Nitrogen Mineralization in Texturally Contrasting Soils Subjected to Different Organic Amendments under Semi-Arid Climates

Author:

Javeed Hafiz Muhammad Rashad1ORCID,Ali Mazhar1ORCID,Kanwal Nitasha1,Ahmad Iftikhar1,Jamal Aftab2ORCID,Qamar Rafi3,Zakir Ali1ORCID,Andaleeb Hina4,Jabeen Raheela5ORCID,Radicetti Emanuele6ORCID,Mancinelli Roberto7ORCID

Affiliation:

1. Department of Environmental Sciences, COMSATS University Islamabad, Vehari Campus, Vehari 61100, Pakistan

2. Department of Soil and Environmental Sciences, Faculty of Crop Production Sciences, The University of Agriculture, Peshawar 25130, Pakistan

3. Department of Agronomy, Faculty of Agriculture, College of Agriculture, University of Sargodha, Sargodha 40100, Pakistan

4. Department of Biochemistry, Bahauddin Zakariya University, Multan 60000, Pakistan

5. Department of Biochemistry and Biotechnology, The Women University Multan, Multan 66000, Pakistan

6. Department of Chemical, Pharmaceutical and Agricultural Sciences (DOCPAS), University of Ferrara, 44121 Ferrara, Italy

7. Department of Agricultural and Forestry Sciences (DAFNE), University of Tuscia, 01100 Viterbo, Italy

Abstract

Nitrogen (N) is the prime essential nutrient for agricultural productivity, and its deficiency is overcome through the application of fertilizers. However, the rate of N mineralization from organic N sources is an important process to be monitored for efficient N use and sustainable agricultural management. Laboratory incubation studies were conducted for a period of 150 days to measure N mineralization (Nmin) from different organic amendments (OA) in texturally contrasting soils collected at three locations: SL1 (Bahawalpur, sandy loam), SL2 (Bahawalnagar, sandy loam), and SL3 (Rahim Yar Khan, sandy clay loam). A second study was also carried out for 25 days to monitor pH dynamics and ammonia volatilization from the same three OA-treated soils. The results showed that there was no significant difference in net Nmin between the soils for poultry manure (PMO) and feather meal (FMO), even if there was a substantial Nmin observed for PMC + FMO followed by poultry manure compost (PMC) at SL2 and SL3 soils. This might have happened due to higher microbial biomass carbon (257), nitrogen (61), fungal colonization (88 cfu g−1 soil) and enzyme activity (79) in SL3 soil receiving PMC + FMO after 150 days of incubation. However, the first-order kinetic model (R2 = 0.86–0.95) better explained the Nmin in all three soils amended with OA (PMC + FMO). The soil pH had more pronounced effects on Nmin in all three soils. A non-significant amount of ammonia volatilization was recorded regardless of the initial pH, buffering capacity, and texture variability of the soils. Further study on the particle size of OA and soil pH is warranted to determine the actual effect of OA on Nmin.

Publisher

MDPI AG

Subject

Nature and Landscape Conservation,Ecology,Global and Planetary Change

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