AMELIORATING ROLE OF N.P.K. FERTILIZER ON THE TOXIC EFFECTS OF Ni ON (SORGHUM) ROOT ANTIOXIDANT ENZYMES1
Table Of Contents
Chapter ONE
INTRODUCTION
- 1.1Introduction
- 1.2Background of Study
- 1.3Problem Statement
- 1.4Objective of Study
- 1.5Limitation of Study
- 1.6Scope of Study
- 1.7Significance of Study
- 1.8Structure of the Research
- 1.9Definition of Terms
Chapter TWO
LITERATURE REVIEW
- 2.1Overview of N.P.K. Fertilizer
- 2.2Toxic Effects of Ni on Sorghum
- 2.3Role of Antioxidant Enzymes
- 2.4Importance of Nutrient Management
- 2.5Previous Studies on N.P.K. Fertilizer
- 2.6Effects of Fertilizers on Plant Growth
- 2.7Impact of Heavy Metals on Plants
- 2.8Mechanisms of Antioxidant Enzymes
- 2.9Role of N.P.K. Fertilizer in Mitigating Toxicity
- 2.10Relationship Between N.P.K. Fertilizer and Antioxidant Enzymes
Chapter THREE
RESEARCH METHODOLOGY
- 3.1Research Design
- 3.2Sampling Methods
- 3.3Data Collection Techniques
- 3.4Experimental Setup
- 3.5Statistical Analysis
- 3.6Variables and Measurements
- 3.7Ethical Considerations
- 3.8Data Interpretation Methods
Chapter FOUR
DATA PRESENTATION AND ANALYSIS
- 4.1Overview of Research Findings
- 4.2Effects of N.P.K. Fertilizer on Ni Toxicity
- 4.3Antioxidant Enzyme Activity
- 4.4Comparison of Treatment Groups
- 4.5Influence of Environmental Factors
- 4.6Discussion on Plant Growth Parameters
- 4.7Implications for Agriculture
- 4.8Future Research Directions
Chapter FIVE
SUMMARY, CONCLUSION AND RECOMMENDATIONS
- 5.1Summary of Findings
- 5.2Conclusion
- 5.3Recommendations for Practice
- 5.4Contributions to the Field
- 5.5Areas for Future Research
Project Abstract
This study investigated the activities of superoxide dismutase (SOD), catalase (CAT), glutothione peroxidase (GP) and the level of malondialdehyde (MDA) in the root of sorghum grown in soils contaminated with 30ppm nickel, 30ppm nickel +20ppm fertilizer and 30ppm nickel + 40ppm fertilizer. Sixty sorghum seeds were germinated in these contaminated soils and were harvested after 2 weeks, 3 weeks, and 4 weeks of planting. Treatment of the plants with 30ppm nickel significantly increased (P < 0.05) the activities of SOD and the level of MDA in the roots compared with the controls. Also, the treatment significantly decreased (P < 0.05) the activities of CAT and GP in the roots compared with controls.The study also revealed a significant decrease (P < 0.05) in the activities of SOD and the level of MDA in plants grown in 30ppm Ni + 20ppm NPK fertilizer and 30ppm Ni + 40ppm NPK fertilizer respectively compared with those grown in 30ppm Ni concentration. These results show that 30ppm Nickel is toxic to sorghum roots for it increases significantly the production of reactive oxygen species but decreases significantly the excretion of reactive oxygen species. This is due to significant increase in the activity of SOD but significant decrease in the activities of CAT and GP. These results also showed that 30ppm Nickel damaged sorghum roots by significantly increasing lipid peroxidation and the levels of MDA. In addition, the results revealed that 20ppm and 40ppm NPK fertilizer had ameliorating effect on the toxicity caused by 30ppm nickel.
Project Overview
INTRODUCTIONTrace metals are redistributed in environment by fossil fuel combustion. This release can be expected to increase soil levels of trace elements such as Ni2+ resulting in a concomitant increase in the concentration of Ni2+ in plants and possibly in the food chain (Dominic et al, 1978). Nickel (Ni) is an essential micronutrient for plants since it is the active centre of the enzyme urease required for nitrogen metabolism in higher plants (Yan et al, 2008). Nickel deficiencies lead to reduced urease activity in tissue cultures of sorghum, rice and tobacco and in excessive accumulation of urea and toxic damage to the leaves of leguminous plants such as sorghum (Peter and Andre, 1986). However, excess Ni is known to be toxic and many studies have been conducted concerning Ni toxicity of various plant species. The most common symptoms of nickel toxicity in plants are inhibition of growth, photosynthesis, mineral nutrition, sugar transport and water relations (Seregin and Kozhevnikova, 2006). Heavy metal affects plants in two ways. First, it alters reaction rates and influences the kinetic properties of enzymes leading to changes in plant metabolism (Yan et al, 2008). Second, excessive heavy metals lead to oxidant stress. During the period of metal treatment, plants develop different resistance mechanisms to avoid or tolerate metal stress, including the changes of lipid composition, enzyme activity, sugar or amino acid contents, and the level of soluble proteins and gene expressions. These adaptations entail qualitative and/or quantitative advantage, and affect plant existence (Schutzendubel and Polle, 2002). It is known that excessive heavy metal exposure may increase the generation of reactive oxygen species (ROS) in plants, and oxidative stress would arise if the balance between ROS generation and removal were broken. Oxidative stress is a part of general stress that arises when an organism experiences different external or internal factors changing its homeostasis. In response, an organism either aims to maintain the previous status by activation of corresponding protective mechanisms or goes to a new stable state (Mittler, 2002). In several plants, Ni has been shown to induce changes in the activity of ROS รขโฌโ scavenging enzymes, including SOD catalase and glutathione peroxidase (Yan et al, 2008).The aim of this study is to investigate the effects of nickel on the activities of sorghum root antioxidant enzymes and also monitor the ameliorating effects of N.P.K. Fertilizer.