Symposium 2000

A Vision for a Greener Campus:

Pesticide and Herbicide Use on the Goshen College Campus
 
Deborah Scott
Junior
Goshen College 2000

Goshen College (IN) is a small Mennonite liberal arts college. The town of Goshen is surrounded by farmland and encroaching urban development. It is located in Elkhart County, which has the distinction of being fifth in the country for producing cancer-causing pollution (Sierra Club, "Cancer"). Against this backdrop of industrial buildup and agricultural dominance, Goshen College stands as a Christian community.

Although the campus of GC is not large by university standards, it does have attractive grounds with trees, flowerbeds, and ample lawns. The physical plant is in charge of the campus grounds maintenance. They have made some ecologically sound decisions that depart from the normal protocol of lawn care - for example, they mulch fallen leaves and grass clippings and let them decompose on the lawn instead of sweeping them away. But in many ways, the philosophy and practices of the lawn care is in keeping with the dominant society's standards of lawn beauty and the accompanying necessary chemical regimen.

This paper will address four of these pesticides and herbicides. The ecological and human risks of using chlorpyrifos, 2,4-D, diazinon, and glyphosate will be examined. Some suggestions will then be given on why GC should stop using these chemicals and on possible alternatives for lawn care.

But first, it is helpful to take a quick look at where this ideal of a perfect lawn originated. For centuries, people in North America dealt with their living spaces in ways that were conducive to their natural environment. As new immigrants came, they brought their own ideas of what lawns should be. Those coming from England were used to the lush, green, rolling lawns possible in such a damp climate, and this ideal began to take hold. In 1892, the senior agrostologist at the U.S. Dept. of Agriculture defined the perfect lawn as "the growth of a single variety of grass with a smooth, even surface, uniform color, and an elastic turf which has become so through constant care, so fine and so close in texture as to exclude weeds" (Jenkins, 52). At that time it was virtually impossible to achieve such a lawn in the United States - the majority of the country did not have the time, energy, or money. It took money because the US did not have the proper biological conditions for such lawns, and there was little point in spending energy to achieve something most didn't care about. As the decades went on, however, the upper classes aggressively forced their ideal onto the masses. Publications stressed lawn care, advertising campaigns were based on lawn care, and community contests for beautiful lawns were held. Nonetheless, those lawns were still practically out of reach for most people, and so the monoculture dream remained unrealized.

This schism between ideal and reality persisted until World War II, when the chemical miracles began to appear. Chemical warfare research led to the development of insecticides, and suddenly the masses were equipped with weapons to wage a full out war on their natural environment (153). And war it was. The new chemicals were marketed with the same militant language the masses heard from their patriotic government. The language was aggressive and violent, and Nature was portrayed increasingly as a woman who could now be dominated and controlled. Scientists and the public embraced methods of lawn care that stepped further and further away from the natural (133). With these new chemical and technological tools, a uniform lawn became possible in places as unlikely as Arizona, and soon most of the country had embraced an ideal which had formerly only belonged to a few.

Today the ideal of a golf-course-smooth and uniform lawn is firmly in place and treated as an unquestionable standard. Nonetheless, this is only possible with careful maintenance and poisoning. The Goshen College campus is arguably far from achieving the desired "green carpet" effect, but we work diligently towards it, attempting to attract prospective students and parents who are assumed to take this ideal for granted. Four of the tools in this struggle are chlorpyrifos, 2,4-D, diazinon, and glyphosate.

All four of these pesticides and herbicides are used widely by the rest of the United States. In 1995, they held the number 1, 2, 5, and 6 spots for pesticides most commonly used in non-agricultural sectors of the U.S. and the number 1, 2, 3, and 7 spots for industrial, commercial, and government usage (EPA, Office of Pesticide Programs). Although they are now a common presence, these are strong poisons that do not only affect the "pests" in our lives.

Chlorpyrifos

Chlorpyrifos is used on the GC campus in the form of "Dursban," sold by Dow Chemical Company. It is a broad-spectrum organophosphate insecticide of toxicity class II - moderately toxic. Body surface contact, ingestion, or inhalation can introduce the chemical (EXTOXNET, Chlorpyrifos). First developed as a nerve-gas agent for chemical warfare, organophosphates work by inhibiting the enzyme cholinesterase (Monks, 17). This leads to a build up of acetycholine at nerve junctions that can cause uncontrollable spasms of the muscles. This affects the central nervous system, cardiovascular system, and respiratory system (EXTOXNET, Cholinesterase; EXTOXNET, Chlorpyrifos).

Because it is generally regarded as a safe alternative to more toxic chemicals, it is applied widely and often with less caution by homeowners. Every year 20 to 24 million tons of chlorpyrifos are applied annually, and it can be found in over 800 products. It is, essentially, everywhere and in everyone. In a recent study of 993 adults by the Environmental Protection Agency (EPA), 80% had "measurable concentrations" of chlorpyrifos in their urine. Of the children, 90% had chlorpyrifos in their urine (Associated Press).

The human health effects of chlorpyrifos are currently being closely reexamined by the EPA. Dow's spokesperson insists that, when used properly, the chemical has "wide margins of safety" (Associated Press, 1999). Nonetheless, Dursban has a history of causing problems. In 1995, Dow was fined $732,000 by the EPA for failing to report complaints of chronic neurological effects caused by Dursban ("DowElanco fined", 54). Between 1985 and 1992, 11,000 children under the age of five reported to Poison Control Centers for chlorpyrifos exposure (NRDC, Chlorpyrifos).

Part of the controversy involves the question of how much chlorpyrifos is too much. The chemical is rather quickly broken down and passed through the human body. On the other hand, it is very toxic at higher amounts, and it possibly has chronic toxicity - particularly in the cases of workers exposed to low levels on a daily basis (EXTOXNET, Chlorpyrifos). Children, infants, and fetuses are more susceptible to the chemical's effects. Exposure from multiple sources is also a complicating factor in determining risk.

Chlorpyrifos is toxic to ecological systems. It is highly toxic to fish and almost all aquatic life , both freshwater or marine. Deaths can result from concentrations as low as 0.01 pounds per acre! Unlike warm blooded animals, aquatic organism's tissue bioaccumulates the chlorpyrifos, causing a build up of chemical concentration from 58 to 5100 times the environment's concentration (EXTOXNET, Chlorpyrifos). This is relevant because the chemical does end up in aquatic environments. Chlorpyrifos is one of two insecticides that have been detected consistently in urban runoff and in urban streams. Studies on urban streams have found the chemical to be acutely toxic to Ceriodaphnia in runoff that contained chlorpyrifos concentrations at the parts per trillion level (Schueler, 4).

Chlorpyrifos is also highly toxic to bees. It is moderately to highly toxic to birds that are exposed to the chemical by grazing from treated lawns and land. Both bees and birds are vital organisms in a healthy ecosystem.

The half-life of chlorpyrifos in soil is generally between 60 to 120 days but can range from 2 weeks to 1 year. The rate of breakdown is very much dependent on the type of soil, the climate, and other environmental conditions. As a rule, the chemical adsorbs to soils strongly and is therefore not likely to leach into groundwater systems. But as it is regularly found in run off, its movement is not completely limited (EXTOXNET, Chlorpyrifos).

2,4-D

2,4-D is a phenoxy compound with many derivatives and forms that is commonly used in its acid form, 2,4-dichlorophenoxyacetic acid. It is a post emergence broadleaf herbicide, targeting plants after they have emerged from the soil. It is toxicity class III for oral exposure and toxicity class I (highly toxic) for eye exposure (EXTOXNET, 2,4-D). 2,4-D works by acting like auxins, plant hormones that control growth. It kills by causing excessive growth that crushes the xylum and phloem of the plant (Cox, Spring 1999, 15).

The chemical was first put on the market in 1944, developed jointly by the American Chemical Paint Company and the U.S. Golf Association. 2,4-D was hailed as a miracle weed killer that could transform any lawn (Jenkins, 151). This "miracle" was the principle ingredient in Agent Orange (though another ingredient, dioxin, caused the majority of controversies) (EXTOXNET, 2,4-D). Today it is contained in over 1,500 over-the-counter weed-killing products, and 60 million pounds are used annually in the U.S. (Jenkins, 164; Cox, Spring 1999, 14).

As with chlorpyrifos, the effects upon humans are not completely clear. A National Cancer Institute study found that Kansas farmers spraying 2,4-D had 8 times the risk of developing non-Hodgkin's lymphoma (Jenkins, 166). Numerous studies done on rats and several case studies have supported this link between exposure and cancer rates. Numerous other studies, however, have not found a link. At present it is unclear whether 2,4-D is a carcinogen.

Myotonia is the most common symptom of acute poisoning. Myotonia is a neurological reaction to toxins that prevent muscles from relaxing after contraction (Cox, Spring 1999, 16). At high doses, 2,4-D has caused birth defects, and it will pass through the placenta in pigs and rats. Humans repeatedly exposed suffer a number of medical problems - mainly muscular effects such as loss of coordination or bladder control, but also liver, kidney, and gastrointestinal effects (EXTOXNET, 1996). Whether or not it causes peripheral neuropathy is again unclear. Cases have occurred in which exposure seemed to lead to problems caused by deadened nerves; nonetheless, there have not been any reliable laboratory tests that substantiate these results (Cox, Spring 1999, 16).

The ecological effects of 2,4-D and its breakdown chemicals can be significant. Depending on the preparation of the chemical, it can be highly toxic to fish (EXTOXNET, 2,4-D). One of its breakdown products is acutely toxic to fish at 2 parts per million. Earthworms that contact 2,4-D suffer acute toxicity (Cox, Fall 1999, 16). 2,4-D is classified as slightly toxic to birds, but some studies have found that young birds are killed or stunted by feeding off of contaminated vegetation (Cox, Fall 1999, 14).

2,4-D has a low half-life in soil - generally less than 7 days (EXTOXNET, 2,4-D). It does not pose a high risk of leaching into the groundwater. Despite these positive characteristics, 2,4-D has frequently been found in urban stormwater, which often runs untreated into urban streams. A significant storm on a freshly treated lawn will cause 90% of the applied 2,4-D to run off. While such conditions are generally avoided, run off is a severe problem for such a highly toxic aquatic herbicide (Schueler, 1995). Another problem occurs when grass clippings that have been treated with 2,4-D are composted. Again, despite its fast half-life, 2,4-D still in compost has been found to reduce plant growth in concentration as low as 2 parts per million (Michel, Graeber, et al, 64). And, as mentioned, the chemicals that 2,4-D decomposes into can be harmful to the environment as well.

Glyphosate

Glyphosate (N-(phosphonomethyl)glycine) is the active ingredient in Roundup, manufactured by Monsanto Company. Glyphosate is a broad, nonselective herbicide of toxicity class II (moderately toxic) (EXTOXNET, Glyphosate). Glyphosate has been seen as the near-perfect herbicide for years ú an herbicide that is practically nontoxic to humans and wildlife, not carcinogenic, not mutagenic, not teratogenic, and not at risk of leaching in soil (EXTOXNET, Glyphosate). Because of its effectiveness as an herbicide and because of its ecologically friendly reputation, an estimated 38-48 million pounds are used in the U.S. annually (Cox, 1998, 3). In 1998, Roundup brought in half of Monsanto Company's corporate profits, with annual sales rising by 20% annually for the past few years (PANUPS, Glyphosate).

Recently, however, glyphosate has been the subject of much debate in medical and scientific fields. A study released in March of 1999 found that exposure to glyphosate was linked to increased risk for non-Hodgkin's lymphoma (Miller, 622). The European Union is currently conducting a review of glyphosate, and preliminary results show that even when used properly it harms beneficial species and reduces biodiversity (PANUPS, Glyphosate). Studies by the International Organization for Biological Control determined Roundup to be toxic to several beneficial insects, including the ladybug.
In Roundup the glyphosate is combined with a surfactant to help the chemical reach and invade the plant cells. This combination of glyphosate and surfactant is much deadlier to aquatic life forms, wildlife, and humans. The acute toxicity level for fish to Roundup is 2 to 5 parts per million - drastically lower than simply glyphosate. Roundup harms nontarget plant life as well. Those plants that it does not kill are harmed by the chemical's lethal effect on the mycorrhizal fungi and nitrogen-fixing bacteria (Cox, 1998, 12).

Diazinon

Like chlorpyrifos, diazinon is an organophosphate, operating by inhibiting cholinesterase. It is a Restricted Use Pesticide of toxicity class II or III, depending on the formula. Diazinon is not itself a potent cholinesterase inhibitor, but when introduced into an animal it is broken down into diazoxon, a very strong cholinesterase inhibitor. In humans and animals, the half-life is 12 hours, and it is excreted quickly through the urine and feces. Still, high exposures have killed humans. Ironically, because it is recognized as a dangerous pesticide and therefore not available for the public to use, there is less controversy about the dangers of it usage (EXTOXNET, Diazinon).

On an ecological level, diazinon is highly toxic to many organisms. Treated open areas are a constant lethal threat to birds. In 1988 the EPA disallowed the use of diazinon on golf courses and sod farms because of massive die offs of congregating birds (EXTOXNET, Diazinon). The toxic effects of diazinon on geese, songbirds, and amphibians have been known for a number of years (Schueler).

Diazinon has a moderately long half-life in soil (EXTOXNET, "Movement of"). Although it does not usually migrate in the soil, it has leached into groundwater and contaminated wells in U.S. Western coast, Canada, and Japan (EXTOXNET, Diazinon). It is regularly found in stormwater runoff at concentrations of 0.5 to 5 parts per billion; yet that low concentration is enough to be acutely toxic to a wide variety of aquatic life forms. Fish, particularly freshwater fish, are highly susceptible to diazinon. Once in the water, diazinon can breakdown quickly (half-life of two weeks in highly acidic water) or very slowly (half-life of six months in neutral water).

Diazinon does not only move by water and soil. In the Central Valley in California the main source of diazinon has been rain and fog drifting down from nearby treated orchards (Schueler, 1995).

WHY CHANGE?

The research on these pesticides and herbicides is ongoing, and changing the groundskeeping practices at GC based on the potential long term human effects is probably unrealistic. On the other hand, it does appear that these chemicals have negative ecological effects on the biodiversity of the GC campus, the aquatic life exposed through various sources, and the health of the soil ecosystem. Officially, the scientific and industrial communities have determined what they believe those negative effects to be and have deemed them "acceptable." Other communities of scientists, citizens, and professionals have measured the risks as higher and find them unacceptable. Increasingly, those voices of dissent are coming from official bodies, such as the European Union and the EPA. The Goshen College administration has listened to the dominant voice thus far. Why should our campus change these practices?

Goshen College needs to change because we are a Christian community. We need to change because no unnecessary damage to God's creation is "acceptable."

In the 1991 Mennonite Central Committee commissioned book Earthkeepers, Art and Jocele Meyer call the Mennonite church to take responsibility for ecological destruction and injustice. They draw out two primary themes in Biblical teaching: "Land is a gift from God. That gift is to be received and cared for as a trust" (26). The Mennonite community often talks about "stewardship," but do we recognize how much more of a gift the earth is than mere money, or how much of an act of praise it would be to restore our ecosystems? Do we recognize, as Paulos Mar Gregorios does, that Christ's redemption is for all: the Church, the human race, and all "orders of created existence" in the universe? (88) Do we truly believe that our redemption is related to that of the whole earth?

We cannot view our call to care for the land as a spiritualized call or as an abstract concept. We have been placed in covenant with this marvelous creation and with God (Dyrness, 64). Our love and respect for the earth is a reflection of and connection to our love and respect for the Creator. This call to be stewards of the land is deeply imbedded in the Mennonite tradition, but the Mennonite community is broadening and moving away from our former cultural definitions. It is time for us to reclaim that tradition as part of our active theology.

At GC, living out this stewardship has taken form in the Merry Lea Educational Facility and Nature Reserve, in the new Environmental Studies program, and in the lives of many of the faculty, staff, and students. Unfortunately, we are also continually defiling the land, water, and air that we inhabit. The use of pesticides and herbicides is one of the more blatant ways in which we are doing this. It is not altogether clear how much we are harming our own bodies with these practices, but it is certain that we are disrupting the natural ecological cycle. Thankfully, this practice is one that we have the resources to change.

Reducing Pesticide and Herbicide Use on the GC grounds

There are several changes that could lead toward a reduction and perhaps elimination of pesticide and herbicide use on the grounds of GC. These can be divided into two areas: changing lawn care practices and reducing the amount of turf.
The changes in how we care for the lawns would focus on improving the health and stability of the grass and ground. Adjusting the way we mow is one simple change. Mowing at 3_ to 4 inches increases the grasses' resistance to drought and pests because taller grass blades lead to stronger, larger roots. In addition, taller grass chokes out a great deal of the annual weeds (Sachs, 47). Sharpening the mower blades after approximately every eight hours of mowing is another simple step that helps. Sharper blades make for a cleaner cut and less evaporation or chance of infection (Sachs, 48).
Applying a quarter inch of compost on the lawns in the fall of each year would improve the soil and thus the health of the grass. This compost could be produced within the campus using the food waste from the cafeteria and the lawn waste that is not mulched. The notion of a compost-covered lawn may make administrators and public relations officials cringe, but within a few days the compost would not be visible. For many it is a more attractive option than staying off the lawns for a few days because of chemical sprayings. Another option would be to apply a compost tea from water run through ripe compost.

Not having monoculture lawns would also help to cut down on weeds and pest damage. If one grass out of three or four types of grasses is targeted by a pest, the results are not as drastic as when that is the sole grass (Sachs, 49). GC experienced the hazards of monoculture landscaping when its locust trees were all infected and consequently cut down. Mixing grasses would minimize pest damage and lead to a stronger, healthier lawn.

At first some of these practices may take more money than our traditional ones, particularly during our initial experiments. But because many of these possibilities are preventative and restorative instead of covering up problems, they would pay off for themselves. Healthier grass in a more stable environment is less expensive to care for. Large universities such as University of Wisconsin and small colleges such as Warren Wilson College are in the process of implementing these ideas and more. Such institutions are resources that we can and should use.

As simple some of these ideas seem, they would require more than just a few changes in the lawn care routine. They would require a change of perception on the part of the physical plant, the administration, and the campus community. For example, we would stop focusing on eliminating the pests and concentrate on strengthening the health of the lawn. Eliot Coleman, a master organic gardener, differentiates these two focuses as "pest negative" and "plant positive." Infestations of pests or weeds are a sign that the plant (grass, in our case) is stressed and can not defend itself (Coleman, 173).

This stress can result from too much irrigation, harmful maintenance practices such as mowing too short or with a dull blade, or the pesticides and herbicides themselves. These chemicals, in addition to killing off vegetation and wildlife, "suppress the soil's biological activity," killing off the beneficial bacteria and fungus (as mentioned in the sections on 2,4-D) and throwing off the natural balance (Sachs, 49). Another cause of stress is attempting to grow something that is not fitted to the environment. This leads us to our second major area of change, the amount of conventional lawn.

Cutting down on the amount of turf would right away reduce the need for pesticides or herbicides. This turf reduction could be an ecological, social, and spiritual improvement if we chose to redo those portions in a spirit of bioregionalism.
Bioregionalism is a term that is becoming increasingly common. It comes from bios, life, and region, territory. Bioregionalism means something a bit different for every individual and community, but in general it points towards listening to and respecting the natural systems of one's area (Dodge, 5). It means digging in where you are and helping to restore the ecological and human communities to which you already belong. One way that this can occur at Goshen College is by restoring sections of our lawn to natural grassland or wildflower meadows.

We could initially set aside a wildflower test area. The land would be plowed and then either seeded with native wildflowers or let alone for the dormant seed bank to reestablish itself. Once the plants were established, additional watering would not be necessary. Pesticides and herbicides are also not needed, and mowing need only be done one to three times a year, depending on the type of landscape wanted (Woodier, 14).

Not only would introducing such a landscape area cut down on labor and costs, it would also increase the native biodiversity of our campus. It would serve as a buffer for polluted runoff since such landscapes more effectively trap water and air pollutants than a grass lawn (Ahern and Boughton, 174). It would also connect us with the actual community and land of Goshen. Restoring a section of campus would foster a greater awareness of this land's background. It would be a symbol of our dedication to this place not only in spirit but also in flesh. It would be a step towards identifying with this watershed, this ecological area, this land.

The benefits of using chlorpyrifos, 2,4-D, glyphosate, diazinon, and other such chemicals have been measured in terms of enrollment numbers and the relative attractiveness of the campus to the outside. We can turn that view on its head. We can turn our efforts towards a bioregional, organic campus. We have the resources to make these alternatives a reality, and if we involve the entire campus and local community those changes can be done in a spirit of rejoicing. We can be creative with our landscaping instead of slaving to achieve the norm. We can attract students who support this concept. We can learn from our own setting, and we can be an educational tool for those in the Goshen and greater Mennonite community.
This won't be a simple process. But once we set our goals and start, we will find that completely phasing out pesticide and herbicide use will become less of a threat and more of a joyful prize. It will be an act of hope in the midst of social and ecological helplessness. It will be a call to the larger Mennonite community to live as stewards of and even partners with the earth. Redemption can be ours, but not through the "miracle" wonders of 2,4-D, nor through the effectiveness of Roundup. Restoring our covenant with the land can happen on the Goshen College campus. And the first step is to stop this poisoning of the land, water, air, and spirit.

 

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