Literature DB >> 29623193

Comparing organic versus conventional soil management on soil respiration.

Bence Mátyás1,2, Maritza Elizabeth Chiluisa Andrade3, Nora Carmen Yandun Chida3, Carina Maribel Taipe Velasco3, Denisse Estefania Gavilanes Morales3, Gisella Nicole Miño Montero4, Lenin Javier Ramirez Cando2, Ronnie Xavier Lizano Acevedo2.   

Abstract

Soil management has great potential to affect soil respiration. In this study, we investigated the effects of organic versus conventional soil management on soil respiration.  We measured the main soil physical-chemical properties from conventional and organic managed soil in Ecuador. Soil respiration was determined using alkaline absorption according to Witkamp.  Soil properties such as organic matter, nitrogen, and humidity, were comparable between conventional and organic soils in the present study, and in a further analysis there was no statically significant correlation with soil respiration. Therefore, even though organic farmers tend to apply more organic material to their fields, but this did not result in a significantly higher CO2 production in their soils in the present study.

Entities:  

Keywords:  conventional soil management; organic soil management; soil respiration

Year:  2018        PMID: 29623193      PMCID: PMC5861514          DOI: 10.12688/f1000research.13852.1

Source DB:  PubMed          Journal:  F1000Res        ISSN: 2046-1402


Introduction

Research related to the benefits of organic management [1] has become increasingly important in sustainable agriculture. Organic soil management can contribute to meaningful socio-economic and ecologically sustainable development. Kilcher states that "Organic agriculture reduces the risk of yield failure, stabilizes returns and improves the quality of life of small farmers’ families" [2]. Soil management has great potential to affect soil respiration, which is an important qualitative indicator of soil microbial activity [3]. Soil respiration is released as a result of soil organic matter decomposition. The present study aims to investigate the effects of organic versus conventional management on CO 2 production of some Northern Ecuadorian agricultural soils. Our hypothesis was that major soil respiration will be observed in soils under organic management due to the increased amount of applied organic materials.

Methods

Sampling sites

Soil samples from 23 organic farms and conventionally managed neighbouring farms were analyzed. In total, 17 sampling sites were located in organic farms, while 6 sampling sites were located in chemical fertilizer-treated areas. The sampling sites were chosen according to proximity of organic and conventionally managed farms in which the same crops are produced. Further details about each of the sampling sites can be found in Table 1. Approximately 1000 g of soil samples of 0–20 cm depth were taken. The following crops were produced in the examined areas: broccoli, potato, tomato and carrot.
Table 1.

Characteristics of the conventional and organic farms chosen for the present study.

Variables are follows: areas of examined lands ( m2), Name of crops, soil management (Organic/Conventional), Total crop production (kg), Applied fertilizer (kg), Type of fertilizers, Concentration of NPK, Concentration of NPK, Amount of NPK (Kg), GPS coordinates of the examined lands.

Farmer’s codeCropSolid fertilizersArea of land m2Total crop production (Kg)Fertilizer application rate on total crop production (Kg)Concentration of NPK (%) in each fertilizer solidAmount of NPK in kgliquid fertilizerFertilizer application rate on total crop production (Kg)Concentration of NPK (%) in each liquid fertilizerAmount of NPK in KgGPS coordinates
NKPNKPNKPNKPlatitudelength
OB1BroccoliAgroecologicalCompost60.3831595.250.530.63451.3220.5048250.604361251.259205Biol2.639750.24280.81830.30610.006409310.021601070.008080275O804800OOO3519
OB2AgroecologicalBocashi118.2576268.030.170.40130.0710.4556511.075604390.1903013Biol1850.21.08160.01480.372.000960.02738O809419OOO6402
OB3AgroecologicalCompost979.220.20.30.38910.12210.06060.07859820.0246642biol300.140.00750.4670.0420.002250.1401O809136OOO3476
OB4AgroecologicalBocashi1446003000.50.86670.12711.52.60010.3813Biol211.180.240.40330.09580.5068320.851688940.20231044O804806OOO3527
OB5AgroecologicalBocashi56326.71010.430.44270.50810.43430.4471270.513181Biol1500.22020.28620.07350.33030.42930.11025O811423OOO3176
CB1Conventional184602511.6831682.216541804614.7989772037.8196084O805608OOO1169
OO6033.339040600020.0034240
Triple 1544.45211515156.6678156.6678156.667815
UREA2.146000.96600
OT1TomatoAgroecologicalGallinaza322.7660.032276615500.590.68150.86739.14510.5632513.44315Biol78.513873071.091.56590.53740.855801221.229448740.42193355408111930006955
Compost15500.892.58750.694913.79540.1061.077
OT2AgroecologicalHumus 1202.40.0202424701.242.94291.082830.62872.6896326.74516Biol2086.45840.260.34430.22165.424791847.183676274.62359181408092140003617
Humus 224700.660.74580.523216.30218.4212612.92304
Bocashi24700.81.24780.648619.7630.82116.02
Bocashi negro24701.291.05810.270531.86326.1356.681
OT3AgroecologicalCompost250.9120.02509126.380.390.87310.20640.0248820.055703780.001316832Biol11964.36920.2200450.0734485860.285999826.32699628.7876634.21807208114290003184
Bocashi6.380.430.50810.44270.0274340.0330.028
CT1ConventionalNitrogen Magnesium847.1320.084713241.3210.7003.790008090210002732
Ultrasol K41.32134605.371619.00720
CT2Conventional8-20-204827.690.48276999.43820207.9519.8919.8908053160001139
MAP99.431206111.93060.65
EC FERTILIZER41.4315.5005.1400
CT3ConventionalFlorone1234.8650.12348655.66863584319.550.0566863580.5385204050.28343179208053120001138
Nitrofoska foliar40.49025602824123.249.717661454.8588307
OP1POTATOAgroecologicalCompost116408.1613600.530.63451.3227.2088.62917.979Biol1.05590.24280.81830.30610.002563730.008640430.003232118048513376
OP2AgroecologicalGallinaza88.2136503.144.37526.09221.572.18763.0461Biol 84.4720.170.40130.0710.14360240.338986140.05997128094146481
Cal Agrícola9.0719xxxxxx
OP3AgroecologicalBocashi69.9181.415000.380.76950.47725.711.54257.158Biol 112.67080.220.36190.0130.027875760.045855630.0016472048081613438
Biol 2 microorga.6.33540.130.20650.00650.008236020.01308260.000411801
OP4AgroecologicalCompost13.1745.354.53590.910.42830.8650.041276690.019427260.03923554Biol1.583850.180.2240.03870.002850930.003547820.000612958082253496
CP1ConventionalHarvest waste10 000136103000xxxx8103115670
1030107501010307575225
1846025018460451150
Stimufolk4113852.27.61
Agricare41919199.59.59.5
OC1CarrotAgroecologicalCompost92.972045146.660.530.63451.3220.7772980.93055771.9388452Biol4.060.24280.81830.30610.009857680.033222980.0124276617N 08048050003544
OC2Agroecological15.645156000000Biol 20.230.0070.01810.00460.000140.00036217 N08114490003795
OC3AgroecologicalBocashi9721.350.380.76950.47720.005130.010388250.0064422Biol (1)1.640.220.36190.0130.0036080.005935160.000213217 N 08082840003066
Biol (2)0.820.130.20650.00650.0010660.00169330.0000533
OC4AgroecologicalBocashi11.224623.30.50.86670.12710.11650.20194110.0296143Biol16.4250.240.40330.09580.039420.066242030.0157351517 N 08048080003504
OC5AgroecologicalCompost601500134.60.30.38910.12210.40380.52372860.1643466biol2000.140.00750.4670.280.0150.93417 N O8091360003548
CC1Conventional176.56108Biofertilizante (lombriz)600.320.39630.45950.1920.001268160.00182099917 N 08053830001613
Nitrato de Calcio0.1315000.019500
Fosfato Monoamonico0.0711052.50.0073333300.035
Nitrato de Potasio0.0713440.0086666700.02933333

Characteristics of the conventional and organic farms chosen for the present study.

Variables are follows: areas of examined lands ( m2), Name of crops, soil management (Organic/Conventional), Total crop production (kg), Applied fertilizer (kg), Type of fertilizers, Concentration of NPK, Concentration of NPK, Amount of NPK (Kg), GPS coordinates of the examined lands.

Soil properties

Soil moisture content was determined gravimetrically, drying the soil at 105°C for 24 hours according to Fernández et al. (2008) [4]. Soil texture was measured using sodium hexametaphosphate (( NaPO 3) 6) according to Bouyoucos (1962) [5]. To measure the soil chemical properties, the samples were sieved through a 2mm mesh and pre-incubated at 25° for 72 hours. Soil pH in distilled water (soil/water, 1/2.5, w/w) was determined according to Karkanis (1991) [6]. In addition, we measured the electrical conductivity (EC) using a glass electrode according to Karkanis (1991) [6]. Cylinder volume was determined according to Agostini et al. (2014) [7]. Soil organic matter was determined according to Walkley and Black (1934) [8]. We measured the phosphorous content according to Olsen (1954) [9]. The Sand/Silt/Clay ratio was determined by Bouyoucos’s method (1936) [10], while the cation exchange capacity was determined according to ISO 11260 (1994) [11] protocol.

Soil respiration

The experiment was applied at 25° C. 0, 1 M NaOH (10 ml) was placed in laboratory bottles (250 ml), a sterile gauze pad were filled with 10 g of soil sample according to Witkamp (1966) [12]. After 10 days, the amount of CO 2 was subsequently measured by standardized titration against 0.1 N HCl using firstly phenolphthalein and then methyl orange indicator according to Witkamp (1966) [12]. The below formula was applied to calculate soil respiration: m( CO 2) = VxNx22 CO 2 And CO 2 production (for 10 days): mg( CO 2) * 100 g – 1 * 10 day – 1 = methyl orange factor * HCI – phenolphthaleinloss) * NAOH factor * 2, 2 * Moisture multiplication factor where We determined the volume of the examined soils (counting with 0 – 20 cm depth) using topsoil calculator tool ( https://www.tillersturf.co.uk/topsoil-calculator). The results of soil respiration was then estimated in kg( CO 2)/ha/day.

Statistical analysis

To evaluate the behavior within results, two types of test were performed: i) Student’s t-test for comparing means between conventional and organic crop systems in terms of soil respiration (kg/CO2/ha/day), organic matter (%) and nitrogen (%). Furthermore, Person’s and Spearman’s correlation were fixed in order to test data covariation and correlation. ii) ANOVA was used to compare conventional and organic crop system and the type of crop harvested in the sampling site.

Results

The results of soil respiration from areas of organic and conventional soil management are comparable ( Dataset 1). For soil respiration, conventional soil mean was 88.50 and organic mean was 98.64, showing and increment around 10%. However, there were no statistically significant differences between group means as determined by one-way ANOVA (p =0.15), comparing conventional and organic systems. Pearson‘s and Kendell‘s tests have showed no correlation. Soil respiration correlation coefficient with organic matter was lower than 0.05 and with nitrogen content was lower than 0.12. This analysis did not consider the differences between conventional and organic systems ( Figure 1).
Figure 1.

Soil respiration compared with organic matter and nitrogen in soil.

There were statistically significant differences between group means as determined by one-way ANOVA (p < 0.05), comparing crop types. Furthermore, a post hoc test (Duncan) was fixed. There was only one crop (carrot) in conventional system (odds lower than 0.05) that differs drastically from the others, as pointed out in ( Figure 2).
Figure 2.

Boxplots showing alterations within crop systems and crop harvested in the zone.

Considering soil characteristics (pH, CIC, K, and Electric conductivity), Student’s t-test was applied to identify differences between conventional and organic systems. Only the characteristics from carrot crop systems (conventional or organic) have shown differences in terms of means (p < 0.05). Furthermore, the mean of conventional crop system was lower in every characteristic evaluated. Besides, these results were in congruence with Figure 2, leading us to believe that the cropping system has no influence on soil respiration, which is in contrast to the influence that soil characteristics have over soil respiration in this study. Parameters as follows: pH, Organic material (percentage), Total Nitrogen (percentage), Match (mg/kg), Potassium (cmol/kg), Electrical conductivity (dS/m), CIC (cmol/kg), Soil moisture content (percentage), Sand (percentage), Silt-limo (percentage), Clay (percentage), Texture (class), Soil respiration (kg/CO2/ha/day). Click here for additional data file.

Conclusions

Organic farmers tend to apply more organic material to their fields, but this did not result in a significantly higher CO 2 production in their soils. The difference between organic and conventional soils (10% in mean) is not enough to conclude that the soil respiration under these two systems was different, considering the analysis of their variance. Soil properties like organic matter, nitrogen, and humidity, were comparable between conventional and organic soils in the present study, and in a further analysis there was no statically significant correlation with soil respiration. However, biological significance should be investigated in a posteriori research including microbial community profile of the soil and specific interactions in highlands (over 2500 m.a.s.l.).

Ethics

Oral consent was obtained from the farmers for the collection of soil samples from their land. Their only request was to inform them about the results of the soil characteristics, that we have already done personally on 9 November, 2017.

Data availability

The data referenced by this article are under copyright with the following copyright statement: Copyright: © 2018 Mátyás B et al. Data associated with the article are available under the terms of the Creative Commons Zero "No rights reserved" data waiver (CC0 1.0 Public domain dedication). Dataset 1: Raw data for various parameters calculated in conventional and organic managed soils. Parameters as follows: pH, Organic material (percentage), Total Nitrogen (percentage), Match (mg/kg), Potassium (cmol/kg), Electrical conductivity (dS/m), CIC (cmol/kg), Soil moisture content (percentage), Sand (percentage), Silt-limo (percentage), Clay (percentage), Texture (class), Soil respiration (kg/CO2/ha/day). DOI, 10.5256/f1000research.13852.d195529 [13] The submitted manuscript by Bence et al. is good work which is suitable for publication in F1000 research. Authors have compared the organic practices and conventional practices, and compared their effects on soil respiration which is very important aspect. Standard methodologies were followed which ensures reproducibility of the results. The findings were subjected to the statistical analysis and conclusion drawn nicely. However, I have below suggestions for improvement which may be considered as minor revisions: "Physical-chemical" could be replaced by "Physico-chemical" throughout the manuscript. In abstract, word "statically" should be replaced by "statistically" In result, "showing and increment around 10%." should be "showing an increment around 10%." The discussion could be added more so that the findings of the study will become stronger. I have read this submission. I believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard. This article worked at the differences between organic and conventional soil management. This research examined an important and topical issue especially the soil respiration under changing plant and soil conditions. Introduction and methods The research investigated 23 soil samples in Ecuador. The samples were located from organic (17 samples) and conventionally managed neighboring farms (6 samples). In the research trials broccoli, potato, tomato and carrot were applied as test plant. Soil properties were measured after 1000 g soil samples of 0-20 cm depths of soil were taken in every picked area. The soil moisture, texture, pH, electrical conductivity, cylinder volume, organic matter, phosphorus content, sand/silt/clay ratio and cation exchange capacity, and the soil respiration were analyzed in laboratory. The values of the soil parameters are presented in a dataset, which inform about the important soil parameters especially the calculated soil respiration in kg (CO 2)/ha/day). The protocols (description of the tests) are clear and traceable, especially the formula to calculate soil respiration. The study describes the applied type of fertilizers especially the concentration of NPK fertilizers. Comment on the Methods - The sampling time and vegetation status are important for the evaluation, this information is missing in the study. If it’s possible, describe the followings: When the soil sampling happened? What was the state of the vegetation of test plants? - A bit more detail of the soil properties inform us about the actual soil status. The studied soils are classified as sandy textured soil, according to the soil classification (Franco Arenoso). The most typical parameters of the samples are the following: high sandy texture, neutral pH, good/very good organic matter-nitrogen and phosphorus content, 10-20% moisture content. I suggest describing it in the Methods. Results The results of the study are described with sufficient statistical analysis. It also describes the statistically significant/not significant results. There were solely statistically significant differences between crop types (for soil respiration by one-way ANOVA correlation test). - The Figure 1 contains a typographical error (Orgacin matter instead of Organic matter). - It may be more informative, if you use a line diagram instead of dot diagrams in the first figure. - The Figure 2 include the soil respiration values in kg CO 2/ha /day, which would be more clear with the average values. Conclusion The results have briefly evaluated and conclusions straightforward formulated. I quite agree with observations of the study that emphasizes the importance of further microbiological studies. I have read this submission. I believe that I have an appropriate level of expertise to confirm that it is of an acceptable scientific standard.
  2 in total

1.  Effect of herbicides on soil respiration: a case study conducted at Debrecen-Látókép Plant Cultivation Experimental Station.

Authors:  Zsolt Sándor; Ida Kincses; Magdolna Tállai; Daniel A Lowy; Jesus R Melendez; Nelly Ivonne Guananga Diaz; Luis Elias Guevara Iñiguez; Gerardo Cuenca Nevarez; Viviana Talledo Solórzano; János Kátai
Journal:  F1000Res       Date:  2020-11-19

2.  Determination of field capacity in the Chibunga and Guano rivers micro-basins.

Authors:  Benito Mendoza; Manuel Fiallos; Sandra Iturralde; Patricio Santillán; Nelly Guananga; Jaime Bejar; Daniel A Lowy; Imre Vágó; Zsolt Sándor
Journal:  F1000Res       Date:  2021-03-03
  2 in total

北京卡尤迪生物科技股份有限公司 © 2022-2023.