Electronic Journal of Polish Agricultural Universities (EJPAU) founded by all Polish Agriculture Universities presents original papers and review articles relevant to all aspects of agricultural sciences. It is target for persons working both in science and industry,regulatory agencies or teaching in agricultural sector. Covered by IFIS Publishing (Food Science and Technology Abstracts), ELSEVIER Science - Food Science and Technology Program, CAS USA (Chemical Abstracts), CABI Publishing UK and ALPSP (Association of Learned and Professional Society Publisher - full membership). Presented in the Master List of Thomson ISI.
2015
Volume 18
Issue 1
Topic:
Economics
ELECTRONIC
JOURNAL OF
POLISH
AGRICULTURAL
UNIVERSITIES
Ko這szycz E. , Wilczy雟ki A. 2015. VARIABILITY OF FARM INCOME IN PLANT PRODUCTION FARMS IN THE PERSPECTIVE OF COMMON AGRICULTURE POLICY REFORM, EJPAU 18(1), #07.
Available Online: http://www.ejpau.media.pl/volume18/issue1/art-07.html

VARIABILITY OF FARM INCOME IN PLANT PRODUCTION FARMS IN THE PERSPECTIVE OF COMMON AGRICULTURE POLICY REFORM

Ewa Ko這szycz, Artur Wilczy雟ki
Department of Management, Faculty of Economics, West Pomeranian University of Technology Szczecin, Poland

 

ABSTRACT

The research was concerned with assessment of the level of income from family farms specialized in arable crops in the years 2014–2020. The analysis assumed a stochastic nature of yields of chosen crops and their prices on the basis of historic data. Using data and measures of the Polish FADN, five models of farms were created and simulations were carried out addressing also the problem of the influence of implementation of agricultural practices beneficial for the climate and the environment on the economic situation of farms. The obtained results indicate that nominal income from the family farm in the majority of farms will remain at the level similar to the income in the year 2014. Agricultural practices beneficial for the climate and the environment, as the new instrument of Common Agricultural Policy, may influence both the structure of crops and the economic situation only in the case of farms of the biggest acreage.

 

Key words: risk, variability of yields, variability of prices of agricultural products, greening.

INTRODUCTION

Making predictions about the future is a complex process. Typically, it consists in gathering and analyzing historic data on a chosen system and then extrapolating the observed regularities to the future. In this manner it is possible to research reactions of a system to changes in its structure and/or its environment. The process becomes more complicated with the increase of instability and complexity of the environment. These problems are also present in preparing forecasts about production-economic situation of farms. As an established knowledge says, agricultural production has a certain specificity resulting from its specific features, both primary and secondary [24]. This specificity gives rise to the risk that – at a distance of years – any decision taken in the farm may prove wrong.

In the process of making predictions about the future, quantitative methods are widely used, mainly of mathematical-statistical nature, including those based on the statistic-economic models. Employment of the deterministic and stochastic computer simulation methods becomes increasingly common. In deterministic simulations a small number of combinations of variables with probabilities a priori is admitted. Experimental results obtained in this manner give fragmentary or rather pointwise reflection of possible effects in the researched system, e.g. a farm. For that reason stochastic simulation methods using random or pseudorandom number generation are employed. In the particularly popular Monte Carlo method it is assumed that chosen input data are of random nature and generate a certain scope of achievable results. These methods allow simultaneous analysis of the influence of many random variables on the obtained results.

Forecasts based on stochastic models are widely used in agriculture. Such models are employed mainly to research impact of changes in farm risk management strategies on the incomes gained [2, 7], and to analyze factors influencing the level of economic results achieved by farms [3, 4, 6, 8, 17, 18, 20]. Analyses covered different types of farms and a considerable share of research concerned plant production, where random factors (and climatic factors in particular) significantly influence the production-economic results. Such studies are carried out especially in periods of market changes, mainly due to desire to explore of the impact of applying new mechanisms affecting the economic situation of farms. The reform of the Common Agricultural Policy creates the need to assess its impact on the farms. The future agricultural policy should be based on three objectives: viable food production (income support and safety net mechanisms for producers), sustainable management of natural resources and climate action (improved the integration of environmental requirements) and balanced territorial development (support for rural development across the EU) [12]. The principal instruments used in the new-CAP are affected by economic, environmental and territorial factors [1, 10, 15, 23]. From 2015 onwards, the CAP introduces new policy instrument in Pillar 1, the Green Direct Payment (greening). This payments will be linked to the respect of three obligatory agricultural practices, namely maintenance of permanent grassland, ecological focus areas and crop diversification [19]. The existing literature provides only limited information on the impact of greening on farm income. Although a few studies have examined link between new-CAP instruments and profitability [9, 22, 26, 27], little empirical evidence exists to inform about details of the economic situation of different types of farms. Similar attempts have been made for arable farms in Italy [11, 26] and Germany [14]. The results of these studies indicate the negative greening effect – decreasing gross profit margin according to the farms organization, their specialization and location, with stronger impacts for the intensively operating farms.

For these reasons it was decided in this research to analyze the influence of variability of yields and prices of produced crops on economic results of plant production farms, taking account of changes of the Common Agricultural Policy regulations in the years 2014–2015. The objective of the research was to determine the risk of not gaining any income from family plant production farms of different production size in the years 2014–2020.

SAMPLE AND METHOD

With the objective of determining distribution of values of income from the family farm the Monte Carlo simulation method was used. This method has its specific procedure, which was carried out in this research in four basic stages:

  1. Creating a model of farm. In this research the TIPI-CAL model was employed. TIPI-CAL (Technology Impact and Policy Impact Calculation) is a multi-period recursive model allowing deterministic and/or stochastic simulations of changes in farms [16]. Five models of farms were created with the use of data and measures from farms participating in the Polish FADN in the year 2011 as published by the IERiGŻ (Institute of Agricultural and Food Economics) [13]. Each model of farm reflected the production-economic capacity of a group of farms specialized in arable crops, separated according to the farmland area size categories used in the FADN (Tab. 1). Data and measures of model farms from the year 2011 were the starting point for further analyses. Basing on these data and measures for each model farm there was established, inter alia, the structure of crops and the value and structure of capital. It was assumed that investments in fixed assets (not including farmland) will be only simple replacement investments allowing continuation of farming without changes in production technology. Value and costs of production after the year 2011 were determined on the grounds of price indices of individual products and inputs (calculated in relation to the level from the preceding year) using to this end statistical data published by the GUS (Polish Statistical Office) and forecasts of the World Bank [28] and OECD-FAO [21]. Designed models farms have some limitations. Firstly, the model fails to optimize production. The structure of resources and the production volume does not change in the model throughout the period of analysis. The model used a nominal values, not taking into account the inflation. Another limitation is that due to the limited availability of historical data from farms in the model used in part of projections historic data from the general statistics.
  2. Defining random variables in the model and their distributions. In this research it was assumed that among many variables shaping economic results of plant production farms yields of crops and their prices are of random nature. These are variables which cannot be influenced by a farmer or an influence of a farmer on these variables is very limited. Both variables often occur in research concerning income risk in farms [2, 3, 5–7, 17]. Analysis covered yields and prices of basic farm crops: wheat, rye, barley, oats, rapeseed, sugar beets and potatoes. With the objective of determining parameters of distributions of yields and prices data from the GUS on average historic yields in voivodships in the years 1999–2012 were used. In the case of crops’ yields normal distribution was used assuming that a yield cannot be lower than zero. In the case of prices there was used triangular distribution characterized by three parameters: the minimum value, the maximum value and the most probable value, i.e. the modal value. The minimum value was assumed to be the chosen crop’s lowest price observed in all voivodships in the years 2005–2012 and the maximum value – the highest price from the same set of data. The most probable value in the years 2014–2020 was established on the grounds of forecasts of the World Bank [28] and OECD-FAO [21] for particular years with the use of chain indices, thus preserving the differences in prices obtained by each of the model farms. On the grounds of data from the GUS there was also determined the correlation between yields and prices of crops using to this end Pearson linear correlation coefficients. Correlation coefficients were of deterministic nature throughout the analyzed period.
  3. Carrying out simulations. @Risk 6.0 software was used for simulations. For each model farm ten thousands iterations were made, which allowed to determine precisely the distribution of probability of income from each of the analyzed family farms for each year from the period 2014–2020.
  4. Determining the distribution of probability of income from the family farm and interpretation. To present and compare the obtained results box plots were used containing information on the location, dispersion and shape of the distribution of income from family the farm.

The research made it also possible to assess the impact of changes of requirements for the farms applying for subsidies to operational activity taking effect from the year 2015. According to the adopted new regulations of the Common Agricultural Policy, besides meeting cross-compliance requirements, farmers will be also required to undertake agricultural practices beneficial for the climate and the environment (referred to as ‘greening’). The relevant scenario was created to assess the influence of this regulation on economic results of farms. Analysis of farmland structure of farms as to meeting the said requirements was conducted and if a farm was not meeting the requirements, then setting aside was assumed in the required acreage. In addition, it was assumed that after the year 2017 the European Commission would increase the required share of ecological focus areas in farms from 5% in the year 2015 to 7% in the year 2018.

Table 1. Parameters of model farms in the year 2011
Parameter
Unit
Model farms specialized in arable crops
by the area of farmland
M-8
M-15
M-25
M-40
M-116
Area of farmland
[ha]
8.46
15.33
24.85
39.88
115.91
Share of arable land in total farmland
[%]
94.79
94.15
95.49
96.3
97.13
Share of area on lease
in the total land of the farm
[%]
10.6
16.4
22.5
26.5
41.1
Sowing area:
Cereals
Oilseeds
Root crops
Other
[ha]
[% of sowing area]
[% of sowing area]
[% of sowing area]
[% of sowing area]
7.86
47.6
8.8
18.7
24.9
14.25
57.7
10.8
13.1
18.4
23.51
62.3
13.7
9.5
14.6
37.96
62.5
16.5
7.6
13.5
111.56
60.7
19.5
5.2
14.7
Capital of the farm
[PLN K·ha F-1]
20.25
16.33
13.88
11.68
9.17
Share of equity in total capital
[%]
97%
94%
90%
85%
74%
Liabilities of the farm
[PLN K·ha F-1]
694.3
1051.1
1420.8
1760.8
2369.7
Work input. total
[hr·ha F-1]
406.0
243.392
149.296
98.345
40.421
Share of work input from outside the farm
in total work input
[%]
13.3
21.4
19.9
17.8
32.33
Share of value of plant production
in total production
[%]
98
90
88
87
91
Share of payments in farm income
[%]
54
47
49
52
49
PLN K·ha F-1 – thousand of Polish zlotys per hectare of farmland, hr·ha F-1 – hours per hectare of farmland
Source: authors’ own elaboration based on FADN data

RESEARCH RESULTS

Simulations encompassed the determination of future shape of the distribution of probability of income from the family farm in two scenarios of activity of the model plant production farms. The first scenario was the reference scenario, which did not assume undertaking agricultural practices beneficial for the climate and the environment and which was the baseline for the other scenario. The second scenario assumed meeting by the farms all the Common Agricultural Policy requirements adopted for the years 2014–2020, which demand, beginning with the year 2015, providing the ecological focus area in farms of the area of more than 15 hectares of arable land. Such an approach allowed to indicate the expected profitability differences resulting from the introduction of the new Common Agricultural Policy mechanisms determining considerably operation of plant production farms. Detailed statistics presented results are given in Appendix A.

Fig. 1. Distribution of probability of income from family farm in the model farm M-8
Source: authors’ own elaboration

Fig. 2. Distribution of probability of income from family farm in the model farm M-15
Source: authors’ own elaboration

Results obtained for model farms M-8 and M-15 do not include the scenario requiring creation of the ecological focus area because the area of arable land in these farms does not exceed 15 hectares (Fig. 1, 2). In the case of the smallest farm in terms of the area of arable land (M-8) it can be observed, that the expected value, determined with the mean value of the possible results obtained for the distribution of probability, is continuously on the decrease. In the year 2014 the mean value for the distribution of income from the family farm was around PLN 14 K and in the year 2020 the expected value decreased to the level close to PLN 1.5 K.

Results of the research obtained for the M-8 farm demonstrate also that, beginning with the year 2018, 50% of observations include the results, where there exists a probability of gaining negative income from the family farm. In the first year of the analysis the interquartile range (H-spread) of the researched income was always above zero but in the year 2020 around 40% of the obtained results of simulations were in the area below zero.

The distribution of probability of future income in the farm M-15 indicates that between the years 2015 and 2020 the income can be expected to be stable despite of the risk related to fluctuations of yields of crops and sale prices of crops (Fig. 2). In the case of the farm M-15, the area of which is nearly two times bigger than the area of the farm M-8, results remaining between first and third quartile indicate positive values of income from the family farm. Examination of the dispersion of distribution of profitability in the two above analyzed farms allows to observe that in the case of the farm with smaller area of arable land such dispersion is clearly lower.

According to the rules of the Common Agricultural Policy the model farm M-25 will have to maintain a share of its arable land as the ecological focus area. Such situation will arise as from the year 2018, when the decision, if any, as to the increase of such an area from 5% to of 7% will be taken.

From the distribution of probability of income from the family farm for the farm M-25 it follows that its expected value in the scenario including the agricultural practices beneficial for the climate and the environment will be characterized by nearly identical levels throughout the years 2015–2020 (Fig. 4). It should be also observed that in the situation where in the analyzed farm a share of land will be set aside for the ecological focus area the expected income will be lower in comparison to the reference scenario (Fig. 3, 4). For the expected value the difference will be very small and it will be around PLN 1.5 K.

Fig. 3. Distribution of probability of income from family farm in the model farm M-25 – reference scenario
Source: authors’ own elaboration

Fig. 4. Distribution of probability of income from family farm in the model farm M-25 – scenario including the greening
Source: authors’ own elaboration

Comparing the dispersion of the results obtained for the farm M-25 with the results for the farms M-8 and M-15 it can be indicated that the diversity of the values obtained in the simulations is bigger in the case of the farm M-25. It means that this farm is much more susceptible to changes of the income driven by fluctuations of the individual risk factors, which in this case are yields and procurement prices of crop products.

Fig. 5. Distribution of probability of income from family farm in the model farm M-40.
Source: authors’ own elaboration

Fig. 6. Distribution of probability of income from family farm in the model farm M-40 – scenario including the greening
Source: authors’ own elaboration

Just as in the case of results obtained for the farm M-25 setting aside a share of land for the ecological focus area by the farms M-40 and M-116 and the increase, if any, of this share beginning with the year 2018 will influence the decrease of the expected value of income from the family farm (Fig. 5–8). The difference between the mean value for the distribution of income between the researched scenarios will amount to around PLN 2 Kin the case of the farm M-40 and in the case of the farm M-116 it will reach the amount of PLN 10 K. An analysis of distribution of probability of future profitability in farms M-40 and M-116 allows to indicate that variability of yields and prices of crop products and introduction of the new rules of the Common Agricultural Policy will influence the deterioration of profitability in these farms. In the year 2014 the value of the expected income is higher than in the next years of operation of these farms.

Fig. 7. Distribution of probability of income from family farm in the model farm M-116
Source: authors’ own elaboration

Fig. 8. Distribution of probability of income from family farm in the model farm M-116 – scenario including the greening
Source: authors’ own elaboration

As it was observed above production size influences the dispersion of results of the conducted simulations concerning the probability of future shape of profitability in the researched farms. In the distribution obtained for the model farm M-40 the interquartile range in the years 2014–2020 remains within the limits from PLN 28 K to PLN 36 K and in the farm of more than three times bigger acreage of arable land it ranges from PLN 98 K to PLN 112 K..

CONCLUSIONS

Future shape of the Common Agricultural Policy introducing new rules governing agricultural markets and making farm support conditional on meeting additional requirements will significantly determine future economic situation of farms. Agricultural practices beneficial for the climate and the environment will be invested with special importance. Results of this research indicate that the requirement of crop diversification will be of little importance for Polish farms. Basic premises for this state of affairs are the present structure of crops and the legislation treating spring and winter crops of the same species as separate types of crops. Analysis of mechanism related to maintaining the ecological focus area (EFA) in farms indicates that strength of this mechanism’s influence on future profitability should not be significant either. The number of elements counted as ecological focus areas should also facilitate meeting this requirement. In the biggest of the researched farms, which works around 115 hectares of arable land, the increase of the ecological focus area to 7% in 2018 would mean the additional 3 hectares of land allotted for the area.

The research on future distribution of probability of income from the family farm demonstrated that only in the model farm of less than 10 hectares of arable land the constant decrease of profitability may be expected in the researched period. The expected value in the year 2020 will be close to zero and the obtained simulation results remaining within first quartile indicate the loss on farming. It could be presumed that in the future such farms might be eliminated from the market as they will be unable to make necessary investments allowing for development of production.

In the case of other farms the distribution of probability of income from the family farm indicates similar levels of the income in the years 2015–2020. The results show that the implementation of practices related to greening will not increase the dispersion of income in farms.  However, such situation cannot be considered advantageous. The forecasts of changes of yields and procurement prices of crop products combined with the instruments of the Common Agricultural Policy provide the stabilization of profitability of the nominal nature only. Adjusting the results by inflation would produce lower values of the income. Results of simulations indicate also that in the year 2020 it could be expected that income from the family farm would be close to the level from the year 2014 with lower values of the income in the years 2015–2019.

APPENDIX A

Table A.1. Summary statistics in the reference scenario for farm M-8
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-9440
-10904
-14811
-16454
-19341
-24056
-30609
Maximum
50997
37777
36830
40994
38665
40490
38161
Mean
14308
9640
8463
6965
5687
3927
1598
Std Dev
9577
8261
8305
8664
8942
9446
9948
Variance
91718644
68238269
68973768
75071018
79951989
89223129
98956629
Skewness
0.4491
0.2888
0.2860
0.2911
0.2513
0.2459
0.2756
Kurtosis
2.8694
2.7146
2.7318
2.8178
2.7900
2.8433
2.8979
Median
13226
9184
7949
6402
5177
3522
1107
Mode
11513
10850
6970
4981
6518
1968
-79
Source: authors’ own elaboration

Table A.2. Summary statistics in the reference scenario for farm M-15
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-15584
-15704
-15961
-19705
-19714
-25626
-29089
Maximum
73923
65025
64249
62207
58442
60580
63194
Mean
20321
16025
15687
15611
15707
15355
14839
Std Dev
13877
12375
12035
12174
12424
12722
13010
Variance
192582672
153134367
144831347
148199536
154367670
161852575
169260301
Skewness
0.4263
0.3206
0.2667
0.2635
0.1858
0.1492
0.0920
Kurtosis
2.9338
2.7429
2.7662
2.8096
2.7310
2.7779
2.7961
Median
18969
15213
15047
15040
15221
15172
14770
Mode
17201
19140
8569
11398
12110
18618
15254
Source: authors’ own elaboration

Table A.3. Summary statistics in the reference scenario for farm M-2
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-24715
-22948
-21290
-19661
-20836
-22535
-22585
Maximum
95894
87745
93402
88782
88450
89907
99187
Mean
28179
24999
24650
24870
25459
26116
26751
Std Dev
18337
17009
16906
16875
17064
17148
17191
Variance
336262257
289292865
285814648
284770205
291177241
294038122
295519014
Skewness
0.2546
0.1864
0.1893
0.1574
0.1523
0.1025
0.0859
Kurtosis
2.8724
2.6203
2.7600
2.7049
2.7176
2.6975
2.6743
Median
27328
24411
24188
24518
25216
26082
26574
Mode
20359
20285
25634
27353
29723
26260
26376
Source: authors’ own elaboration

Table A.4. Summary statistics in the scenario including greening for farm M-25
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-26174
-19281
-24573
-24806
-22099
-28668
-26434
Maximum
103359
93694
87453
86538
81042
94492
95214
Mean
28316
25176
24575
24897
24047
24800
25156
Std Dev
18321
16830
16918
16763
16893
16755
17001
Variance
335670776
283248403
286219464
281006680
285369110
280719088
289039370
Skewness
0.1957
0.1899
0.1558
0.1537
0.1370
0.0850
0.1367
Kurtosis
2.8444
2.7098
2.6717
2.7235
2.6537
2.7347
2.7395
Median
27733
24537
24217
24564
23635
24670
24787
Mode
26569
23085
26653
19530
22584
24091
27278
Source: authors’ own elaboration

Table A.5. Summary statistics in the reference scenario for farm M-40
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-42840
-31750
-34632
-29880
-34910
-35238
-32301
Maximum
154828
138848
132934
138239
140937
126817
127022
Mean
40538
37485
36303
36790
36942
38175
38648
Std Dev
28227
25548
25959
25878
26168
25994
26237
Variance
796773522
652691088
673890123
669657922
684781641
675689778
688392235
Skewness
0.2065
0.1535
0.1992
0.1463
0.1193
0.0938
0.1137
Kurtosis
2.7486
2.6998
2.7050
2.6517
2.6569
2.6377
2.6459
Median
39139
36724
35347
36313
36580
38169
38421
Mode
39383
27927
41967
28297
23102
47828
28886
Source: authors’ own elaboration

Table A.6. Summary statistics in the scenario including greening for farm M-40
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-43748
-32653
-36789
-33652
-36935
-43747
-37568
Maximum
141005
128046
130270
125241
137228
132914
130281
Mean
40372
37000
36055
36671
35034
35516
36168
Std Dev
28203
25777
25763
25771
25946
25927
26272
Variance
795411947
664469404
663744314
664123109
673175818
672212812
690227360
Skewness
0.2212
0.1841
0.2224
0.1660
0.1237
0.1379
0.1339
Kurtosis
2.7791
2.6439
2.7389
2.7068
2.7014
2.7489
2.6607
Median
39232
36299
35059
36010
34743
35094
35791
Mode
32206
37359
34764
46749
28277
42199
29839
Source: authors’ own elaboration

Table A.7. Summary statistics in the reference scenario for farm M-116
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-116529
-94184
-114201
-100362
-111261
-132981
-102702
Maximum
382939
347669
347143
369382
373944
377855
343999
Mean
97706
91513
89002
91609
92248
95132
95091
Std Dev
79900
70675
70745
72288
73235
72881
72681
Variance
6383995982
4995008877
5004813295
5225517857
5363358470
5311686580
5282592677
Skewness
0.1714
0.1829
0.1616
0.1536
0.1539
0.1026
0.1346
Kurtosis
2.7102
2.6509
2.7181
2.6551
2.6574
2.6902
2.6519
Median
93674
88813
87494
89765
89794
95119
93026
Mode
73316
84480
78900
96929
117747
101508
92193
Source: authors’ own elaboration

Table A.8. Summary statistics in the scenario including greening for farm M-116
Year
2014
2015
2016
2017
2018
2019
2020
Minimum
-126239
-98209
-115999
-96292
-117586
-110651
-122500
Maximum
367659
348454
347644
337303
320354
359915
327309
Mean
97263
91581
90842
91867
81714
85886
87529
Std Dev
79251
71141
72213
72300
71783
71209
71625
Variance
6280667164
5060991352
5214708353
5227305958
5152762517
5070726873
5130138282
Skewness
0.1862
0.1649
0.1684
0.1594
0.1528
0.1040
0.0695
Kurtosis
2.7276
2.6675
2.6948
2.6311
2.6622
2.7113
2.6298
Median
94688
89097
88790
89679
79739
85017
87264
Mode
74748
88193
82253
72061
77114
82567
102029
Source: authors’ own elaboration

REFERENCES

  1. Agricultural Policy 2014–2020. PBL Netherlands Environmental Assessment Agency, PBL Publication number: 500136007.
  2. Anton J., Kimura S., 2009. Farm level analysis of risk, and risk management strategies and policies: evidence from German crop farms. Paper provided by International Association of Agricultural Economists in its series 2009 Conference, August 16–22, Beijing, China.
  3. Atzori A., Tedeschi L., Cannas A., 2013. A multivariate and stochastic approach to identify key variables to rank dairy farms on profitability. Journal of Dairy Science, 96, 3378–3387.
  4. Barham E., Robinson J., Richardson J., Rister M., 2011. Mitigating cotton revenue risk through irrigation, insurance, and hedging. Journal of Agricultural and Applied Economics, Southern Agricultural Economics Association, vol. 43(04), 529–540.
  5. Benni N., Finger R., 2012. Where is the risk? Price, yield and cost risk in Swiss crop production. Paper provided by International Association of Agricultural Economists in its series 2012 Conference, August 18–24, Foz do Iguacu, Brazil.
  6. Benni N., Finger R., 2013. Gross revenue risk in Swiss dairy farming. Journal of Dairy Science, 96, 936–948.
  7. Bielza M., Garrido A., 2006. Evaluating the potential of whole-farm insurance over crop-specific insurance policies. Paper provided by International Association of Agricultural Economists in its series 2006 Annual Meeting, August 12–18, Queensland, Australia.
  8. Briner S., Finger R., 2013. The effect of price and production risks on optimal farm plans in Swiss dairy production considering 2 different milk quota systems. Journal of Dairy Science, 96, 2234–2246.
  9. Cantore N., 2012. The potential impact of a greener CAP on developing countries. Overseas Development Institute, London.
  10. Chen Y. 2014. Trade, food security, and human rights : the rules for international trade in agricultural products and the evolving world food crisis. Ashgate Publishing Ltd, UK, 156–165.
  11. Cimino O., Henke R., Vanni F., 2014. Greening direct payments in Italy: what consequences for arable farms? Paper prepared for presentation at the EAAE 2014 Congress ‘Agri-Food and Rural Innovations for Healthier Societies’August 26 to 29, 2014, Ljubljana, Slovenia.
  12. European Commission, 2013. Overview of CAP Reform 2014-2020. Agricultural Policy Perspectives Brief nº 5, December 2013. European Commission, DG Agriculture and Rural Development, Brussels.
  13. Goraj L., Bocian M., Osuch D., Smolik A., 2013. Parametry techniczno-ekonomiczne według grup gospodarstw rolnych uczestniczących w polskim FADN w 2011 r. [Technical and economic parameters by the groups of farms participating in Polish FADN in the year 2011], IERiGŻ, Warsaw [in Polish].
  14. Heinrich B., 2012. Calculating the 'greening' effect: A case study approach to predict the gross margin losses in different farm types in Germany due to the reform of the CAP. Diskussionspapiere, Department für Agrarökonomie und Rurale Entwicklung, No. 1205.
  15. Huygens D., Carlier L., Rotar I., Vidican R., 2011. Economy and Ecology: Twin Span for a Qualitative Agricultural Production in Europe? Bulletin UASVM Agriculture, 68(1)/2011.
  16. IFCN Dairy Report 2012, International Farm Comparison Network. Joint publication edited by: Hemme T., Kiel: IFCN Dairy Research Center, 2013.
  17. Lien G., 2003. Assisting whole-farm decision-making through stochastic budgeting. Agricultural Systems, 76, 399–413.
  18. Majewski E., Wąs A., Guba W., Dalton G. 2007. Oszacowanie ryzyka dochodów rolniczych w gospodarstwach mlecznych w Polsce na tle gospodarstw innych kierunków produkcji w warunkach różnych scenariuszy polityki rolnej [Assessment of farm income risk in dairy farms in Poland in comparison to farms of other production types under different agricultural policy scenarios]. Roczniki Nauk Rolniczych, Seria G, t. 93, z. 2, 98–106 [in Polish].
  19. Matthews, A., 2013. Greening agricultural payments in the EU’s Common Agricultural.
  20. Neyhard J., Tauer L., Gloy B., 2013. Analysis of price risk management strategies in dairy farming using whole-farm simulations. Journal of Agricultural and Applied Economics, 45, 2, 313–327.
  21. OECD-FAO Agricultural Outlook 2013. OECD/Food and Agriculture Organization of United Nations, OECD Publishing, 2013
  22. Offermann F., Deblitz C., Golla B., Gömann H., Haenel H., Kleinhanß W., Kreins P., Ledebur O., Osterburg B., Pelikan J., Röder N., Rösemann C., Salamon P., Sanders J., Witte T., 2014. Thünen-Baseline 2013–2023: Agrarökonomische Projektionen für Deutschland. Thünen Report, No. 19, Johann Heinrich von Thünen-Institut, Braunschweig, Germany.
  23. Sieber S., Amjath-Babu T.S., Jansson T., Müller K., Tscherning K., Graef F., Pohle D., Helming K., Rudloff B., Saravia-Matus B.S., Gomez y Paloma S., 2013. Sustainability impact assessment using integrated meta-modelling: Simulating the reduction of direct support under the EU common agricultural policy. Land Use Policy, 33, 235–245.
  24. Stachak S. 1998. Ekonomika agrofirmy [Economics of agricultural business]. Wydawnictwo Naukowe PWN, Warsaw [in Polish].
  25. Vanni F., Cardillo C., Cimino O., Henke R., 2013. Introducing green payments in the CAP: the economic impact on Italian arable farms. Economia & Diritto Agroalimentare XVIII, 11–29.
  26. Wąs A., Majewski E., Czekaj S., 2014. Impacts of CAP “Greening” on Polish Farms. Paper prepared for presentation at the EAAE 2014 Congress ‘Agri-Food and Rural Innovations for Healthier Societies’August 26 to 29, 2014, Ljubljana, Slovenia.
  27. Westhoek H., Zeijts H., Witmer M., Berg M., Overmars K., Esch S., Bilt W., 2012. Greening the CAP: An analysis of the effects of the European Commission’s proposals for the Common.
  28. World Bank Commodities Price Forecast. October 2013. http://www.worldbank.org.
Accepted for print: 17.03.2015
Ewa Ko這szycz
Department of Management, Faculty of Economics, West Pomeranian University of Technology Szczecin, Poland
ul. K. Janickiego 31
71-270 Szczecin
Poland
email: ewa.koloszycz@zut.edu.pl

Artur Wilczy雟ki
Department of Management, Faculty of Economics, West Pomeranian University of Technology Szczecin, Poland
ul. K. Janickiego 31
71-270 Szczecin
Poland
email: artur.wilczynski@zut.edu.pl

Responses to this article, comments are invited and should be submitted within three months of the publication of the article. If accepted for publication, they will be published in the chapter headed 'Discussions' and hyperlinked to the article.