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Stabilization of Cd in Soil by Biochar and Growth of Rice (Oryza sativa) in Artificially Contaminated Soil

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.

Sarhad Journal of Agriculture

September

Vol.40, Iss. 3, Pages 680-1101

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