Stabilization of Cd in Soil by Biochar and Growth of Rice (Oryza sativa) in Artificially Contaminated Soil
Zaryab Murad1*, Sobia Bibi1, Shehr e Yar Ahmad1, Mohsin Ali Khan1, Rimsha Sadaf2, Mauz ul Haq1, Umair Manan1 and Muhammad Younas2
1Department of Soil and Environmental Sciences, The University of Agriculture Peshawar, Peshawar, Khyber Pakhtunkhwa, Pakistan; 2Institute of Soil and Environmental Sciences, PMAS Arid Agriculture University Rawalpindi, Pakistan.
*Correspondence | Zaryab Murad, Department of Soil and Environmental Sciences, The University of Agriculture Peshawar, Peshawar, Khyber Pakhtunkhwa, Pakistan; Email: zaryab@aup.edu.pk
Figure 1:
Effects of different biochar concentrations on rice plant height grown in intentionally Cd-contaminated soil.
Figure 2:
Effects of different rates of biochar on rice plant grain yield grown in intentionally Cd-contaminated soil.
Figure 3:
Effects of different rates of biochar on the biological yield of rice plants grown in intentionally Cd-contaminated soil.
Figure 4:
Effect of different rates of biochar on the harvest index of rice plants grown in intentionally Cd-contaminated soil.
Figure 5:
Effect of different rates of biochar on the flag leaves length of rice plants grown in intentionally Cd-contaminated soil.
Figure 6:
Effect of different rates of biochar on the panicles length of rice plants grown in intentionally Cd-contaminated soil.
Figure 7:
Effects of different amounts of biochar on the fresh shoot weight of rice plants grown in intentionally Cd-contaminated soil.
Figure 8:
Impact of various biochar levels on the dry shoot weight of rice plants cultivated in soil artificially contaminated with Cd.
Figure 9:
Effect of different rates of biochar on fresh grains weight grown in intentionally Cd-contaminated soil.
Figure 10:
Effects of different rates of biochar on the dry grain weight of rice plants grown in intentionally Cd-contaminated soil.
Figure 11:
Impact of different rates of biochar on soil AB-DTPA extractable Cd.
Figure 12:
Effects of different rates of biochar on the content of Cd in rice shoot grown in intentionally contaminated soil.
Figure 13:
Impact of varying levels of biochar on the content of Cd in rice grains cultivated in intentionally Cd-contaminated soil.
Figure 14:
Effects of different quantities of biochar on the Cd total uptake by rice plants grown in intentionally Cd-contaminated soil.
Figure 15:
Impacts of different biochar concentrations on soil pH that has been artificially Cd-contaminated.
Figure 16:
Effects of varying rates of biochar on soil electrical conductivity under artificially contaminated.
Figure 17:
Impact of different rates of biochar on soil organic matter in artificially Cd-contaminated.
Figure 18:
Impact of different biochar levels on soil AB-DTPA extractable P in soil that has been intentionally Cd-contaminated.
Figure 19:
Effect of varying rates of biochar on soil AB-DTPA extractable K in intentionally Cd-contaminated soil.
Figure 20:
Impact of different rates of biochar on soil total N content in intentionally Cd-contaminated soil.