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Estimation of Soil Erosion Deforestation-induced Using Nuclear Techniques (Ca...ExternalEvents
Mr. Mohammadreza Gharibreza, Soil Conservation and
Watershed Management Research Institute, Iran. Global Symposium on Soil Erosion (GSER19), 15 - 17 May 2019 at FAO HQ.
Estimation of Soil Erosion Deforestation-induced Using Nuclear Techniques (Ca...ExternalEvents
Mr. Mohammadreza Gharibreza, Soil Conservation and
Watershed Management Research Institute, Iran. Global Symposium on Soil Erosion (GSER19), 15 - 17 May 2019 at FAO HQ.
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Estimation of Soil Erosion Deforestation-induced Using Nuclear Techniques (Ca...ExternalEvents
Mr. Mohammadreza Gharibreza, Soil Conservation and
Watershed Management Research Institute, Iran. Global Symposium on Soil Erosion (GSER19), 15 - 17 May 2019 at FAO HQ.
Estimation of Soil Erosion Deforestation-induced Using Nuclear Techniques (Ca...ExternalEvents
Mr. Mohammadreza Gharibreza, Soil Conservation and
Watershed Management Research Institute, Iran. Global Symposium on Soil Erosion (GSER19), 15 - 17 May 2019 at FAO HQ.
Soil suitability is the fitness of given type of land for defined use.
soil suitability analysis is a method of land evaluation, which measures the degree of appropriateness of land for a certain use.
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Item 3: Current initiatives, new proposals and next steps of 5 pillars of action
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Item 3: Current initiatives, new proposals and next steps of 5 pillars of action
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Estimation of Soil Erosion Deforestation-induced Using Nuclear Techniques (Case study: Golestan Province, Iran)
1. Estimation of Soil Erosion Deforestation-
induced Using Nuclear Techniques (Case
study: Golestan Province, Iran)
Mohammadreza Gharibreza
Soil Conservation and Watershed Management
Research Institute, Iran (SCWMRI)
1
2. Content
• Hyrcanian Forests
• Gorgan Province Deforestation and Afforestation
• Technical Cooperation between IAEA and SCWMRI
• Site Selection
• Sampling and Sample Preparation
• Cs-137 inventory
• Soil Erosion rate
• Conclusion
2
3. Hyrcanian Forests
• A continuous 800+km belt of deciduous forests
• Along the northern slopes of the Alborz mountains,
including 1.85 million hectares in Iran.
• Including an important refugium of temperate broad-leaved
trees, and date back to at least 25 million years BP.
• They stretch across three provinces of Iran (Gilan,
Mazandaran and Golestan)
• Up to 60 mammal species plus 340 bird, 67 fish, 29 reptile
and 9 amphibian species recorded in various habitats of the
region.
3
6. Gorgan Province Deforestation and Afforestation
• Up to 452,000 ha forest coverage, from which 66%
productive, 18 % conserved, and 16 % degraded.
• Golestan National Park with 91,000 ha distribution
• Deforestation has been happened through wood
harvesting with the mean rate of 2.3 million m-3
per year between 1976 and 1991 years. Afterward,
this rate was decreased to 300,000 m-3 per year.
• Up to 75,527 ha Afforestation has been conducted
since 1981.
• Converting of forest to Dry-land farming is most
common land use change by farmers.
6
10. Technical Cooperation between IAEA and SCWMRI
10
Project Number: IRA5013
Project Title:
Investigating the Effects of Deforestation and
Afforestation on Soil Redistribution in the North
of Iran
Country: Iran, Islamic Republic of
Main Counterpart: Mohammadreza GHARIBREZA
Counterpart Institution:
Soil Conservation and Watershed Management
Research Institute (SCWMRI)
Technical Officer: Mohammad ZAMAN
Program Manager Officer
Name:
M. B. MISHAR
17. 17
Code Sand % Silt % Clay % Texture
290 3 54 43 Si - C
291 15 55 30 Si - C - L
292 11 55 34 Si - C - L
293 5 61 34 Si - C - L
294 6 57 37 Si - C - L
295 6 56 38 Si - C - L
296 0 60 40 Si - C
297 0 61 39 Si - C - L
298 1 58 41 Si - C
299 9 60 31 Si - C - L
300 9 62 29 Si - C - L
301 13 56 31 Si - C - L
302 2 62 36 Si - C - L
303 2 73 25 Si - L
304 2 60 38 Si - C - L
305 1 61 38 Si - C - L
306 7 60 33 Si - C - L
307 3 60 37 Si - C - L
308 1 68 31 Si - C - L
309 1 58 41 Si - C
310 1 58 41 Si - C
311 1 57 42 Si - C
312 1 60 39 Si - C - L
313 12 59 28 Si - C - L
Code Sand % Silt % Clay % Texture
269 7 60 33 Si - C - L
270 8 60 32 Si - C - L
271 11 60 29 Si - C - L
272 8 59 33 Si - C - L
273 6 63 31 Si - C - L
274 9 57 34 Si - C - L
275 13 54 33 Si - C - L
276 8 62 30 Si - C - L
277 9 57 34 Si - C - L
278 9 57 34 Si - C - L
279 5 60 35 Si - C - L
280 8 56 36 Si - C - L
281 2 65 33 Si - C - L
282 2 63 35 Si - C - L
283 1 62 37 Si - C - L
284 1 64 35 Si - C - L
285 2 68 30 Si - C - L
286 2 60 38 Si - C - L
287 1 63 36 Si - C - L
288 1 62 37 Si - C - L
289 4 62 34 Si - C - L
Code Sand % Silt % Clay % Texture
365 10 63 27 Si - L
366 9 61 30 Si - C - L
367 10 59 31 Si - C - L
368 6 61 33 Si - C - L
369 4 58 38 Si - C - L
370 2 64 34 Si - C - L
371 1 63 36 Si - C - L
372 3 63 34 Si - C - L
373 16 53 31 Si - C - L
374 6 61 33 Si - C - L
375 2 59 39 Si - C - L
376 1 58 41 Si - C
377 2 59 39 Si - C - L
378 0 60 40 Si - C
379 1 59 40 Si - C
380 2 64 34 Si - C - L
381 6 63 31 Si - C - L
382 9 62 29 Si - C - L
383 7 62 31 Si - C - L
384 1 61 38 Si - C - L
Eastward Direction, Azad Shahr Westward Direction, Azad Shahr Northward Direction, Galilesh
RESULTS
Silty clay loam is the dominant soil texture along the studied transects which are
characterized by loess deposits in the North-East of Iran.
18. 18
RESULTS
y = 145.35e-0.451x
R² = 0.8801
0 5 10 15 20 25 30 35 40
0-2
2-4
4-6
6-8
8-10
10-12
12-14
14-16
16-18
18-20
20-22
22-26
26-30
Cs-137 Activity (Bq/kg)
Cs-137 Inventory and grain size distribution in Reference site of Azad Shahr area
26. 26
Loss soil based on reduction of Cs-137 inventory along the Azadshahr
transects are 64.24 % and 60.24 %, respectively.
The mean bulk density of 1400 kg m-2, the tillage depth of 250 kg m-2
the results indicated that ca. 153.1 kg m-2 (or ca. 10.93 cm) and ca.
150.0 kg m-2 (or ca. 10.71 cm) of soil has been eroded from the AZ-
westward and AZ-Eastward transects, respectively.
Erosion values estimated based on Mass Balance II model and 54
years the elapsed time between dates of deforestation and sampling
operation.
The annual net erosion of the Dryland Farms (Westward and Eastward)
transects were calculated to be 34.87 tone ha-1 and 35.86 tone ha-1,
respectively.
Therefore, the soil loss along the representative transects have been
occurred with the rate of 0.20 cm y-1, 0.19 cm y-1 respectively.
27. 27
Loss soil based on reduction of Cs-137 inventory along the Azadshahr
transect is 60.59 %.
The mean bulk density of 1430 kg m-2, the tillage depth of 250 kg m-2
the results indicated that ca. 151.47 kg m-2 (or ca. 10.59 cm) of soil
has been eroded from the Galikesh transect.
Erosion values estimated based on Mass Balance II model and 54
years the elapsed time between dates of deforestation and sampling
operation.
The annual rate of soil erosion in Galikesh area (Dryland Farm) was
calculated to be 29.19 tone ha-1.
Therefore, the soil loss across the representative transect has been
happened with the rate of 0.19 cm y-1.
28. 28
CONCLUSION
Clear cutting of forests to develop dryland farming has been the worst
kind of land use change in terms of soil erosion.
Using the FRNs techniques indicated that rate of soil erosion in farms
with tillage along the slope direction is 1.7 higher than farms with
tillage parallel to contour lines.
Erosion condition controlled mainly by loess mother material.
Slope direction does not play important role in rate of soil erosion in the
study area.
Reduction of ≈ 20 % of precipitation has resulted in declining of 17.5%
rate of soil erosion.
The annual rate of soil erosion rate (32.27 t ha-1) in Golestan Province
is two times of the national rate of soil erosion (16.7 t ha-1).