Long-term effect of organic amendments on soil enzymatic activities Cheviron Nathalie1,P, Marrauld Christelle1, Vecten Helen1, Houot Sabine2, Bispo Antonio3, Grand Cécile3 , Galsomiès Laurence3, Mougin Christian1 (1) INRA, Unité PESSAC 78026 Versailles, FR (2) INRA/AGROPARISTECH, UMR Environnement et Grandes Cultures, 78850 Thiverval-Grignon, FR (3) ADEME, 49004 ANGERS cedex 01, FR [email protected] Abstract Microbial ecology provides tools to understand the effects of organic matter application on soil microbial functions, following soil amendment with organic waste products. Here we studied the longterm effect of soil amendment with composts and manure on different soil enzyme activities involved in the C (β-glucosidase), N (urease), S (arylsulphatase) and P (phosphatase) biogeochemical cycles. The amended plots showed higher enzymatic activity than the unamended ones. Our results demonstrate that organic amendments had a noticeable long-term effect on enzyme activities, depending on the cycle considered. Clearly, the dynamics of microorganism response is closely related to organic matter nature, and more precisely to its degradability. Introduction For many decades, soil has been considered as a reactor for recycling human and agricultural wastes. Since 2006, it is considered as a non-renewable resource to protect (CEE, 2006). Threats affecting soils, such as organic matter loss or contaminations by chemical pollutants, have been pointed out by EEC. The use of organic waste products (OWP) seems a good alternative to reduce soil organic matter (OM) losses, to improve soil fertility, and thus to limit ecological deleterious impacts of intensive agriculture. These actions stimulate the activity of soil microorganisms and reactive the biogeochemical cycles [1]. Amendments allow the storage of Carbon in soil as a remediation of agricultural practices. In France, the SOERE-PRO is a long-term experiment network to observe and understand the effects of OWP amendments on cropped soils. The use of long-term field experiments is very useful to investigate the environmental impacts of recycling organic residues on soil biochemical properties, as well as the possible resilience of the agrosystems, to assess cost/benefit balance, and to improve agricultural practices. Since 1998, one site of the SOERE-PRO, Qualiagro (Feucherolles - Yvelines; France), allows to study the effects of several types of organic amendments (composts and manure) in relation with two levels of nitrogen. Soil microorganisms are involved in the transformation and recycling of OM [2] and contaminants [3, 4, 5]. They are the main contributors to biogeochemical cycles and are key actors responsible for optimal soil functioning [6]. Soil functions are maintained by the production of extra or intracellular enzymes [7]. Several authors have shown that OM amendments [8] and cultural practices [6] affect soil enzymatic activities. The changes observed are linked to modifications of gene and protein expression under the pressure of environmental factors [9, 10], thus governing the final enzymatic activities. In our laboratory, previous studies have shown that enzymatic activities were relevant to assess the impacts of human perturbations, namely urease, β-glucosidase, arylsulfatase, and phosphatase. In addition, numerous organisms including filamentous fungi are known to secrete oxidases [11]. The production of laccase, a phenoloxidase, is known as regulated by lignin availability and induced by pesticides at environmental concentration [12]. Enzymatic activities are relevant indicators of soil functioning [14] and soil functional biodiversity [15]. Here we investigated the enzymatic activities in the Qualiagro site, in relation with OM amendments. Materials and methods Experimental site For each treatment, the Qualiagro site (INRA and Veolia Environment collaboration) comprised four replicates of plots (45 m x 10 m, 450 m2). The treatments were: no organic amendment (CON), farmyard manure (FYM), biowaste compost (BIO), co-compost of green wastes and sludge (GWS) and municipal solid waste compost (MSW)(Figure 1). The present study was managed on plots with optimal mineral nitrogen fertilization. In the site, the luvisol was a silt loam comprising 15% clay, 78% silt, and 7% sand. Its initial pH value was 6.9 and initial organic matter was 1.8%. During the past twenty years, the average annual precipitations amounted to 582 mm, and the average annual temperature was 11°C. The experimental design CON FYM BIO MSW GWS MSW CON GWS CON MSW BIO MSW BIO FYM BIO FYM GWS bloc 4 FYM GWS FYM CON BIO MSW bloc 3 FYM MSW GWS bloc 2 BIO GWS MSW CON FYM Bloc 1 CON FYM GWS CON BIO GWS MSW CON low mineral N low BIO optimal mineral N Figure 1: Map of the Qualiagro site The physic-chemical characteristics of the amendments were listed in Table 1. Tab 1: Average physico-chemical characteristics of organic amendments applied in 1998, 2000, 2002, 2004, 2006, 2007, 2009 and 2011, GWS MSW BIO FYM Dry matter, g kg-1 fw 633 (±9) 678 (±129) 700 (±91) 396 (±97) OC, g kg-1 dw 308 (±48) 208 (±50) 320 (±72) 265 (±48) C/Ntot 10.7 (±2.2) 15.6 (±2.8) 11.7 (±1.9) 14.0 (±3.0) pH (in H2O) 7.7 (±0.8) 7.4 (±0.4) 8.5 (±0.2) 9.0 (±0.2) Potentially Mineralized Carbonb, %OC 44 (±11) 16 (±6) 20 (±10) 12 (±5) a fw, fresh weight; dw, dry weight; OC, organic carbon content; ON, organic nitrogen content ; C/Ntot, organic C to total N ratio b The excess mineralized carbon after 91 days in the soil-organic amendment mixtures was expressed as a percentage of the amendment organic C applied during incubation (after subtracting mineralized C of the control treatment) Enzymatic activity measurements The soils were collected at different times (at T0, then 6 and 18 months after amendments from) 2011 to 2013 at a depth of 0-10 cm. Samples were sieved through a 5 mm mesh, and stored at 12 °C before use. Soil water content was determined by drying 5 g of soil at 105 °C for 48 H. Tab 2: Characteristics of hydrolase activity measurements Substrates Incubation Incubation T°C λ (nm) Phosphatase 4-nitrophenylphosphate (0,05M) 30 min 37 405 β -Glucosidase 4-nitrophenyl β-D-glucopyranoside (0,05M) 1h 37 405 Arylsulfatase Potassium 4-nitrophenyl sulfate (25 mM) 4h 37 405 Urease Urea (0,4 M) 3h 25 650 Phosphatase, β-glucosidase, arylsulfatase, and urease activities were performed in microplate according to modified protocols [16, 17, 18, 19] less than 48 hours after sample collection. Briefly, hydrolases were measured in triplicates in 4 g soil samples mixed during 10 min at 250 rpm with 25 ml water. For phosphatase, β-glucosidase and arylsulfatase activities, soil solutions were incubated with specific substrates (Sigma chemicals) (Tab.2). Reaction was stopped with 0,5 M CaCl2 and 0,1 M Tris at pH 12. For urease activity, soil solutions were mixed with 0,4 M urea. NH4 formed was revealed with ammonium salicylate and ammonium cyan rate (Hach reagents). After the reactions, each plate was centrifuged 5 min at 2000 g, and absorbance was measured on a microplate reader Genius (SAFAS). The amounts of p-nitrophenol (PNP) and NH4Cl formed were obtained by the absorbance at 405 nm and 610 nm. Results and discussion Our results show that OWPs modify the soil organic matter status and microbial biomass during the months following OWP inputs (data not shown). Soil enzymatic activities are modified for P, C and N cycles with brought of organic amendment, according to OM status, as well with microbial biomass, water retention capacity and soil aggregate stability. The level of increase depends on the nature of the amendment, more specially on the status of organic matter added, its availability and degradability. Moreover, these organic amendments promote immobilization of enzymes linked to humic colloids, which could strongly affect soil quality. Fig 2: Time-course of hydrolase activities (expressed in % of control plot): A: phosphatase activity, B: arylsulfatase activity, C: urease activity, D: β-glucosidase activity. Amendments were: farmyard manure: FYM (purple lines), biowaste compost: BIO (red lines), municipal solid waste compost: MSW (blue line), co-compost of green wastes and sludge: GWS (green line). Significant differences between control and amended plots are with (*). Dick [7] and many researchers reported that phosphatase activity was increased by the addition of organic materials. Our results are in agreement with these previous studies, but the responses vary according to amendment and duration after application (figure 1A). Just after amendment, FYM increases the activity by 40%, probably because of its high biodegradability and micro-organisms addition. Incorporation and stimulation of phosphatase activity occurs later for MSW and GWS, and no effect is observed for BIO after 18 months. Whatever the amendment considered (Figure 1B), arylsulfatase activity does not show contrasted results. That lack of noticeable effects is in agreement with previous studies [20], which reported that arylsulfatase activity was inversely affected by elevated urban and industrial wastes amendments. Just after amendments, urease activity increases slightly (BIO) or highly (FYM and MSW). No effect of GWS is noticed. For 18 months, the activity is increased by BIO, FYM and GWS. The low effect of MSW may be due to accessibility of OM, N content and low NH4+ concentration. High NH4+ concentration induces low urease activity in GWS. Nevertheless, progressive incorporation of recalcitrant OM with GWS and BIO induces a high increase of activity with time. Several months after amendments, BIO and GWS do not modify β-glucosidase activity with respect to the control. These two amendments present high amounts of recalcitrant OM and the impacts of amendment appear later, after incorporation to the soil. The highest response occurs with MSW, the most biodegradable compost exhibiting a high OC content. Then, FYM increases highly enzymatic activity. Conclusion Our results demonstrate that organic amendments have noticeable long-term-effects on enzymatic activities. They suggest that soil microbial processes are sensitive indicators for the monitoring of soil biological properties changes due to amendments by organic wastes. References [1] Pascual JA, Garcia C, Hernandez T. 1998. Comparison of fresh and composted organic waste in their efficacy for improvement of arid soil quality. Bioresource Technology 68, 255-265. [2] Burns RG, 1979. Interaction of microorganisms, their substrates and their products with soil surface. 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The SOERE-PRO and Qualiagro programmes are acknowledged for their interdisciplinary research framework.
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