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III. An Empirical Field Study : Comparisons of Energy

3.4 Results of Energy Use

3.4.8 Driving Factors Determining the EE

If so, what is the driving factors determining the EE on energy inputs? The evaluation for this was conducted on two aspects - input categories and farming practices, by using the multiple regression analysis.

3.4.8.1 Input Categories Determining the EE

Regardless of farming systems, input category which can strongly influence the result of EE was explored by the multi-regression analysis.

<Table 3-33> Relations of Inputs Categories (GJ/ha) and EE  Input Variables

(category) B t value p value

(Constant) 2.215 6.542 .000

Machinery .594 1.264 .212

Fuel -.156 -2.482 .016*

Electricity -.216 -.733 .467

Seeds .042 .167 .868

Compost &

Fertilizers -.038 -2.582 .013*

Natural & Chemical

Pesticides -.036 -.266 .791

Mulch

Plastic -.124 -3.928 .000**

Labor .921 2.737 .009**

R=0.641 R-square=0.411 Corrected R-square=0.318 Durbin-Watson=1.628 F=4.446 p=0.000**

-Dependent variable: EE, *p<.05 **p<.01

Significant driving factors of input categories for EE are presented in Table 3-33.

The strongest driving factor to determine the outcome of EE beyond farm systems is mulching film (p=0.000) and labor(p=0.009). fuels (p=0.016), and composts and fertilizers (p=0.013) were also significantly related to the results of EE at the level of 5%. These results mean that the differences of these energy inputs vary largely between farms than other energy inputs.

The more the mulching film, fertilizers and fuels were used, the poorer the EE was (minus t value). On the other hand, the more the labor used, the better the EE obtained, because the energy coefficients of labor is relatively much lower than that of other inputs.

<Table 3-34> Relations of Inputs Categories (GJ/ha) and EE in CFS  Input Variables

(category) B t value p value

(Constant) 2.446 4.350 .000

Machinery .201 .224 .825

Fuel -.128 -1.007 .325

Electricity -.087 -.175 .863

Seeds .869 .805 .430

Compost &

Fertilizers -.056 -2.496 .021*

Natural & Chemical

Pesticides -.288 -1.471 .156

Mulch Plastic -.183 -2.296 .032*

Labor 1.305 2.539 .019*

R=0.722 R-square=0.522 Corrected R-square=0.340 Durbin-Watson=2.071 F=2.864 p=0.025*

-Dependent variable: EE, *p<.05 **p<.01

In addition, Tables 3-34 and 35 show the results when conventional and organic soybean production systems are separately analyzed from each other,

Table 3-34 shows the influential input variables to determine the outcome of conventional EE.

The result indicates that the massive commitment of fertilizers (p=0.021), mulching film (p=0.032) and labor (0.019) decreased the efficiency of conventional EE in soybean production. This means that the amounts of these input materials have big variations between conventional farms.

Hence, by regulating these inputs, conventional farms are able to effectively improve their EE.

On the other hand, the driving factors of EE in organic soybean farms are revealed with extraordinary results as shown in Table 3-35.

<Table 3-35> Relations of Inputs Categories (GJ/ha) and EE in OFS  Input Variables

(category) B t value p value

(Constant) 1.558 4.932 .000

Machinery .757 1.983 .061

Fuel -.052 -.975 .341

Electricity -.130 -.392 .699

Seeds -.203 -1.190 .247

Compost &

Fertilizers -.038 -1.706 .103

Natural & Chemical

Pesticides -1.610 -.447 .659

Mulch

Plastic -.046 -1.573 .131

Labor -.174 -.465 .646

R=0.591 R-square=0.349 Corrected R-square=0.101 Durbin-Watson=2.834 F=1.407 p=0.251

-Dependent variable: EE, *p<.05 **p<.01

In organic soybean production, only machinery has a weak relationship with EE (p=0.061). No other inputs variable have relations with the outcome of EE in organic farms.

These results imply that in general organic farmers typically use the same kind and amount of inputs within the limits of allowances under the organic standards.

Therefore, to improve the efficiency of energy use in organic farms, it is suggested that the development of alternative materials for low energy input is rather better than changing amount of currently used inputs.

3.4.8.2. Farming Practices Determining the EE

Which farming practices have serious impacts on the results of EE in both systems?

<Table 3-36> Relations of Farming Practices (GJ/ha) and EE  Input Variables

(practices) B t value p value

(Constant) 2.374 7.696 .000

Cultivation -.118 -2.335 .024*

Fertilizing -.023 -1.659 .104

Mulching -.102 -3.404 .001**

Seeding -.100 -.872 .388

Weeding .021 .159 .874

Spraying -.074 -.594 .555

Pruning 1.718 .862 .393

Irrigation -.080 -.172 .864

Harvesting .157 .890 .378

Threshing -.138 -2.066 .044*

Grading 2.572 3.002 .004**

R=0.666 R-square=0.444 Corrected R-square=0.317 Durbin-Watson=1.484 F=3.484 p=0.001*

-Dependent variable: EE, *p<.05 **p<.01

Table 3-36 shows the results of relationship with energy use for farming practices and EE regardless of farm management systems.

The result indicates that the mulching (p=0.001) and grading (p=0.004) practices have strong affected on the outcome of EE regardless of the farming systems. In addition, cultivation and threshing are significantly related to the EE at the level of 5%.

On the other hand, the results of the conventional and organic farming practices in relation to the EE are separately shown in Tables 37 and 38, respectively.

<Table 3-37> Relations of Farming Practices and EE in CFS  Input Variables

(practices) B t value p value

(Constant) 3.521 7.557 .000

Cultivation -.181 -2.436 .025*

Fertilizing -.030 -1.631 .120

Mulching -.107 -1.626 .121

Seeding -.245 -.448 .659

Weeding .081 .195 .848

Spraying -.540 -1.933 .069

Pruning 1.197 .422 .678

Irrigation 5.689 1.496 .152

Harvesting .344 .514 .614

Threshing -.203 -.926 .367

Grading 3.066 2.626 .017*

R=0.799 R-square=0.639 Corrected R-square=0.418 Durbin-Watson=1.717 F=2.892 p=0.022*

-Dependent variable: EE, *p<.05 **p<.01

In CFS, cultivation (p=0.025) and grading (p=0.017) energy have influenced on the outcome of the EE. This means that all other practices except cultivation and grading have no variations between practices. Also, cultivation and grading are meant to be adjustable practice for the improvement of EE at least in conventional farms.

Table 3-38 presents the results of the relationship of farming practices and EE in OFS. The results show that seeding (p=0.046) and harvesting (p=0.015) have significant variations to determine the result of EE in organic soybean farms. That is, seeding and harvesting can be the adjustable practice variables to determine EE in organic farms.

<Table 3-38> Relations of Farming Practices and EE in OFS  Input

Variables

(practices) B t value p value

(Constant) 1.256 4.017 .001

Cultivation -.043 -.903 .379

Fertilizing -.022 -1.197 .247

Mulching -.017 -.706 .489

Seeding -.169 -2.141 .046*

Weeding .057 .640 .530

Spraying 1.015 1.434 .169

Pruning -3.557 -1.201 .245

Irrigation .183 .530 .603

Harvesting .376 2.695 .015*

Threshing .004 .082 .936

Grading .739 .864 .399

R=0.731 R-square=0.534 Corrected R-square=0.250 Durbin-Watson=1.854 F=1.878 p=0.113*

-Dependent variable: EE, *p<.05 **p<.01

Therefore, to improve the efficiency of energy use, the alternative ways for cultivation and grading in CFS and for seeding and harvesting in OFS can be suggested as applicable solutions.