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Environmental Risks of Applying Sewage Sludge Compost to Vineyards

Carbon, Heavy Metals, Nitrogen, and Phosphorus Accumulation

Nathalie Korboulewsky*, Sylvie Dupouyet and Gilles Bonin

Laboratoire de Biosystématique et Ecologie Méditerranéenne (LBEM)—Institut Méditerranéen d'Ecologie et de Paléoecologie (IMEP), UMR CNRS 6116, Université de Provence, FST St Jérôme, case 421 bis, 13397 Marseille cedex 20, France



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  		Fig. 1. Total organic matter (OM) in control and amended topsoils (0–30 cm) measured before (12 Mar. 1999), 2 d after (24 Mar. 1999), 6 mo after (28 Sept. 1999), and 18 mo after (26 Oct. 2000) the amendment (mean and standard error of n = 3). For each sampling date, columns with the same letter are not statistically different (Tukey's Honest Significant Difference test, p < 0.05).

 


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  		Fig. 2. Nitrogen mineralization (NH+4–N and NO-3–N) over time in (a) the topsoil (0–30 cm) and (b) the subsoil (30–60 cm) following the application of 0, 10, 30, and 90 Mg ha-1 compost (fresh wt.). The sewage sludge compost was applied on 23 Mar. 1999.

 


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  		Fig. 3. Available P with time in (a) topsoil (0–30 cm) and (b) subsoil (30–60 cm) following the application of 0, 10, 30, and 90 Mg ha-1 compost (fresh wt.). The sewage sludge compost was applied on 23 Mar. 1999.

 




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