variations in nitrogen mineralization from water hyacinth (eichhornia crassipes) on salt-affected...
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Nitrogen mineralization in salt affected soilTRANSCRIPT
Variations in Nitrogen Mineralization from Water Hyacinth (Eichhornia crassipes) on Salt-Affected Soils
E. A. Elhadi, F.A.M. Rezig.. A. R. Mubarak
Introduction Salinity Land degradation crop
production . Saline soil soluble salt N and OM Reclamation suggested through research 7- day irrigation interval, 80 kg/ha of urea
N, a basal phosphorus dose and organic amendments (Chicken manure, Water hyacinth and farm yard manure )
MineralizationOrganic N NH4 Or NO3 Immobilization
Mineral Nitrogen
Plant uptake
Understanding the rate of N mineralization from organic amendments is important to develop practical recommendations on the rate and time of application; so that the N releases could meet the crop needs.
Objective
Examine the effect of different salinity levels on nitrogen mineralization from water hyacinth.
Treatments A factorial combination of three salinity
levels (0, 500, 1000 mg L-1 NaCl ; S0, S1 and S2) and two levels of Water Hyacinth (0 and 150 mg N kg-1 soil ; W0 and W1) with three replications .
This will give us the fallowing combination
1-S0W0; 2- S0W1 ; 3-S1W0 ; 4- S1W1; 5- S2W0 ; 6- S2W1
Incubation experiment: leaching and aerobic incubation technique glass cups d 5.5 cm
300 g sand soil 70% WHC
10 day pre incubationSoil moisture was kept constant at 70% WHC
W0, 2.6 g W1, +3 level salinity
At each sampling from incubation, 2, 4, 6, 8, 10, 12, 14 and 16 weeks; two sub-samples 10 g each were taken from each treatment. One for MC and other for NH4
+ -N + NO3—N
determination
Total mineral N (TMN) in each week= NH4+ -N + NO3
- -NNet N mineralization /immobilization = TMN in each treatment- the control.
The cups were covered gas permeable Parafilm wax
S0W0S1W0S2W0S0W1S1W1S2W1
NH4-N
2 4 6 8 10 12 14 16 180
10
20
30
40
50
60
70
80S0W0
S0W1
S1W0
S1W1
S2W0
S2W1
Incubation time (weeks)
NH
4-N
g/k
g so
il
75.9
11.2
W0IM
Nitrate
S2 W1> S1W0S0W0< S1W1<S2W1
Nitrate was the dominant form of mineral N throughout the incubation period
2 4 6 8 10 12 14 16 180
10
20
30
40
50
60
70
80
90
100 S0W0
S0W1
S1W0
S1W1
S2W0
S2W1
Incubation time (weeks)
NO
3-N
mg/
kg s
oil
W0IM
88.6
15.9
Total mineral nitrogen (TMN)
2 4 6 8 10 12 14 16 180
20
40
60
80
100
120
140
160
180 S0W0
S0W1
S1W0
S1W1
S2W0
S2W1
Incubation time (weeks)
TMN
mg/
kg s
oil
164.5
27. 0
Net Nitrogen Mineralization
2 4 6 8 10 12 14 16 18
-80
-60
-40
-20
0
20
40 S0W0
S0W1
S1W0
S1W1
S2W0
S2W1
Incubation time (weeks)
Net
N M
iner
aliz
atio
n m
g/kg
Immobilization
Mineralization
Limitation Only three levels of salinity is used in
this study NaCl is easy choice but not typical
soil solution. Other treatments should be test It is laboratory experiment
verification in the field is needed
Conclusions Net N released from water hyacinth
was negatively correlated with salinity levels; the results also showed that NO3
-N was the dominant form of mineral N in all weeks during the study period. This is study reflects the adverse effects of soil salinity on soil microbiological processes (mineralization).