Compensatory fertilization of Scots pine stands polluted by heavy metals

• Published in: Nutrient cycling in agroecosystems 1999-11, Vol.55 (3), p.239-268
• Main Authors: Maelkoenen, E. (Finnish Forest Research Inst., Vantaa (Finland). Vantaa Research Centre), Derome, J, Fritze, H, Helmisaari, H.S, Kukkola, M, Kytoe, M, Saarsalmi, A, Salemaa, M
• Format: Article
• Language: English
• Subjects: Ammonium; Ammonium nitrate; APLICACION DE ABONOS; Calcium; CHAULAGE; Chemical precipitation; Copper; Deposition; ENCALADO; Experiments; FERTILISATION; Fertilization; FERTILIZER APPLICATION; Fertilizers; Finland; HEAVY METALS; Immobilization; Limestone; LIMING; Magnesium; METAL LOURD; METALES PESADOS; Methylene; Microorganisms; Mycorrhizas; Nickel; Nutrient concentrations; Nutrient dynamics; Nutrient reserves; Nutrient status; Organic chemistry; Organic soils; Pine trees; PINUS SYLVESTRIS; Plant roots; Pollutant deposition; POLLUTED SOIL; Sediments; Smelters; Soil chemistry; Soil layers; Soil pollution; Soil properties; Soil solution; Soil types; SOL POLLUE; SUELO CONTAMINADO; Trees; Urea
• ISSN: 1385-1314; 1573-0867
• DOI: 10.1023/A:1009851326584

The results from four compensatory fertilization experiments located at different distances (0.5, 2, 4 and 8 km) along a heavy metal deposition gradient extending from the Harjavalta Cu-Ni smelter in SW Finland are presented. The experiments were established in middle-age Scots pine stands growing on dryish sites of sorted glaciofluvial sediments. The soil type in all the experiments is ferric podsol. The treatments in the experiments consisted of liming, a powdered slow-release mineral mixture and stand-specific fertilization which comprised at least methylene urea and ammonium nitrate.Monitoring of deposition and soil solution and studies on soil chemical and microbiological properties, on the nutrient status of trees and needle litterfall, on fine root dynamics and on the growth of the tree stands were carried out during a 5-year period.There was a severe shortage of exchangeable Ca and Mg in the organic layer of the most polluted stands. Although the uppermost mineral soil layer had relatively high exchangeable Ca and Mg concentrations, the trees were not able to utilize these nutrient reserves presumably due to the toxic effects of Cu and Ni on the plant roots and mycorrhizas.The treatments that included limestone markedly decreased the Cu and Ni concentrations in the soil solution and soil organic layer, presumably due to immobilisation through precipitation or absorption. The Ca and Mg concentrations correspondingly increased, which certainly contributed to the partial recovery of fine root and stand growth. The powdered mineral mixture and the combination of methylene urea and ammonium nitrate had no short-term effect on the microbial biomass and activity. All the fertilizer treatments increased volume growth in the most polluted stand. The stand-specific fertilization increased needle mass in heavily polluted stands, but the response of the needle mass to fertilizer treatments was low in the less polluted stands. No clear evidence was found to support the role of nutrient status in tree resistance.