The Disposal of Copper‐enriched Pig‐manure Slurry on Grassland

Batey, T.; Berryman, Claire E.

doi:10.1111/j.1365-2494.1972.tb00701.x

Cited by 51 publications

(17 citation statements)

References 5 publications

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“…Cu Van Rhee (1975), Batey et al (1972 Robinson et al (1971) Farmyard manures Cd Andersson (1976b) Mercury seed dressings Hg Fimreite et al (1970), Odsjo (1975) Orchard sprays Pb Jones and Hatch (1937) Pb,As Jones and Hatch (1945), Vandecaveye et al…”

Section: Nimentioning

confidence: 99%

Biological Monitoring of Heavy Metal Pollution

Martin

Coughtrey

1982

212

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Section: Nimentioning

confidence: 99%

Biological Monitoring of Heavy Metal Pollution

Martin

Coughtrey

1982

212

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“…(4),Kornegay et al (16), and Sutton et al(26). This paper reports the effects of the eleventh year of Cu rich swine manure or CUSO4 application on three soils.…”

mentioning

confidence: 92%

“…Batey et al (4) reported that three annual applications of Cu rich swine manure on a fine sandy loam soil at a rate of 12.3 kg Cu ha" 1 increased the concentration of Cu in pasture grasses; however, the level was not hazardous to grazing animals. In their study, yield decreases occurred where plants were smothered by applied manure.…”

Section: Introductionmentioning

confidence: 98%

Long‐term effects of copper rich swine manure application on continuous corn production

Anderson

McKenna

Martens

et al. 1991

Communications in Soil Science and Plant Analysis

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Three long-term field experiments were established in the spring of 1978 and continued through 1988 to evaluate corn (Zea mays L.) response to high Cu levels from Cu rich swine manure and CuSO 4 applications. The field research was conducted on soils with diverse properties, i.e., on a Bertie fine sandy loam (fine-loamy, mixed, thermic, Aquic Hapludults), a Guernsey silt loam (fine, mixed, mesic, Aquic Hapludalfs), and a Starr-Dyke clay loam (fine-loamy, mixed, thermic Fluventic Dystrochrepts-clayey, mixed, mesic, Typic Rhodudults). Three treatments in the long-term field experiments on the three soils were i) a control, ii) annual applications of Cu as Cu rich swine manure, and iii) annual applications of Cu as CuSO 4 equivalent to that in the manure. After the 11 years, 1109 mt ha -1 of wet Cu rich swine manure were applied for the manure treatment. The Cu rich manure, which contained an average of 1316 mg Cu kg -1 , was produced by swine fed diets supplemented with an average of 251 mg Cu kg -1 as CuSO 4 . An average of 325 kg Cu ha -1 added to the soils from the manure application over the 11 years exceeded U.S.E.P.A. guidelines for safe copper loading levels for cropland by 45 kg ha -1 . Copper concentrations in corn ear leaves were within the normal range of 3 to 15 mg kg -1 where the 325 kg Cu ha -1 were applied to the soils as either Cu rich manure or CuSO 4 over the 11 years. Concentrations of Cu in the grain also were in the normal range of 1 to 5 mg kg -1 where the high level of the two Cu sources were applied to the soils. There was no decrease in corn yield on the three soils from application of 993

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“…The pollution of Cu in environment may have caused by animal manure. After that, Cu is used as supplement for inhibition of parasites as well as the industrial factory such as paint factory and the disposed by electronic and electrical factory [27]. The anthropogenic sources of copper element is mostly found in pollution sites from landfills, mine sites, combustion of fossil fuels and domestic waste waters.…”

Section: Coppermentioning

confidence: 99%