摘要
<p style="text-align:justify;"> <b><span>Background:</span></b><span> The objective of this study was to determine the short-term effect of urea fertiliser application on soil reactions in a Ferralsol, with particular thrust on P sorption. </span><b><span>Methods:</span></b><span> Two experiments were conducted for this purpose</span><span>:</span><span> </span><span>1</span><span>) a screenhouse pot experiment</span><span>;</span><span> and </span><span>2</span><span>) a laboratory P sorption component. The pot (10 litre capacity plastic pots) experiment was conducted at the Makerere University Agricultural Research, Kabanyolo in Uganda, using a Ferralsol. The study comprised of four urea N (46% N) fertiliser treatments, namely, 0, 40, 80 and 120 kg N·ha</span><sup><span style="vertical-align:super;">-1</span></sup><span>, equivalent to 0, 200, 400 and 600 mg N per pot. A completely randomised design was adopted with three replicates. Urea rates were applied in 50% split doses, one at planting and the other at 19 days after seedling emergence (to simulate farmer practice). This was followed by watering to field capacity using distilled water. Soil samples were taken at three daily intervals until day fourteen;thereafter, soil sampling was at an interval of seven days. The second urea split dose was applied at 21 days followed by soil sampling at </span><span>an </span><span>interval of three days till day fourteen. Thereafter, soil was sampled at seven day intervals until the end of experi</span><span>ment. Soil samples were analysed for exchangeable H</span><sup><span style="vertical-align:super;">+</span></sup><span>, Al</span><sup><span style="vertical-align:super;">3+</span></sup><span>, NH<sub>4</sub><sup style="margin-left:-9px;">+</sup></span><span>and</span><span> NO<sub>3</sub><sup style="margin-left:-9px;">-</sup> </span><span>ions. The reaction trends of the concentrations of these ions and Bray 1 P were used to structure different response curves representing the instantaneous reactions. As for the laboratory P-sorption study, treatments included the four rates of urea used in the pot experiment (0, 40, 80 and 120 kg N·ha</span><sup><span style="vertical-align:super;">-1</span></sup><span>) and seven levels of P (2.5, 5, 10, 20, 30, 40 and 50 ppm) as KH</span><sub><span style="vertical-align:sub;">2</span></sub><span>PO</span><sub><span style="vertical-align:sub;">4</span></sub><span>. The setup was incubated under laboratory conditions and soil samples were repeatedly taken at 10 days (after 4 days of urea incubation plus 6 days of P application). The P sorption data were fitted to Langmuir model. </span><b><span>Results: </span></b><span>The pot experiment revealed an abrupt drop in the concentrations of exchangeable Al</span><sup><span style="vertical-align:super;">3+</span></sup><span> and H</span><sup><span style="vertical-align:super;">+</span></sup><span> ions (p</span><span> </span><span><</span><span> </span><span>0.05) within the first 6 days after urea application, accompanied by a positive surge in the concentration of NH<sub>4</sub><sup style="margin-left:-9px;">+</sup> </span><span>ions. This phase (6 days) was followed by a rise in the levels of exchangeable Al</span><sup><span style="vertical-align:super;">3+</span></sup><span>, H</span><sup><span style="vertical-align:super;">+</span></sup><span> and NO<sub>3</sub><sup style="margin-left:-9px;">-</sup> </span><span>ion concentration, which was inversely mirrored by a drop in the concentration </span><span>of NH<sub>4</sub><sup style="margin-left:-9px;">+</sup> </span><span>ions. Consequently, the patterns displayed by the soil reactions </span><span>were delineated into four phases, with Phase 1 (6 days) being characterised by urea hydrolysis reactions of deamination and ammonification, Phase 2 (10 days) being</span><span> </span><span>dominated by nitrification and its acidifying properties, Phase 3 being a repeat of Phase 1, both occurring immediately after urea application (within 6 days);and Phase 4 being a repeat of Phase 2. As for the P-sorption study, the effects of urea hydrolysis in a Ferralsol markedly increased soil pH and surprisingly P sorption. The contradictory P sorption behavior, despite the drop in exchange acidity was attributed to presence of divalent calcium in the extraction reagent used. </span><b><span>Conclusion:</span></b><span> The short term insights obtained in response to urea N application in the Ferralsol, are eye openers to future use of N fertilisers as well as strategic management of the associated acidification process which is often more costly and complicated to manage.</span> </p>
<p style="text-align:justify;"> <b><span>Background:</span></b><span> The objective of this study was to determine the short-term effect of urea fertiliser application on soil reactions in a Ferralsol, with particular thrust on P sorption. </span><b><span>Methods:</span></b><span> Two experiments were conducted for this purpose</span><span>:</span><span> </span><span>1</span><span>) a screenhouse pot experiment</span><span>;</span><span> and </span><span>2</span><span>) a laboratory P sorption component. The pot (10 litre capacity plastic pots) experiment was conducted at the Makerere University Agricultural Research, Kabanyolo in Uganda, using a Ferralsol. The study comprised of four urea N (46% N) fertiliser treatments, namely, 0, 40, 80 and 120 kg N·ha</span><sup><span style="vertical-align:super;">-1</span></sup><span>, equivalent to 0, 200, 400 and 600 mg N per pot. A completely randomised design was adopted with three replicates. Urea rates were applied in 50% split doses, one at planting and the other at 19 days after seedling emergence (to simulate farmer practice). This was followed by watering to field capacity using distilled water. Soil samples were taken at three daily intervals until day fourteen;thereafter, soil sampling was at an interval of seven days. The second urea split dose was applied at 21 days followed by soil sampling at </span><span>an </span><span>interval of three days till day fourteen. Thereafter, soil was sampled at seven day intervals until the end of experi</span><span>ment. Soil samples were analysed for exchangeable H</span><sup><span style="vertical-align:super;">+</span></sup><span>, Al</span><sup><span style="vertical-align:super;">3+</span></sup><span>, NH<sub>4</sub><sup style="margin-left:-9px;">+</sup></span><span>and</span><span> NO<sub>3</sub><sup style="margin-left:-9px;">-</sup> </span><span>ions. The reaction trends of the concentrations of these ions and Bray 1 P were used to structure different response curves representing the instantaneous reactions. As for the laboratory P-sorption study, treatments included the four rates of urea used in the pot experiment (0, 40, 80 and 120 kg N·ha</span><sup><span style="vertical-align:super;">-1</span></sup><span>) and seven levels of P (2.5, 5, 10, 20, 30, 40 and 50 ppm) as KH</span><sub><span style="vertical-align:sub;">2</span></sub><span>PO</span><sub><span style="vertical-align:sub;">4</span></sub><span>. The setup was incubated under laboratory conditions and soil samples were repeatedly taken at 10 days (after 4 days of urea incubation plus 6 days of P application). The P sorption data were fitted to Langmuir model. </span><b><span>Results: </span></b><span>The pot experiment revealed an abrupt drop in the concentrations of exchangeable Al</span><sup><span style="vertical-align:super;">3+</span></sup><span> and H</span><sup><span style="vertical-align:super;">+</span></sup><span> ions (p</span><span> </span><span><</span><span> </span><span>0.05) within the first 6 days after urea application, accompanied by a positive surge in the concentration of NH<sub>4</sub><sup style="margin-left:-9px;">+</sup> </span><span>ions. This phase (6 days) was followed by a rise in the levels of exchangeable Al</span><sup><span style="vertical-align:super;">3+</span></sup><span>, H</span><sup><span style="vertical-align:super;">+</span></sup><span> and NO<sub>3</sub><sup style="margin-left:-9px;">-</sup> </span><span>ion concentration, which was inversely mirrored by a drop in the concentration </span><span>of NH<sub>4</sub><sup style="margin-left:-9px;">+</sup> </span><span>ions. Consequently, the patterns displayed by the soil reactions </span><span>were delineated into four phases, with Phase 1 (6 days) being characterised by urea hydrolysis reactions of deamination and ammonification, Phase 2 (10 days) being</span><span> </span><span>dominated by nitrification and its acidifying properties, Phase 3 being a repeat of Phase 1, both occurring immediately after urea application (within 6 days);and Phase 4 being a repeat of Phase 2. As for the P-sorption study, the effects of urea hydrolysis in a Ferralsol markedly increased soil pH and surprisingly P sorption. The contradictory P sorption behavior, despite the drop in exchange acidity was attributed to presence of divalent calcium in the extraction reagent used. </span><b><span>Conclusion:</span></b><span> The short term insights obtained in response to urea N application in the Ferralsol, are eye openers to future use of N fertilisers as well as strategic management of the associated acidification process which is often more costly and complicated to manage.</span> </p>