Impact of Copper Sulfate on Field Crops Mike
Rankin During the past year, there's been several articles in the popular farm press addressing the potential problem of increased soil copper (Cu) levels from the land spreading of spent copper sulfate (CuSO4) foot bath solutions with liquid manure. This occurs, of course, because the used CuSO4 solution is often pumped into manure lagoons, which significantly raises the Cu concentration. Some
things to know about copper Copper is an essential nutrient for plant growth. Like most micronutrients, it is needed in small amounts by the plant (less than 1 lb/acre/year is removed from harvested plant biomass). Soil minerals and organic matter hold copper very tightly so there is little risk of leaching. However, once Cu levels become high, they will remain that way for a long time. Several factors reduce the availability of Cu in soil. These include high organic matter, high soil pH, and fine textured (clay) soils. In Wisconsin, plant Cu toxicity situations have been extremely rare. Toxic levels in the plant cause reduced vigor, poor root development, and leaf chlorosis.
There have been no reported cases of Cu toxicity in dairy cattle due
to high forage Cu levels. Sheep,
on the other hand, are very sensitive to Cu levels (over 20 ppm in the
ration and figure on having lamb chops for supper). The Miner Institute situation
One of the first people to identify the potential problem of land
spreading spent CuSO4 solutions was Ev Thomas of the Miner
Institute in Chazy, New York. In 1998, the farm was using about 250 lbs. of CuSO4
per week for their 160 cow herd. This
amount of CuSO4 was being spread on 470 acres.
After a couple of years, Thomas noticed an upward spike in manure and
forage Cu concentrations. In 2001, the Miner Institute reduced from 5 to 3 the number
of days per week that CuSO4 was used and reduced the solution
concentration. They also began
using tetracycline as an alternative treatment in alternating weeks.
These changes reduced the total amount of Cu being applied on the
land from 3300 to 1000 lbs annually. How
much Cu is being applied on WI fields? Copper sulfate is 25 percent elemental Cu. To determine the amount of Cu being applied per year, and more importantly per acre, first determine the amount of CuSO4 being used per week. Multiply this number by 52 weeks, then by 0.25 to determine lbs. of Cu applied per year. Finally, divide by crop acres receiving manure per year to obtain pounds of Cu applied per acre. For example, if a farm operator is using 250 lbs of CuSO4 per week and spreads manure on about 400 acres annually, the field-loading rate would be: (250
lbs./wk) x (52 wks) x (0.25) = 3250
lb Cu/yr (3250
lb Cu/ yr) divided by (400 acres) = 8.1 lb Cu/ac/yr It seems that many farms using CuSO4 solutions fall into the range of 7 to 8 lbs of Cu applied per acre per year. Remember that some fields may not get manure applied every year. The following table can be used to quickly estimate the amount of Cu from CuSO4 applied per acre per year.
Liquid dairy manure with spent CuSO4 solution added could
easily have a Cu concentration of over 500 ppm (dry matter basis).
To put this in some perspective, liquid swine manure and biosolids
(sewage sludge) also may contain similarly high levels of Cu.
Thus, it is certainly not unprecedented to be applying over 5 lbs. of
Cu per acre per year to crop land. Such
a practice, in and of itself, will not cause harm to plants or livestock.
In fact, Wisconsin DNR loading limit regulation for biosolids is 66
lb/ac annually (1350 lb. lifetime) on materials ranging from 1500 – 4300
ppm Cu. The difference with biosolids compared to dairy manure is that
biosolids are not typically applied repeatedly to the same fields over a
period of years. Recommendations Given current knowledge, here are some recommendations relative to CuSO4 use and land application:
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