 |
 |
 |
 |
 |
 |
 |
 |
 |
 |
 |
 |
 |
From BioCycle Journal of Composting &Organics Recycling Febuary 2002, Page 57 |
 |
ONGOING INVESTIGATIONS
PREVALENCE AND FATE OF CLOPYRALID IN COMPOST
More extensive sampling in Washington state shows presence of the herbicide in composts and a variety of feedstocks, while a study of grass clippings found both significant loss and residue of clopyralid
10 weeks after application.
Robert Rynk
NOW THAT clopyralid has been found in compost and composting feedstocks, the question that immediately leaps out is “What should we do about it?” This, of course, is the big question. The answer hinges on the answers to lots of other questions like: How widespread is the contamination? Is it a regional problem? Where does the clopyralid come from? Why doesn’t it breakdown during composting? Can we help it to breakdown faster? What levels are safe enough?
The discovery of clopyralid in compost is relatively recent so the effort to gather the answers is just beginning. It may take some time to sort through the information before the big question can be addressed. Nevertheless, the information gathering process at least has started. There are a number of interested parties looking into the issue including the U.S. Composting Council, U.S. Environmental Protection Agency, state environmental and agricultural agencies, universities, laboratories, compost producers, compost users, herbicide applicators and Dow AgroSciences, the manufacturer of clopyralid.
Not surprisingly, the leading edge of the investigation is taking place in Washington state, where the problem first hit the fan in the United States. Both Washington State University (WSU) and Washington State Department of Agriculture (WSDA) have started collecting and analyzing samples to determine how pervasive clopyralid is in compost and composting feedstocks. There are also new efforts to determine what the fate of clopyralid is in the environment (composting and otherwise) after it is applied.
WSDA STATEWIDE SAMPLING
In the wake of the problems resulting from clopyralid-tainted compost, WSDA is reexamining the uses of clopyralid in the state (see accompanying article, “Clopyralid Developments in Washington State”). First, WSDA needs to determine whether clopyralid residue in compost is potentially a statewide problem. Up until now, damage from clopyralid in compost has been documented only in eastern Washington, specifically in Spokane and Pullman. In addition, it has been suggested that the clopyralid contamination is due to the much higher than normal use in the eastern region.
In October, WSDA gathered samples of composting feedstocks and compost to test them for clopyralid and picloram, a clopyralid-like herbicide that also has caused problems in compost. The program was voluntary for composting facilities. Nine major facilities participated, five from western Washington and four from the eastern side of the mountains. The facilities known to have clopyralid contamination, from Spokane and WSU, were not included in this survey. The participating facilities are fairly diverse. In addition to their location differences, they comprise windrow and forced aeration operations and several are enclosed. Most process yard trimmings but some operations also handle food residuals, paper products or animal manures and bedding.
Separate samples were taken on the same day of incoming feedstocks and compost, both immature and final products. All samples were analyzed by the Anatech Lab. The detection limit was one part per billion (ppb).
The results of WSDA’s clopyralid analysis program are shown in Table 1. Picloram was not detected in any of the samples. However, clopyralid was detected above critical levels at every facility. To put the numbers into perspective, clopyralid is damaging to sensitive crops (e.g. tomatoes, potatoes, sunflower, beans, peas) at concentrations as low as 10 ppb (and even lower). The feedstock analysis does seem to implicate yard trimmings, and grass clippings in particular, as a primary source of clopyralid. However, the herbicide also was present in worrisome levels within feedstocks that included straw or manure. The most alarming numbers came from an eastern Washington facility where clopyralid was found in grass clippings at 1,550 ppb and at 477 ppb in immature compost. At the other facilities, the clopyralid concentrations in the mature or finished compost ranged from nondetect to 182 ppb. Seven of nine compost samples from eastern Washington and 12 of 14 compost samples from the Western region had clopyralid concentrations greater than 20 ppb. This is clearly not an eastern Washington phenomenon.
It is worth noting that, for each facility, this data represents a one-day in time picture. It does not necessarily show how the clopyralid concentration changes through the composting process.
WSU MONITORING PROGRAM
Since it was beset by herbicide contamination in 2000, the WSU composting program has been working to remove and prevent clopyralid and picloram from entering the feedstock stream. On an ongoing basis, WSU has tested a wide range of feedstocks and agricultural residuals that may affect compost quality, including animal bedding, manure, straw, hay and grain fed to cattle. The results of the analysis are available on the WSU compost program web site (www.css.wsu.edu/compost/). They are reproduced in Table 2.
As Table 2 shows, WSU compost continues to contain significant concentrations of clopyralid. Although timothy hay consistently contains some clopyralid, the feedstock analysis does not point to a specific clopyralid source. Rather, the detection of clopyralid in the feedstocks is sporadic and variable. While one batch of straw or hay can be relatively free of the herbicide, the next batch may carry enough clopyralid (or picloram) to contaminate several batches of compost. In general, the WSU test results suggest that clopyralid contamination is not restricted to grass clippings. Many agricultural products can move the herbicide into compost. For example, the horse manure tested (used to amend a local garden) showed damaging levels of both clopyralid and picloram.
Several of the feedstock test results are notable. First, hay produced on campus (sampled on October 26) still has a high concentration of picloram. This may include residual hay from the crop that brought picloram into the facility in 2000. (Overall, the levels of picloram, the herbicide that initially caused WSU problems, has appeared to have subsided.) Second, one sample of barley contained a relatively high concentration of clopyralid (114 ppb). This is a feed product, not a crop residue. When fed to cattle, much of the clopyralid will pass through the urine of the animals and be collected with the manure. At least one other cattle manure composting facility (outside of Washington) has reported barley as a likely source of clopyralid in compost. It demonstrates that herbicide residues are a concern to any agricultural products treated with clopyralid.
OTHER INVESTIGATIONS
The clopyralid problem is being investigated on other fronts as well. For instance, Dow AgroSciences is funding several studies that are intended to provide information about the degradation of clopyralid after it is applied.
One Dow AgroSciences-funded study is being conducted by WSU researchers in Puyallup. They are looking at clopyralid concentrations in grass clippings following application. The objective is to identify management practices that might reduce the concentrations in clippings collected for composting. Although the study is not completed, some preliminary results are available. The average clopyralid concentration in grass clippings mowed ten weeks after herbicide application were less than one percent of the initial concentration. However, that average concentration was 150 ppb, still high enough to potentially cause plant damage.
In conjunction with these trials, Woods End Research Laboratory is conducting studies investigating the fate of clopyralid during and after composting. Woods End also is attempting to determine what may be acceptable uses for compost that contains various levels of clopyralid contamination. Clopyralid behaves in a very specific manner. Some plant species — mostly in the grass family — are not affected at all at moderate to low levels, while others — in the broadleaf family — are severely affected. In conjunction with transportation agencies that use composts for roadsides, Woods End is determining which species of plants will not be affected in the time between application and sufficient biodegradation of the herbicide residues. According to Woods End, “the goal is not at all to condone clopyralid in composts, but to help retain value of composts by showing appropriate uses that do not affect crops.”
The fact that research is finding clopyralid difficult to eradicate should not be surprising. First, it is known to be a moderately persistent chemical (see this month’s Q&A column). Although it is dangerous to generalize, the test results from both WSDA and WSU suggest that clopyralid is sticking around through the composting process (see Tables 1 and 2). More importantly, we are trying to achieve residual levels on the order of a few parts per billion. Even substantial degradation of clopyralid could leave behind damaging concentrations as is being demonstrated by the WSU grass clippings study.
Woods End researchers stress from plant studies that clopyralid does not affect all crops in the same way, and certain genus are largely unaffected except by very high levels. Thus, certain composts that contain some residues can still be safely used, however, this requires good communication between the producer and the user. Whether such communication is practical in the long term remains to be seen.
END NOTE ON LAB ANALYSES
With regard to laboratory analyses for clopyralid, labs have had to adjust their methods in order to get detection at the parts per billion level. (More common detection is in the parts per million range.) The adjustments basically revolve around the methods to extract the chemical from the sample. For example, the Anatech lab cited earlier has been able to lower its detection level to one ppb.
However, Woods End Research Laboratory, in a separate study, has found that other test methods give different concentration levels, depending on how the sample is extracted. More aggressive extraction methods for plant tissue from Europe show higher levels present, according to Will Brinton of Woods End, but conversely, suggest lesser toxicity of the residues. For this reason, Woods End stresses that bioassays may more accurately reflect the real situation, since they report probable damage levels to crops.
In general, bioassays are a less expensive method to determine whether damage may occur from clopyralid. Several bioassay methods are available, including ones developed by Woods End and WSU (posted on the WSU web site at the address cited above). However, bioassays may show damage that is not related to clopyralid, such as high soluble salts, therefore it is important to look at the probability of contamination in feedstocks before making a judgement on the bioassay alone.
www.jgpress.com
BIOCYCLE | IN BUSINESS | COMPOST SCIENCE |
HOME