can affect everyone in some way regardless of whether or not you eat meat.

CAFOs have been found to create antibiotic resistance. One study tested over thirty different CAFOs for nine different antibiotic resistant genes and resistance was found at all locations (Brooks, Adeli, and McLaughlin, 2014). Another study sampled retail ground meat and found 84% to be resistant to at least one antibiotic and 53% to be resistant to at least three (White et al., 2001, p. 1148).  A third study found bacteria that is not only resistant to the average antibiotic, but is also cross resistant to an antibiotic used as a last resort to treat multidrug-resistant infections (Chapin, Rule, Gibson, Buckley, and Schwab, 2005).  They also tested for resistance of different antibiotics, some that are used in the swine industry and one that is not (Chapin et al., 2005).  Their results show that CAFOs do indeed create antibiotic resistance because the antibiotics used in CAFOs had resistance whereas the antibiotic that was not used had no resistance (Chapin et al., 2005, p. 139). One final example of antibiotic feed leading to resistance is the use of a class of antibiotics, in poultry, which led to the development of resistant strains (Cronin, 2013). Previously, this class of antibiotics were not used by CAFOs and there was not resistance found;  however, once CAFOs began using them, they found resistance (Cronin, 2013). There is a consensus among scientists that CAFOs create antibiotic resistance.

CAFOs are not only creating antibiotic resistant bacteria but they inevitably spread it to the human population. Transfer occurs in multiple different ways including through meat and the environment. Samples of ground meat tested positive for different strains of salmonella and  antibiotic resistance.  Five different strains of salmonella were identified in the meats that are resistant to nine different types of antibiotics (White et al., 2001). If someone eats this meat and the salmonella is not killed they would get very sick with an antibiotic resistant bacteria. This bacteria is difficult to treat and may not respond to a simple round of antibiotic treatment. These meats all came from different CAFOs and had been processed at different slaughterhouses showing that this is a widespread problem (White et al., 2001). It is not just one or two operations causing the problem it is the whole system of feeding antibiotic feed. Research was done to test the quality of air inside a swine CAFO. They found that there were very high levels of antibiotic resistant bacteria inside the operations themselves (Chapin et al., 2005). Research further proved this by comparing levels of antibiotic resistant bacteria inside the CAFO to areas upwind from the facility; they found concentrations of multidrug resistant bacteria to be 2.1 times higher inside the facility (Gibbs et al., 2006, p. 1034). This means that people who work in the facility are exposed to these high levels of resistance everyday and could easily transmit an antibiotic resistant strain to people outside the facility. Inhalation of these bacteria could lead to the sick person having almost no treatment options (Chapin et al., 2005). These multidrug resistant bacteria are not just found inside the operations, they are also found in the air around the facility and affect the nearby communities. It was found that the same high concentrations of multidrug resistant bacteria can be found 150 meters downwind of the facility (Gibbs et al., 2006). The antibiotic resistance can truly affect anyone. Not eating meat does not protect you from exposure to antibiotic resistant bacteria.

The United States needs to enforce bans on antibiotic feed used in livestock operations, especially restricting the use of antibiotics that are vital to human medicine. It is important to monitor our levels of antibiotics and what we are using them for. The United states currently does not keep records on antibiotic usage so farmers are not being held responsible for what they use. In order to get a handle on our antibiotic use we need to ban the subtherapeutic use of antibiotics and even regulate what antibiotics are given to livestock to treat diseases. It would be best to use ones that are not common in human medicine. Most importantly the United States needs to track its usage in order to make a difference.

In Europe antibiotic resistance has already been noticed and steps have been taken towards fixing it. Denmark in particular has made huge strides in reducing their antibiotic resistance and the United States should follow their lead. The use of antibiotic feed in CAFOs leads to more antibiotic resistant bacteria being spread and adopting the same standards as Denmark will help protect human lives in the United States. Denmark is the world’s leading exporter of pork and they banned all subtherapeutic uses of antibiotics in swine by 1999. Since these bans they have found significant decreases in levels of antibiotic resistant bacteria (Levy, 2014). “From 1992 to 2008, antibiotic use per kilogram of pig raised in Denmark dropped by more than 50%. Yet overall productivity increased. Production of weaning pigs increased from 18.4 million in 1992 to 27.1 million in 2008” (Levy, 2014, para. 15). They did not just ban the use of antibiotics for growth promotion, but also limited their use for disease prevention (Charles, 2012). While cost of raising these animals has gone up by about $1.14 the animals have lower disease rates and more efficient production (Levy, 2014, para. 16).  Human health should be prioritized over economic gain. Denmark closely regulates the amounts of antibiotics used and the types given to the animals.

Despite all of the scientific consensus on antibiotic resistance and how it poses a serious problem for humans humans, there are still some concerns that should be addressed.  One major concern is if the use of antibiotics is stopped then the cost of meat will increase. In 1999 it was estimated that it would have cost CAFOs $45.5 million if the drug use was banned (PBS, 2014, para. 18). However, this is including their profit, not all of that would be passed on to consumers. Also, feed that does not contain antibiotics costs 1 penny less per chicken, with the cost also being less in other animals (Parsons, 2007). Unfortunately, the American people may need to accept that they will have to pay a bit more for their meat in order to properly take care of their health like Denmark has. Denmark also managed to increase their production using their new system and the same could happen in the United States (Levy, 2014). If no change occurs, drug resistance will become more of a problem then it already is and we will be unable to find cures for our sickness, which would result in families spending hundreds if not thousands of dollars trying to find an answer to the sickness.

 A second concern of sceptics is the ever growing demand for more food. Ultimately, the use of antibiotics in feed only leads to about a 3 percent increase in size of the animals, which is really not substantial (PBS, 2014). As stated previously, Denmark is still the lead exporter of pork despite banning all subtherapeutic antibiotic use. CAFOs first came into existence in the 1970’s by chicken producers and were created so they could have a large number of animals and decrease production costs (History of CAFOs, 2011). However, we do not need them in order to produce enough animals to feed our population. Denmark evolved their way of farming so that they could still produce large amounts of pork for the population. So, despite popular belief antibiotic feed is not the answer to how we will feed the growing population.

Another concern to address is people wondering how we will treat sick animals without the use of antibiotic feed. This is actually quite simple to address. The main concern of antibiotic resistance comes from antibiotic feed, not injections, which is what is used to treat sick animals. Antibiotic feed is used as a growth hormone and preventative measure, not to treat sickness. As long as the antibiotics are used to treat disease and this is monitored by a veterinarian to make sure the antibiotics are not misused they can still be used to treat diseases in animals.

One final concern could be whether or not the way Denmark is handling eliminating antibiotic feed and resistance is transferable to the United States. The answer to that concern is yes, the American people just need to focus their priorities on protecting their health and their family’s health. Denmark simply changed the way they look at farming. In order to be successful without antibiotic feed they had to move away from the CAFO style of production. When animals are all kept close together there is a higher risk of disease spread, therefore they have moved into a more spacious style of farming (Kennedy, 2011). The United States could easily do this as we have significantly more land than Denmark that we could put towards farming. Instead of containing lots of animals in small spaces we could allow them to have space and significantly decrease the need for antibiotics in the first place.

Antibiotic resistant bacteria are a major health threat because they make it harder to treat illnesses caused by these bacteria. CAFOs are closed off, high volume operations and the animals in them are more likely to get sick. The sub-therapeutic levels of antibiotics which are put into these animals feed has led to an increase in antibiotic resistant bacteria, this is why the US needs to adopt the same standards as Denmark and ban all sub-therapeutic use of antibiotics in livestock operations. Doing so will decrease antibiotic resistant bacteria levels and make livestock products safer for humans.

 

References

 

Aarestrup, F.M., Hendriksen, R.S., Lockett, J., Gay, K., Teates, K., McDermott, P.F., …Gerner-Smidt, P. (2007). International spread of multidrug-resistant Salmonella Schwarzengrund in food products. Emerging Infectious Diseases, 13(5), 726-731. doi: 10.3201/eid1305.061489

Brooks, J. P., Adeli, A., & McLaughlin, M. R. (2014). Microbial ecology, bacterial pathogens, and antibiotic resistant genes in swine manure wastewater as influenced by three swine management systems. Water Research, 57, 96-103. doi:http://dx.doi.org/10.1016/j.watres.2014.03.017

Chapin, A., Rule, A., Gibson, K., Buckley, T., & Schwab, K. (2005). Airborne multidrug-resistant bacteria isolated from a concentrated swine feeding operation. Environmental Health Perspectives, 113(2), 137-142. doi:10.1289/ehp.7473

Charles, D. (2012, March 23). Europe’s Mixed Record on Animal Antibiotics. New England Public Radio. Retrieved from http://www.npr.org/sections/thesalt/2012/03/23/149221287/europes-mixed-record-on-animal-antibiotics

Cronin, J. (2013, September 17). Antibiotics & Human Disease: The CAFO Connection. Retrieved April 03, 2016, from https://earthdesk.blogs.pace.edu/2013/09/17/antibiotics-human-disease-the-cafo-connection/

Gibbs, S. G., Green, C. F., Tarwater, P. M., Mota, L. C., Mena, K. D., & Scarpino, P. V. (2006). Isolation of antibiotic-resistant bacteria from the air plume downwind of a swine confined or concentrated animal feeding operation. Environmental Health Perspectives, 114(7), 1032-1037.doi:10.1289/ehp.8910

Gunther, A. (2013). Is The Antibiotic Free Campaign Really “Antibiotic Free” Or Will It Just Create A Two Tier Food System? Retrieved from http://animalwelfareapproved.org/2013/04/01/is-the-antibiotic-free-campaign-really-antibiotic-free-or-will-it-just-create-a-two-tier-food-system/

History of CAFOs. (2011, October 22). Retrieved from http://www.world-foodhistory.com/2011/10/history-of-cafos.html

Kennedy, M. (2011, June 21). Finally: Putting the CAFO out to Pasture. Retrieved from https://thesesaltyoats.com/posts/food_culture_and_politics/finally-putting-the-cafo-out-to-pasture

Levy, S. (2014, June). Reduced Antibiotic Use in Livestock: How Denmark Tackled Resistance. Spheres of Influence, 122(6). Retrieved from http://ehp.niehs.nih.gov/122-a160/

Natural Resources Conservation Service. (n.d.). Retrieved from http://www.nrcs.usda.gov/wps/portal/nrcs/main/national/plantsanimals/livestock/afo/

Nowakowski, K., (2015, February 3). Should we continue to feed antibiotics to livestock? National Geographic. Retrieved from http://news.nationalgeographic.com/2015/02/150213-antibiotic-resistance-animals-ngfood/

Parsons, T. (2007, January 5). Adding Antibiotics to Chicken Feed Not Cost-Effective. Retrieved from http://www.jhsph.edu/news/news-releases/2007/graham-antibiotics.html

PBS. (2014). Modern Meat: Antibiotic Debate Overview. Retrieved from http://www.pbs.org/wgbh/pages/frontline/shows/meat/safe/overview.html

Terry, L. (2015, May 1). Scarred For Life. Retrieved from http://www.oregonlive.com/usda-salmonella/chapter-2.html

Voetsch AC, van Gilder TJ, Angulo FJ, Farley MM, Shallow S, Marcus R, et al. (2004). FoodNet estimate of the burden of illness caused by nontyphoidal Salmonella infections in the United States. Clinical Infectious Diseases. 38 (3). doi: S127–34 10.1086/381578

White, D. G., Zhao, S., Sudler, R., Ayers, S., Friedman, S., Chen, S., . . . Meng, J. (2001). The isolation of antibiotic-resistant salmonella from retail ground meats. New England Journal of Medicine, 345(16), 1147-1154. doi:10.1056/NEJMoa010315

Whether or not wind turbines are a significant threat to bird populations

 

 

Billy DeVore, Forestry

Jamie Remillard, Animal Science

Chloe Doe, Animal Science

Kyle Gibbons, Plant Soil and Insect Sciences

         An article title in bold-faced letters reads “EMERGING SOLAR PLANTS SCORCH BIRDS IN MID-AIR”.  Appearing on Associated Press , this article , authored by Ellen Knickmeyer and John Locher (2014) , is exemplary of the media’s use of biased sensationalism to slight alternative energy and its effects on bird populations.  Whenever possible , popular media tends to highlight examples of charismatic megafauna , or larger organisms with high popular appeal , brutally killed off in cruel and , unusual manners . Whether it be wind turbines decapitating raptors, displaced and dehydrated desert tortoises, or spontaneously combusting “Streamer” birds , these stories serve to aggrandize the farcical evils of alternative energy sources (Knickmeyer and Locher , 2014). What is left out of a large portion of popular media and discourse are the comparative death rates of birds among energy sources . These aforementioned stories , with their inclusion of palpable violence done unto the most emotionally-appealing creatures , mask the long-standing direct and indirect ways in which the fossil fuel industry kills over 14 million birds annually . Infrequently do reports surface documenting the extraction of coal being solely responsible for the death of 7.9 million bird deaths per year (Sovacool , 2013) Rarely discussed are the immediate and downstream effects on avian creatures resulting from the fossil fuel industry ; such as the depletion of viable bird habitat in the form of hundreds of thousands of acres of deciduous forest clear cut annually for coal mining . The combustion of fossil fuels, like coal and oil , is responsible for incredible rates of non-point source pollution which cause detrimental effects on birds that transcend generations; such as the nation wide phenomenon of acid rain , or the bioaccumulation of mercury in birds that lowers their brood sizes and made serious effects on the health of their young(Sovacool 2013). Our paper intends to make a case in defense of wind energy , with regard to its association with having severe negative effects on bird populations . By comparing the number of annual bird deaths attributable to a combination of several energy resources,  this essay intends to provide evidence for wind power’s relatively small involvement in bird mortality within the United States ; while simultaneously highlighting how structural modifications to and an increased dependence on wind turbines can reduce said mortality in addition to the average national annual death toll .   

        Commonly used in the narrative espoused by anti-wind turbine organizations, is the rate at which wind turbines kill birds on an annual basis .  Generous estimates  made by wildlife and ornithological enthusiasts , contend that this number ranges well beyond half a million birds per year , reaching up to nearly 700,000 (Smallwood 2013) .  The consensus among most scientists is that this number is actually somewhere between 300,000- 400,000 birds per year (Loss et al ., 2013 ; Sovacool, 2013;Wang & Wang , 2015) . Despite this contention , bird fatalities caused by wind turbines still do not even come close to that of coal , which reach nearly 8 million annually (Sovacool , 2013)

        The Gigawatt hour ,or GWh , is the standard unit of energy used to discuss electricity production at a national scale-level . One GWh is the equivalent to 1,000,000 Kilowatt hours . By looking at this same issue in terms of the number of birds killed per Gigawatt hour generated by the various energy sources(coal and wind) , the comparative ratios serve to portray coal extraction and its’ resulting energy production as the truly destructive industry that it is .

        In his 2013 Report , The avian benefits of wind energy , Benjamin K. Sovacool assesses the number of bird fatalities associated with various energy sources based on meta-analysis and a collection of results from experiments from across the country . His findings indicate that on average , wind turbines killed .3 to .4 birds per GWh of electricity they produced , while coal killed approximately 5.2 bird per GWh (Sovacool 2013) . Standing alone , these numbers are indicative of the marked increase in harm done unto bird populations posed by coal . What is more telling , is that by using these determined multipliers (.35 for wind energy and 5.2 for coal) , in addition to a hypothetical inflation of wind energy’s contribution toward the national electricity production , it is evident that even despite this inflation , coal would still kill more birds annually .  According to the U.S. Energy Information Administration , Coal accounts for approximately 33% of our nation’s electricity production (2015). As a nation the United States produces a total of 4 million GWh per year , meaning that coal accounts for 1,333,333.33 of those gigawatt-hours . In contrast , wind energy contributes much less  , at 4.7 % , or 188,000 GWh annually (US EIA , 2015) . Disregarding the latent effects of coal extraction that also account for bird fatality such as acid rain , bioaccumulation of mercury and habitat loss ,  this would conservatively determine that coal causes  6,933,333.22 , or approximately 7 million bird fatalities annually . In comparison , multiplying the 188,000 GWh produced by wind turbines , by Sovacool’s averaged experimental ratio of .35 birds per GWh , equals to 65,800 bird fatalities per year . Note that these are both conservative , and hypothetical calculations . In reality , the number of bird fatalities attributable to wind energy is approximately 350,000 (Loss et al ., 2013 ; Sovacool, 2013;Wang & Wang , 2015) . Hypothetically , if our nation saw a significant increase such as a 50% dependency on wind energy , the total number of birds killed on an annual basis would still be less than that of coal . The national generation electricity is currently 4 million GWh . If wind turbines were to account for 2 million GWh produced annually , multiplied by Sovacool’s factor of .35 , this equates to 700,000 bird fatalities annually . For argument sake , even despite adding the current number of bird fatalities attributable to wind energy to this hypothetical calculation , approximately 350,000 , it still remains less than those attributable to coal , at 1,050,000 bird fatalities per year  (Loss et al ., 2013 ; Sovacool, 2013;Wang & Wang , 2015) .

        Wind farms across the U.S. show a  rather insignificant impact on bird populations, but researchers tested and implemented proven methods of altering wind turbines to make them even less hazardous to birds populations. It can be difficult to see the impact wind turbines pose on endangered bird species due to the fact they do not kill any bird species in particular, but by reducing the overall mortality rate of bird species caused by wind turbines through altering the turbines, other benefits, such as the endangered bird species mortality rate, will decrease accordingly.

        The numbers of avian mortality due to wind turbines are much lower compared to other avian mortality contributors such as feral cats and power lines that serve more than triple the risk (Wang & Wang , 2015), although some people may worry about the turbines critically affecting endangered bird species whose populations are already at risk and low in quantity. Only 214,000- 368,000 birds are killed by turbines each year in the U.S. (Erickson et al.), compared to the 10-20 billion that currently reside in the US, leaving approximating  99.64% of the bird population unaffected by wind turbines. Wind turbines are a modern source of sustainable energy- efficient electricity, that pose very little threat to the environment in general. Therefore, we should continue to move forward with implementing wind turbines, and instead work to cut down avian mortality by implementing new turbine standards that would substantially reduce death. Wind turbine facilities can increase the diameter of the blades,which birds can see clearly and  avoid. Khan (2014) notes that birds, like wind turbines, are more often favorably positioned near high winds to allow for less energy expensive flying and migration, which poses a threat since birds are drawn to these wind turbine locations.Wind turbine facilities could raise the height of the wind turbine itself, where birds may not commonly fly at and away from foraging nests (Khan, 2014).

        Wind turbine areas could prove to help collect data for bird species residing in that current area, which could help them determine whether this is an area heavily populated by  birds,  including endangered species. In this case, wind turbines should move elsewhere if a high number of birds occupy in that given location. We can reduce the amount of avian mortality by reducing cut-in speeds, the  minimum speed at which the rotor blades turning will produce a certain amount of usable power, by 66% percent, which only lowers the efficiency of the wind turbines by a 3% loss in production (Horn et al. 2008.) The loss in production compared to the speed reduced is highly insignificant, and worth it if it means dramatically reducing avian mortality to an even smaller amount.

        Wind turbines are usually painted in a neutral white, a non-obtrusive color, making them more inconspicuous than noticeably obvious bright colors. Although  these wind turbines may blend in so well against the sky, many birds who lack well defined eyesight, do not see them and collide with the blades upon direct impact. Birds have a fourth set of cone cells,  a type of receptor for color,  that is particularly sensitive to ultraviolet light. Many of their prey’s bodies naturally reflect UV light making them more detectable, and is highly innate skill for birds to pick up on UV light.  Therefore, the suggestion is that we paint wind turbines in bright colors, and add a large ultraviolet lights facing upwind. The effect of these altercations to wind turbines serve to be similarly based upon applying Pavlov’s theory.  A dog salivates upon solely hearing a bell alone after numerous occasions when it was time to eat a bell rang at the same time as well, and the same theory can be applied to birds. A loud sound can be applied to the wind turbine, which will emit a noise for birds to stay away when they get too close, similar to a motion detector. The birds may become extremely startled the first time the sound goes off, but the bird, along with its fellow peers, will learn to avoid these areas with wind turbines over time after repetition, like the dinner bell. Hence, it is possible that with time, the number of birds fatalities at a given wind turbine location will decrease due to the repetitive teaching of where the wind turbines are exactly located, solely due to a sound being emitted.

 

       As our environment becomes increasingly polluted by huge fossil fuel burning power emissions, there is a greater need for greener solutions for energy production. Coal is one of the largest polluters and causes the deaths of over 7,900,000 birds every year through polluted air, habitats and food sources. As an extreme polluter, releasing over 200 pounds of CO2 into the atmosphere per kiloWatt hour of energy, it is also one of the more expensive energy alternatives costing $297-$332 per MegaWatt Hour. This is over ten times the cost of wind turbines which cost $31-$81 per MegaWatt Hour. Along with being a cheaper energy source than most alternatives including coal wind turbines show zero carbon emissions and no negative pollutants associated with the collection of energy. Wind Energy also provides a safer alternative than nuclear power in that it does not involve the use of radioactive isotopes. Which also allows for the land to repurposed for other uses if they are no longer needed.

 

       Large predatory birds like eagles and hawks,  have been studied in regard to their susceptibility to being killed by wind turbines. A study was conducted by Johnston, Bradley, and Otter (2014) that directly looked at how frequently Golden Eagles were able to adjust their flight altitudes in order to miss collision with wind turbines. This study specifically looked at how frequently golden eagles flew through areas containing wind turbines, which the authors refer to as the “risk zone” (Johnston et al., 2014, p. 5). By combining and comparing their observations of the numbers in past to more recent years, the authors were able to determine that there are a growing number of golden eagles in the population in which the study took place. The data specifically showed a gradual increase of golden eagles over the years with 327 eagles in 2009 , 380 in 2010 , and 427 in 2011. (Johnston et al., 2014,p.5). This data directly supports the idea that wind turbines are not decimating large predatory birds at a faster rate than they are able to reproduce.

        The study by Johnston et al. (2014) also shows important information that the golden eagles were able to detect the presence of wind turbines and successfully avoid them. The authors assess the frequencies at which golden eagles would pass through areas containing wind turbines, and determined that before after construction of wind turbines, less than 1% of recorded golden eagles flights flew in the areas of the study low enough to potentially collide with a wind turbine. (Johnston et al., 2014,p.5).

        Another similar study was conducted in the U.S. specific to golden eagles and wind turbine collision frequencies. “Landscapes for energy and wildlife”, by Tack and Fedy assess the distances of golden eagle nesting areas and their proximity to wind turbines, where they tried to determine a correlation between them. The observations of the authors showed no correlation between nesting distance to collision with wind turbines (Tach & Fedy, 2015, p.6). This supports the idea that golden eagles are able to detect wind turbines and make decisions regarding how to avoid them. This is evidence that larger birds of prey and capable of avoiding wind turbines intentionally and will also be able to teach their offspring how to avoid collision.

        In regard to larger waterfowl and wind turbines, such as swans, a case study in Denmark was conducted by Jesper Kyed Larsen and Preben Clausen in 2001. The authors observed swans taking off and landing near coastal areas with about 50 wind turbines present at all 4 locations. The authors after the study were able to conclude that the swans were capable of completely avoiding the wind turbines during the day, at sunrise and sunset (Larsen & Clausen 2001, p.397). They agree that wind turbines were not hard for the birds to avoid in lighter conditions, “It seems likely that Whooper Swans will be fully capable of avoiding wind turbines during daylight and good visibility”, Larsen and Clausen (2001, p. 398).

        Larsen and Clausen (2001) agreed that this swan population’s risk of collision with wind turbines was highest during the morning and evening flights. This points to a very small time frame for collision risks, when light conditions are not optimal, but not dark enough for the birds to completely miss. This small time frame of collision, plus adequate light conditions is evidence that only a small number of swans will collide with wind turbines (Larsen & Clausen, 2001, p. 329).

       The authors also provide strong evidence that using taller wind turbines can further reduce the risk of collision. They support this argument by showing from their observations, that the average flight height of swans is about 11-20 meters high. They measured the wind turbines in the study zone and found that the tallest wind turbines lowest blade rotation point was 40 meters above the ground (Larsen & Clausen 2001, p. 329, Figure 2.). This is double the average flight height showing that swans are not likely to fly at heights high enough to collide with wind turbines. This evidence supports the points that wind turbines only pose a threat to swans for a very small time frame, and are generally tall enough that swans wouldn’t normally collide with them anyway.

       Larsen and Clausen in their research did not consider or test the benefits of using lights on wind turbines. The addition of lights to wind turbines would provide the birds extra visibility of wind turbines if light conditions for flying were not optimal. Since the collision rate is already very low for larger swan species, the addition of lights would help reduce wind turbine induced swan deaths further.

 

        There are much more harmful things to the bird population than the small number of deaths caused by collision with wind turbines. Overall, through installing more wind turbines in the U.S., green energy will  greatly reduce fossil fuel use and benefit the environment by declining the negative effects fossil fuels pose to both the environment collectively as a whole and the animals within it. By implementing more wind turbines that are altered for birds, green energy will lower  our dependency on fossil fuel use, and reduce the fatalities caused by fossil fuel pollution.

        Studies show various methods that can easily be applied for reducing wind turbine induced avian mortality further. Some of these techniques include  reducing the speed of the blades, addition of colors and sound, and improving the overall structural heights and widths of each component of the wind turbine. Adding lights is a simple measure that if used correctly can deter birds away from wind turbines. Birds are extremely receptive to UV light in particular. Small UV lights can be attached to wind turbines that would notify birds of the turbines location so that they could be avoided.

        Wind turbines actually pose as a safer energy alternative for birds than conventional methods such as coal. Coal ash fly is the remaining waste product after coal is  burned for energy. The deposition sites of coal ash fly prove to make highly toxic areas that (unlike wind turbines), affect all birds in that habitat (Chernick et al.,2016). The coal fly ash areas will leach excessive amounts of selenium into the soil and can induce many developmental growth deformities that lead to fatalities in all surrounding bird populations Chernick et al.,2016 page 188).

         Wind turbines only show to have an affect on a very small number of birds in the areas they are implemented, whereas the coal fly ash deposition sites are shown to have toxic effects on almost every neighboring inhabitat (Chernick et al., 2016 page 189). Wind turbines also only cause mortality to individual animals while selenium toxicity can cause issues to bird over generations. The selenium can genetically alter birds, cause them to have underdeveloped bodies,  organs, and fatal conditions that can be genetically passed down to offspring (Chernick et al., 2016 page 190).Wind turbines do not pose any genetic mutations to bird populations and effect less birds, making them the safer option than using non-renewable resources like coal.

 

       In reducing the number of birds that die from wind turbines, our group decided that all current and future wind turbines need modification with the mentioned alterations. These modifications are mandatory for all wind turbine industries and enforced by the EPA. Implementing laws regarding the alterations for all wind turbines would need to pass for every state in the U.S. and would also require every wind turbine company to go through them to continue building or collecting wind. Through making all wind turbine companies go through the EPA, this would also help to regulate the current wind turbine industry and help researchers to collect better data samples. Through better data sampling, we can continue to improve wind turbines and further lower the amount of bird related deaths substantially more, and the country can continue to progressively move towards an efficient source of green sustainable energy.

 

       

this image shows the large differences in causes of bird death.

this image shows the large differences in causes of bird death.

Our group decided that the benefits of green energy collected from wind turbines outweighs the slight loss in bird populations in the U.S. We have come to this  conclusion for a couple of reasons first being the current wind turbines are altered in order further reduce bird mortality rates, by changing the color of the turbines along with added lights that are visible to the birds and loud noises associated with the wind turbines to all act together as a warning system to reduce bird fatalities. next , the implementation of these wind turbines have the ability to reduce the use of fossil fuel burning power plants therefore decreasing the pollution which is actually responsible for far greater displacement and death of birds . By lowering pollution levels in the environment, the overall health of the wildlife including birds will increase and the mortality rates caused by polluted habitats, air and food sources will decrease at a more substantial rate than the death rates caused by the wind turbines.

 

Literature Cited

Chernick, M., Ware, M., Albright, E., Kwok, K. W. H., Dong, W., Zheng, N., & Hinton, D. E. (2016). Parental dietary seleno-L-methionine exposure and resultant offspring developmental toxicity. Aquatic Toxicology, 170, 187-198. doi:10.1016/j.aquatox.2015.11.004

 

Erickson, W. P., Wolfe, M. M., Bay, K. J., Johnson, D. H., & Gehring, J. L. (2014). A comprehensive analysis of small-passerine fatalities from collision with turbines at wind energy facilities. Plos One, 9(9), e107491. doi:10.1371/journal.pone.0107491

 

Johnston, N.N.,  Bradley, J., & Otter,K.A. (2014). Increased flight altitudes among

migrating golden eagles suggest turbine avoidance at a rocky mountain wind installation. Plos one , 9(3) doi : 10.1371/journal.pone.0093030

 

Khan, S. (2014). Warning sounds and color for reducing bird and bat mortality at wind turbines. 9th International Forum on Strategic Technology, IFOST 2014, October 21, 2014 – October 23, 322-325. doi:10.1109/IFOST.2014.6991131

 

Knickmeyer, E., & Locher , J.(2014, August 18) Emerging solar plants scorch birds in mid-air. Associated Press. Retrieved from http://bigstory.ap.org/article/emerging-solar-plants-scorch-birds-mid-air

 

Larsen, J. K., & Clausen, P.. (2002). Potential Wind Park Impacts on Whooper Swans in Winter: The Risk of Collision. Waterbirds: The International Journal of Waterbird Biology 25(1), 327–330.

 

Loss, S. R., Will, T., & Marra, P. P. (2015). Direct mortality of birds from anthropogenic causes. Annu. Rev. Ecol. Evol. Syst. Annual Review of Ecology, Evolution, and Systematics, 46(1), 99-120. Retrieved February 28, 2016.

 

Sovacool,Benjamin K.(2013) The avian benefits of wind energy: A 2009 update

Renewable Energy, 2013, 49, 19-24

 

Tack, J. D., & Fedy, B. C. (2015). Landscapes for energy and wildlife: Conservation prioritization for golden eagles across large spatial scales. Plos One, 10(8), e0134781. doi:10.1371/journal.pone.0134781

 

United States Energy Information Administration . (2015). What is U.S. electricity production by energy source . Retrieved from https://www.eia.gov/tools/faqs/faq.cfm?id=427&t=3

 

Environmental Impact of GMOs

Jessica Neves, Animal Science

Adam D’Agostino, Natural Resources and Conservation

Alicia Zolondick, Plant, Soil, and Insect Sciences

Introduction to Genetically Modified Organisms

gmo

When examining population ecology, a common story comes to mind.  Imagine a habitat   with endless resources, and no predation or competition. It sounds like this would be ideal for sustaining population. What could possibly go wrong? This type of environment is the perfect breeding ground for the overpopulation of any species. If a population has enough food to sustain and thrive, exponential breeding will occur. For several generations this growth will not be a significant problem. However, soon there won’t be enough food to sustain the entire population. Food becomes scarce, and individuals begin to compete for limited resources. Only the most fit of the individuals will survive, while the weak will die off due to disease and starvation. The population will plummet drastically, leaving only several individuals left. This cycle is related to the carrying capacity of a species, which is the size of the population that can be sustained indefinitely. By exceeding this limit, the clock starts to tick until disaster strikes.

Just as in the scenario above, the human population will continue to grow when resources allow. Genetically modifying crops became the solution to prolong human existence beyond our carrying capacity. Once the carrying capacity is reached, humans will outnumber the resources available and drastic changes in population will occur.  To prevent a collapse in population, humans are doing their best to provide enough food for all to survive by developing genetic modified crops. It is established that genetically modified (GM) crops impact the environment, but are we willing to overlook that in order to save our own? GM crops are necessary to sustain life and increase the carrying capacity of the human population, so we can not foresee eliminating them. Therefore, our plan is to reduce the impact of GM products on the environment, rather than abolish genetic engineering completely.

The World Health Organization defines genetically modified organisms (GMOs) as “organisms (i.e. plants, animals or microorganisms) in which the genetic material (DNA) has been altered in a way that does not occur naturally by mating and/or natural recombination” (World Health Organization [WHO], 2016).  GM crops are becoming more and more prevalent in our everyday lives. In the past 30 years, new GM products are available on shelves in supermarkets worldwide.  The following paper will discuss the environmental impacts of GM crops and explain how our global society utilizes them in the food system.

Background on the Environmental Impacts of GMOs

Negative impacts on the environment from GMOs are a big concern for scientists and the public. Negative effects on the environment include increased use of herbicides and pollution of aquatic ecosystems.  These fundamental issues will comprise the focus of this paper.  Given the negative impacts and the need for GMOs for food production, the only way to cope with this dichotomy is to decrease the environmental impact without eliminating modified crops. Preventing these impacts is improbable, but reduction of long term damage to affected ecosystems is plausible and should be attended to by conservationists and genetic engineers collaboratively.  There is no one solution to the problem, but there are several practical strategies to limit environmental damage due to GMOs.

Glyphosate Impact

Managing weeds is one of the most tedious tasks of farming.  Recognizing the struggles that farmers face with weed management, scientists developed genetically modified herbicide-tolerant (HT) crops so farmers can spray their fields with weed killers without affecting their crop yield.  In the past 30 years, developing herbicide tolerant crops (such as corn, soybean, and cotton) has been the most notable advancement in crop engineering history (Bonny 2016).  Most of the HT crops are tolerant to glyphosate, a compound used in Roundup to kill many species of weeds that compete with crops.

Glyphosate-tolerant (GT) crops were first developed by Monsanto in 1994.  Since GT crops were brought to market, glyphosate-based herbicides (like Roundup) dominated the market and GT soybean, corn, and cotton are the majority of cultivated varieties in global agriculture (Bonny 2016).  In 2012, it was calculated that glyphosate made up “about 30% of the global herbicide market, far ahead of other herbicides. (…) For example, for soybean, the glyphosate proportion of total herbicides used grew from 4 % in the 1990-1993 to 89 % in 2006” (Bonny, 2016, p.35).  Furthermore, Bonny (2016) states “in 2014, GT soybeans represented 50 % of all HT crops and about 80 % of all globally cultivated soybeans” (Bonny, 2016, p.35).

Monsanto was the world’s top provider of both the GT Roundup Ready crops and the Roundup herbicide treatment.  In the 1990s and again in 2003, Monsanto produced literature ensuring that weeds developing GR was extremely unlikely and urged farmers to increase their use of GT crops and Roundup paired together (Bonny 2016).  Meanwhile in 1996, Australian scientists who discovered the first GR weed species contended “it would be prudent to accept that resistance can occur to this highly valuable herbicide and to encourage glyphosate use patterns within integrated strategies that do not impose a strong selection pressure for resistance” (Powles et al. 1998, p.6).

GT crops were developed because they were thought to not only eliminate the burden of weed management for farmers, but also reduce the overall amount of herbicides sprayed.  GT crops served the farmers well and reduced the amount of time and money spent on hand weeding.  However, since the widespread adoption of glyphosate herbicides sprayed on GT crops, the weeds targeted by glyphosate-based herbicides started to develop a resistance to these herbicides (Bonny 2016).  The more glyphosate resistance (GR) develops in weed populations, the less effective glyphosate-based herbicides become (Bonny 2016).  When herbicides are continually sprayed, there is a high selective pressure on the weed populations.  Resistant populations arise from random mutations within individuals that happen to survive the herbicide treatments.  When glyphosate is used at a higher frequency than other herbicides, the chance of mutant weed survival to glyphosate is more frequent (Bonny 2016).  In other words, the more you spray glyphosate, the more likely it is that the weeds will evolve to survive glyphosate treatment.  

Due to the frequency of GT crops, glyphosate herbicides became the sole dominator of the market.  As a result, there was an initial decrease in the frequency of general herbicide use.    Glyphosate was at first considered a low-risk herbicide for both human consumption and environmental impact, so this decrease was very well received by the public and scientific communities (Bonny 2016).  However, this decrease was closely followed by a plateau and then a steady increase in glyphosate applications.  It is believed that there is a direct correlation between the decrease in availability of alternate herbicides and an increase in GR weeds. Nearly half of the GR weeds found globally are flourishing on US soil, and burdening farmers with weeds that continued to compete with their crops even when drenching their fields with Roundup.

The graph below was produced by Bonny (2016) based on statistics found from USDA-NASS (1991-2013) and from Heap (2015).  This image displays several different herbicides applied to soybeans in the USA in relation to the development and growth of glyphosate-resistant weeds from 1990-2012.  The right axis is displaying the number of GR weeds, the left axis is displaying the number of herbicides, and the bottom axis is displaying time.  Bonny (2016) states that there was only one survey reporting herbicide usage from 2006-2012.  The increased use of herbicides from 2006-2012 based on the numbers from the survey is expressed with the dotted line in the image.

The development of GM Roundup Ready (RR) crops triggered a steady increase in the use of glyphosate (Szekacs & Darvas, 2012). The increased amount of spraying due to GR weeds leads to a higher amount of glyphosate found in our groundwater, surface water, soils, and precipitation (Coupe et al. 2012; Battaglin et al. 2014). The glyphosate can pollute through runoff, pesticide-drift, and leaching through the ground. Research of Mexican water sources by Ruiz-Toledo, Castro, Rivero-Perez, Bello Mendoza and Sanchez (2014), found traces of glyphosate in all tested sources. Sampling sites included irrigation channels, wells, and points along a river bank, providing diversity of water sources (Ruiz-Toledo et al., 2014). The tests found traces of glyphosate in all samples, including tests within natural protected areas (Ruiz-Toledo et al., 2014).  The test results prove that glyphosate found its way into water sources through surface runoff, leaching, pesticide-drift, or potentially other modes of transport.

Glyphosate is a water-soluble compound, meaning that glyphosate dissolves in water creating a solution (Szekacs & Darvas, 2012). Glyphosate supposedly decomposes quickly in water, with a relatively short half-life, however it also binds with soils resulting in much longer half-life (Szekacs & Darvas, 2012). Water quality problems arise when glyphosate absorbs into the soil because the chemical leaches or is carried away by runoff.

The concentration of glyphosate in the water source is significantly influenced by the amount of precipitation within the given season, either rainy or dry (Ruiz-Toledo et al., 2014). During a rainy season, the concentration of glyphosate within a water source is diluted, but during a dry season concentrations rise dramatically creating unsafe water quality (Ruiz-Toledo et al., 2014). Amounts of precipitation also determine how far polluted runoff can reach geographically speaking.  These changes in precipitation levels cause glyphosate to travel far away from the intended application site. Daouk, De Alencastro, Pfeifer, Grandjean, and Chevre (2013) attribute rainfall to the transport of glyphosate when soils are composed of fine-textured layers on a significant slope. However, Daouk et al. (2013) believe that surface runoff is responsible for the majority of glyphosate transport. With this in mind, Ruiz-Toledo et al. (2014) propose tighter restrictions on proximity of glyphosate application sites to water sources, such as rivers.  Since GM crops are frequently paired with excessive glyphosate use, it is crucial that actions are taken to use glyphosate safely in large scale agriculture systems.

Glyphosate applications in close proximity to rivers is problematic to wildlife populations.  A high amount of glyphosate is lethal to amphibians and other organisms. Relyea (2005) suggests that Roundup, a compound designed to kill plants, can cause extremely high rates of mortality to amphibians that could lead to population declines in the natural environment as well as death in laboratory conditions. Relyea (2005) provides the example that after three weeks of exposure, Roundup killed 96–100% of larval amphibians (regardless of soil presence) in their natural environment. Another specific example of the lethal effects of glyphosate provided by Relyea (2005) is that when juvenile anurans (a type of amphibian) were exposed to a direct overspray of Roundup in laboratory containers, Roundup killed 68–86% of the juveniles.

Other organisms besides amphibians are also affected. Tsui and Chu (2003) provide the example thatmicroalgae and crustaceans were 4–5 folds more sensitive to Roundup toxicity than bacteria and protozoa” (p.1189). The toxicity was mainly due to the extreme decrease in pH of the water surrounding the microalgae and crustaceans after glyphosate acid was added during testing (Tsui & Chu, 2003).

Based on the negative impacts that GMOs inflict on the environment presented in this paper, one might formulate the opinion that GMOs should be discontinued or outlawed.  However, as predicted by human population growth specialists, the global human population is predicted to reach 9 billion by 2050.  The question at the forefront of the century is: how are we, as a collective humanity, going to feed the population?  According to “PLOS Biology”, “because most of the Earth’s arable land is already in production and what remains is being lost to urbanization, salinization, desertification, and environmental degradation, cropland expansion is not a viable approach to food security” (Ronald, 2014, p.1).  Therefore, engineering GM crops to grow in poor quality soils, fight virulent pathogens, and carry protection against pest damage are necessary to sustain the food demands of the rising populous. Over the past 50 years, population grew substantially and the demand for efficient food production increased.  GM crop development accelerated immensely in the past 30 years to try and sustain the global demands for food.  According to the Department of Plant Pathology and the Genome Center, “in Bangladesh and India, four million tons of rice, enough to feed 30 million people, is lost each year to flooding,” and their team engineered a species of rice with a flood resistant gene (Ronald, 2014, p.2). This flood resistant gene enables more plants to survive floods, and more people are subsequently able to eat the plants.   In our current food system in the Unites States, 80% of food contains derivatives from genetically engineered crops. (Ronald, 2014).  The food market is already reliant on GM crop production to feed the people alive right now, and the demand for GM crop production will only increase as the population grows in the future.  Certain staple crops like cultivated papayas and bananas would be extinct due to noxious diseases if GM resistant varieties were not developed (Ronald, 2014). Due to the prevalence of GMOs, steps should be taken by growers and plant scientists to ensure that the conservation of the ecosystem and the reduction of negative environmental impact is a top priority.  These strategies aiming to balance conservation and technology are a realistic solution instead of abolishing genetic engineering entirely.

Proposal

We propose implementing a plan to change the management practices of using herbicides. Although this plan would not completely reverse the negative impact that GM crops have on the environment, it will be a first step in slowing the total rate of detrimental effects in time. We propose the approval of varieties of GM crops with “stacked herbicide tolerance” (Bonny, 2016, p.40) by the USDA in order to combat the GR weeds.  Stacked herbicide tolerance refers to a crop that is engineered to have resistance to multiple herbicides simultaneously.  The development of GM crops with stacked herbicide resistance could benefit large scale agriculture because it would allow farmers to spray their fields with multiple different herbicides instead of just glyphosate-based treatments, creating an herbicide management plan.  Allowing for variation in herbicide applications would minimize mutant weed resistant populations from developing (Bonny 2016). In addition to encouraging more stacked GM crops, weed scientists should also encourage growers to integrate a wider variety of weed management methods “such as crop rotation, cover crops and mulches, reduced tillage, precision agriculture, adequate seeding rates, seed quality, etc” (Bonny, 2016, p.44).  Tsui and Chu (2003) also suggest other alternatives to the original Roundup to use as herbicides. According to Tsui and Chu (2003) “Roundup Biactive was about 14 times less toxic than Roundup” (p. 1196). Using Roundup Bioactive instead of the original Roundup will also hopefully reduce the lethality that this herbicide has on other organisms. Widening the scope of weed management will foster “scientific knowledge in a manner that considers the causes of weed problems rather than reacts to existing weed populations” (Buhler, 2002, p.279).   GM crops are necessary to feed the population and will continue to exist, but they can be dangerous to the environment if they are not properly controlled. Changing the management practices of using herbicides will reduce the detrimental effects that many GM crops have on the environment, while simultaneously allowing humans to enjoy their benefits.  

References

Battaglin, W.A., Meyer, M.T., Kuivila, K.M., Dietze, J.E. (2014). Glyphosate and its degradation product AMPA occur frequently and widely in US soils, surface water, groundwater, and precipitation. Journal of the American Water Resources Association, 50(2):275–290. doi:10.1111/jawr.12159.

Bonny, S. (2016). Genetically modified herbicide-tolerant crops, weeds, and herbicides: Overview and impact.  Journal of Environmental Management, 57, 31-48. doi: http://dx.doi.org/10.1007/s00267-015-0589-7.

Buhler, D. D. (2002). 50th Anniversary, Invited Article: challenges and opportunities for integrated weed management. Weed Science Society of America, 50(3):273–280. doi: http://dx.doi.org/10.1614/0043-1745(2002)050[0273:AIAAOF]2.0.CO;2

Coupe, R.H., Barlow, J.R., Capel, P.D. (2012) Complexity of human and ecosystem interactions in an agricultural landscape. Environmental Development (4):88–104. doi: http://dx.doi.org/10.1016/j.envdev.2012.09

Daouk, S., De Alencastro, L. F., Pfeifer, H., Grandjean, D., & Chevre, N. (2013). The herbicide glyphosate and its metabolite AMPA in the lavaux vineyard area, western switzerland: Proof of widespread export to surface waters. part I: Method validation in different water matrices. Journal of Environmental Science and Health, Part B Pesticides, Food Contaminants and Agricultural Wastes, 48(9), 717-724.

GMO Corn. Digital Image. GMO Corn Crops Under Attack By Leafworms. 2014. 20 Apr 2014.

Heap I (2015) The International Survey of Herbicide Resistant Weeds. http://www.weedscience.org. Accessed 22 July 2015

Powles, S.B., Lorraine-Colwill, D.F., Dellow, J.J., Preston, C. (1998). Evolved resistance to glyphosate in rigid ryegrass (Lolium rigidum) in Australia. Weed Science Society of America 46(5):604–607. doi: http://www. jstor.org/stable/4045968.

Relyea, R. A. (2005). The lethal impact of roundup on aquatic and terrestrial amphibians. Ecological Applications, 15(4), 1118-1124. doi: 10.1890/04-1291

Ronald, P. C. (2014). Lab to farm: Applying research on plant genetics and genomics to crop improvement. Public Library of Science: Biology, 12(6). doi: http://dx.doi.org/10.1371/journal.pbio.1001878.

Ruiz-Toledo, J., Bello-Mendoza, R., Sánchez, D., Castro, R., & Rivero-Pérez, N. (2014). Occurrence of glyphosate in water bodies derived from intensive agriculture in a tropical region of southern mexico. Bulletin of Environmental Contamination and Toxicology, 93(3), 289-293.

Székács, A., & Darvas, B. (2012). Forty years with glyphosate. Herbicides-properties, synthesis and control of weeds. Hasaneen, MN: InTech.

Tsui, M. T. K., & Chu, L. M. (2003). Aquatic toxicity of glyphosate-based formulations: Comparison between different organisms and the effects of environmental factors. Chemosphere Journal, 52(1), 1189-1197. doi: 10.1016/S0045-6535(03)00306-0

USDA-NASS (1991–2013) Agricultural chemical usage, field crops summary. USDA ESMIS (Economics, Statistics and Market Information System), Mann Library, Cornell University, 1990–2013. http://usda.mannlib.cornell.edu/MannUsda/viewDo cumentInfo.do?documentID=1560. Accessed 1 July 2015

World Health Organization. (2016). Frequently asked questions on genetically modified foods.  Retrieved from: http://www.who.int/foodsafety/areas_work/food-technology/faq-

genetically-modified- food/en/

 

Understanding the Buzz on Honey Bee Population Decline

Arianna Wills [NRC Wildlife] Emily Mann [Pre-Veterinary Science] Valovia Costa [Environmental Science]

Understanding the Buzz on Honey Bee Population Decline

      In the 1940s the pesticide DDT was developed and used with great success to combat deadly insect borne diseases like malaria and typhus. DDT was sprayed on everything, including: crops, livestock farms, lakes, parks, homes, and gardens (Environmental Protection Agency, 2015). It was relatively cheap, extremely effective, and began to be used around the globe. However, in the 1960s, evidence showed that DDT was having unforeseen environmental consequences (EPA, 2015). DDT proved toxic to nontarget species, like birds and fish because this chemical does not break down naturally in the environment and accumulates in the fatty tissues of wildlife (EPA, 2015). DDT began to significantly impact bald eagles because they ate contaminated fish and this chemical began building up in the birds (U.S. Fish & Wildlife, 2007). DDT interfered with the eagles ability to produce proper eggshells, so the eggs were crushed during incubation or otherwise simply never hatched (U.S. Fish & Wildlife, 2007). The bald eagle population crashed (U.S. Fish & Wildlife, 2007). Once the Environmental Protection Agency banned the use of DDT in the U.S., bald eagle populations slowly began to bounce back (U.S. Fish & Wildlife, 2007). Impressively, the ban lead to the removal of the bald eagles from the endangered species list (U.S. Fish & Wildlife, 2007). The environmental repercussions of DDT were realized and caught in time to save bald eagles from extinction.

      Now, a similar threat is faced by an even more important species: the honey bee. In the spring of 2007, commercial beekeepers, who loan their bees out to help farmers pollinate their crops, began to see more and more cases of what became known as colony collapse disorder (CCD) (Turner, 2014). Continue Reading

Free-Range Eggs: Are They Actually a Healthier Option?

Rebecca DeMederios (Animal Science), Kyle Lunetta (Building and Construction Technology), Holly Sullivan (Animal Science), Alan-Michael Turner (Turfgrass Science and Management)

“A warning about Salmonella in eggs was issued today after two outbreaks of food poisoning, which have already claimed one life” (Daily Mail News, 2015). This past fall in the southeast and northwest of England, a Salmonella outbreak swept through, resulting in over 150 reported cases, and one death. Salmonella has become synonymous with eggs, and for good reason. “The Centers for Disease Control and Prevention estimates that over 1 million people in the U.S. contract Salmonella each year, and that an average of 20,000 hospitalizations and almost 400 deaths occur from Salmonella poisoning” (Marler Clark, 2016). It is for this reason that we must be vigilant regarding our egg handling practices, especially in free-range systems where the risk of salmonella exposure is significantly higher. Continue Reading

The Un-BEE-lievable News

Channy Chhim, Environmental Science

Dean Fish, Geology

Chelsey Mullen, Pre-Veterinary Science

When people think about bees, they instantly think of being stung and maybe even allergies associated with them. However, cases of stinging tend to be from more aggressive species like hornets or wasps.These aggressive species tend to give bees a bad reputation, despite the fact that the honey bee is an integral part of our agricultural system. Honey bees not only produce honey, but they also pollinate, and therefore enable the procreation of, our fruit and flowering crops, which contributes to 40% of our food supply (Siegel and Betz, 2010). In 2010, honey bees aided the production of over $19 billion of crops in the United States alone, whereas all other pollinators combined contributed to the production of almost $10 billion of crops (US Fish and Wildlife, 2016). This means that honey bees alone are responsible for two thirds of animal pollinated crops. Wild populations of bees provide a free pollination service, which is worth $215 billion on a global scale (Goulson, Nicholls, Botías, & Rotheray, 2015). These crops not only include produce such as apples, squash, and almonds, but also commodities such as chocolate and coffee. Although the pollination services that bees offer are an integral aspect of the world’s agricultural production of insect pollinated crops, they go largely unrecognized. This is especially troubling now because bee populations are not only declining, but doing so at an alarming rate (Goulson, Nicholls, Botías, & Rotheray, 2015). Continue Reading

Significance of Wind Turbines on Bird Mortality

Birds flying over a field at dawn in winter. J. Marijis. Shutterstock

Birds flying over a field at dawn in winter. (Marijis, J.)

Jacqueline Kennedy- Environmental Science, Gina Chesmore- Animal Science, Johanna Smith- Animal Science

As scientists decipher threats to human health and the ecosystem, they look to birds to find indicators of these threats. Particular bird species are susceptible to changes in the environment, making them good indicators of environmental conditions. Rachel Carson was among one of the first scientists to study this linkage; she observed the impact of DDT on bird populations after World War II, when the compound was widely used as a pesticide. If it were not for birds, the Environmental Protection Agency would not have discovered the negative effects of the pesticide so readily. As a result of these findings the United States banned DDT in 1972 (Beard, 2006). Another example of birds as an indicator species is the use of canaries in coal mines to detect carbon monoxide and other toxic gases, since the birds are more sensitive to toxins and would show signs of poisoning before the miners did. Other examples include mortality of crows as an indication of West Nile Virus and sick vultures in Asia due to diclofenac, a drug administered to livestock in order to help them heal from wounds (Balmford, 2013). In order to continue to utilize birds as an indicator species, we must find ways to preserve their populations, as they are a necessary part of the food chain that can lead to scientific discovery in regards to both human health and ecosystem health. Continue Reading