Conversion of cropland to forests: How environmental benefit lead to food security-evidence of China
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Transcript of Conversion of cropland to forests: How environmental benefit lead to food security-evidence of China
Conversion of Cropland to Forests: how environmental benefit lead to
food security--evidence of China
XIE Chen
FEDRC, SFA, China
Forest Asia Summit, Jakarta, 5-6 May
Outline
• Conversion of Cropland to Forests Program
• CCFP policy related to food security
• CCFP monitoring system by FEDRC
• Direct impact of CCFP on grain production
• Indirect impact of CCFP on grain production
• Discussion and future direction
CCFP policy
• Over 32 million rural households involved.
• Up to 2013 more than US$42 billion invested.
• 27.55 million ha of land converted/afforested.
• 9.06 million ha of cropland enrolled.
• 15.80 million ha of barren/waste land enrolled.
• 2.68 million ha sealed off to allow natural regeneration (a.k.a. “closed mountain” afforestation)
• Currently one of the most wide-spread programs in rural China.
CCFP policy regarding grain security
• From forbidden intercropping to allow it;
• Allow economic tree plantation which mainly provide fruits, and other edible non-timber forest products;
• basic cropland construction and crop production has been part of program task since 2008
CCFP monitoring system
• Since 2003, annual based and 300 personal network around China;
• 100 counties from 21 provinces considering CCFP tasks, geo-location and socio-economic conditions
• 120 villages from 100 counties
• 1165 farmers households from 120 villages
Indicators
• County: socio-economic condition, CCFP investment, program implementation, forest resources and main outputs;
• Village: land use change, main price of A&F products, geo-features;
• Households: population & labor migration, land use, input and output of family productions, CCFP subsidy, households consumption
Direct impact of CCFP on Grain production
• Increase supply of fruits, edible non-timber forests via economic tree on CCFP land;
• Reduced cropland and reduced grain volume at household level;
Change of grain area and grain output volume of CCFP 100 monitoring counties
Grain area increase 9.48%
Grain volume increase 24.12%
Change of cropland and forestland of sample farmer
households
18.52
10.89
8.409.26
8.34 8.85 9.53 9.25 9.85 9.59 10.05
3.48
10.93
13.86
16.51 16.8018.04 18.69
19.69
23.1124.25
26.58
0
5
10
15
20
25
30
1998 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011
mu/household
cropland forestland
Change of CCFP HH’ grain output volume
Total grain -9.28%
corn 12.01%
Wheat -30.52%
rice -10.87%
Root crop -24.15%
0
200000
400000
600000
800000
1000000
1200000
1998 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012
Total fruits volume CCFP fruits volume
30%
Contribution of CCFP to monitoring HH’ fruit output
0
2000
4000
6000
8000
10000
12000
14000
16000
18000
20000
2009 2010 2011 2012
total tea-seed oil ccfp tea-seed oil
Tea seed oil production of CCFP monitoring HH
Indirect impact
• Intensification of crop production;
• per unit area yield of grain has increasing;
• Increase of grain output larger than grain production area;
• Decline of natural disaster on crop
Dependent Variable: GRAIN_OUTPUTMethod: Panel Least SquaresDate: 04/27/14 Time: 16:18Sample (adjusted): 1999 2012Cross-sections included: 98Total panel (unbalanced) observations: 817
Variable Coefficient Std. Error t-Statistic Prob.C 88488.06 10713.90 8.259183 0.0000
PAREAGRAIN 35.18393 8.094751 4.346512 0.0000GRAINSUB 13.54254 0.846971 15.98937 0.0000IRRIAREA 2.238077 0.256190 8.735989 0.0000
FERTILIZER 2650.104 1195.543 2.216653 0.0270DISASTER -0.008897 0.029147 -0.305263 0.7603
PER_CROPLAND -1326.416 2299.700 -0.576778 0.5643CCFPAREA 1.762699 0.883512 1.995105 0.0464PINCOME 6.260976 2.809942 2.228151 0.0262
R-squared 0.972839 Mean dependent var 192180.4Adjusted R-squared 0.968247 S.D. dependent var 242609.3S.E. of regression 43231.49 Akaike info criterion 24.32042Sum squared resid 1.30E+12 Schwarz criterion 25.00581Log likelihood -9815.890 F-statistic 211.8670Durbin-Watson stat 1.022551 Prob(F-statistic) 0.000000
G0G1
T1
T0
F1
F2
F3
PPF0 PPF1
Cropland
Fore
st land
Theory of environmental supply of CCFP and it relation with agricultural production
1. CCFP is China’s massive efforts to reverse it’s thousand of years’ over exploring forestland and deforestation, rebalancing agriculture and forestry;
2. In its policy design, livelihood has always been fundamental concern, grain production has become part of CCFP policy in phase II;
3. CCFP increase rural poor’s food security by providing stable subsidy which guarantee their basic needs;
16%Low income participants
‘The subsidy might be little to farmers who have heavy burden to support college students or care patient, but for that poor grandmother, it is almost all income for her year round’.
a survey student of Beijing Forestry University
4. CCFP encourage economic trees and intercropping which significantly increase’s farmers fruits and related foods directly;
Ecological trees
Economic trees
Both
9.52%
22.66%
63.49%
• 5. CCFP demonstrate that a developing country could balance it’s agricultural and forestry land use when it fully recognize importance of environmental conservation to rural development and using government finance to compensate its past environmental loss from its economic development gains;
6. Considerable research is needed to exploring the environmental benefit of re/afforesation, forest conservation to grain production and food security;
7. Relationship between forest environment and grain production at small holder and plot level should have considerable potential to explore from primary results of FEDRC-CIFRO ongoing project.