Assessment of the Influence of Peach Production Systems on the Quantity and Quality of Root Collinization by Arbuscular Mycorrhizal Fungi

José Luis da Silva Nunes*

Doctor in Plant Science, Administrative Director of BADESUL Desenvolvimento - Agência de Fomento do Estado do Rio Grande do Sul, Brasil, Andrade Neves street, Porto Alegre, Rio Grande do Sul, Brazil.

Corresponding Author E-mail: joselsnunes@yahoo.com.br

DOI : http://dx.doi.org/10.12944/CARJ.12.2.06

Article Publishing History

Received: 20 Jun 2024
Accepted: 30 Jul 2024
Published Online: 30 Jul 2024

Review Details

Plagiarism Check: Yes
Reviewed by: Dr. Rania Khater
Second Review by: Dr. Hayyawi Aljutheri
Final Approval by: Dr. Mohammad Reza Naroui Rad

Article Metrics

Views     PDF Download PDF Downloads: 118

Google Scholar

Abstract:

This work aimed to evaluate changes in arbuscular mycorrhizal fungi (AMF) communities in soils under different peach production systems in three municipalities in southern Brazil. Root and soil samples were collected in orchards under Integrated Production (IP) and Conventional Production (PB) management on municipal properties for three years. Soil samples of AMF spores were extracted, identified and counted. Root colonization and presence of mycorrhizal structures (hyphae, vesicles and arbuscules) present in the radicle. IP systems have always presented higher colonization levels than PC systems. The municipality of São Jerônimo presented the highest colonization rates in the summer, while Charqueadas presented the highest in the spring, all higher than the municipality of Pelotas. Colonization peaks occurred above 90% in São Jerônimo and Charqueadas for IP, while in Pelotas they did not reach levels above 61%. There were no differences between AMF communities regarding the number of species, between management systems in each production system. The municipality of Charqueadas presented a smaller number of species than Pelotas. The genus Glomus had the largest number of species (9), followed by Acaulospora (7), Scutellospora (2) and Archaeospora, Entrophospora and Gigaspora (1 each). Archaeospora leptoticha and Gigaspora margarita present in 97% of the samples.

Keywords:

Endomycorrhyzas; Production systems; Prunus persea; Time of the year

Download this article as: 

Copy the following to cite this article:

Nunes J. L. D. S. Assessment of the Influence of Peach Production Systems on the Quantity and Quality of Root Collinization by Arbuscular Mycorrhizal Fungi. Curr Agri Res 2024; 12(2). doi : http://dx.doi.org/10.12944/CARJ.12.2.06

Copy the following to cite this URL:

Nunes J. L. D. S. Assessment of the Influence of Peach Production Systems on the Quantity and Quality of Root Collinization by Arbuscular Mycorrhizal Fungi. Curr Agri Res 2024; 12(2). Available from: https://bit.ly/3YoToQL


Introduction 

In Brazil, peach production is concentrated in the southern state of Rio Grande do Sul1. Peach seedling production in southern Brazil takes place, the field, at the risk of serious phytosanitary problems2. In order to avoid such problems, one alternative be the production of seedlings in environment shelter (greenhouses or nurseries). However, in such cases, it is necessary to disinfect of the substrate, to eliminate plant pathogens. That procedure eliminates almost all microorganisms, including beneficial ones, such as arbuscular mycorrhizal fungi (AMF)3.

The inoculation of endomychorrhyzal fungi in substrates and disinfected soils in nurseries due to its ability to improve the radicular system, may increase to biotic and abiotic stresses. That can lead to production of high-quality plants in systems using lower amounts of agricultural inputs4.

The search for sustainable agriculture necessarily involves a substantial reduction of chemical inputs, including fertilizers, and Integrated Production system offers a possibility to increase farmers gains and consumer’s access to high-quality products1.

Those factors increase the relevance of understanding population changes in AMF in peach orchards, along seasons, once they are already adapted to the edaphocilmatic conditions of the region, propitiating a high potential of response when inoculated in plants to be cultivated in this region. Furthermore, it is crucial to assess the influence upon these populations of soil management systems used in the Integrated Production System and Conventional Production System. The aim of this work was to assess the influence of the management system (Conventional Production and Integrated Production), the locations, season upon the composition and diversity of species AMF peach orchards.

Materials and Methods

The evaluations were carried out in the years 2021, 2022 and 2023, in commercial peach orchards in the municipalities of Charqueadas, São Jerônimo and Pelotas, in the state of Rio Grande do Sul, Brazil. The predominant soil in these locations is Typical Paleudult5, the climate is Cfa6, corresponding to the humid subtropical climate with hot summer7. The orchards were managed under the Integrated Production (IP) system, according to PI technical guidelines, and Conventional Production (PC), according to technical recommendations for peach cultivation8.

The samples (rhizospheric soil and roots collected in the four seasons of the year), composed of 20 subsamples, were collected in the upper 20 cm of the soil, under projections of the tree canopy. During the Spring-Summer period, samples were analyzed for pH, organic matter and macronutrient content9.

The intensity of AMF colonization was evaluated in 96 segments of 1cm long rootlets, per orchard and season. These fragments were clarified and stained10 and examined under a microscope to evaluate the presence of hyphae, vesicles and arbuscules11. The percentage of colonized roots was obtained through the relationship: number of infected segments by the number of segments analyzed.

Spores were isolated from 100 g of soil samples by wet sieving (105 μm and 53 μm sieves)12,13, followed by centrifugation and 50% sucrose gradient14. Viable spores were counted under stereomicroscope and determined to species level15.

The data were subjected to analysis of variance, carried out using the Statistical Analysis System (SAS) software, and the means were compared using the Duncan test at a significance level of 5%. The results of presence and absence of species and chemical characteristics of the soil were subjected to correlation analysis (P<0.01 and P<0.05).

Results and Discussion 

In the municipality of São Jerônimo, the percentage of root colonization by AMF was high (above 67%) in both production systems, with significant differences between them. The percentage of root colonization under IP was always higher than under CP, while in Charqueadas this occurred in winter and spring. Colonization reached peaks in the summers of 2021, 2022 and 2023, for São Jerônimo, and in the springs of 2021, 2022 and 2023 for Charqueadas, being greater than 90% in the IP. In the municipality of Pelotas, the percentage of root colonization by AMF was low in both production systems, always higher in the IP system. Throughout the year there were differences between the seasons, in both systems, always greater in spring. The comparison between regional averages shows that the percentage of root colonization by AMF was higher in the IP in the São Jerônimo and Charqueadas regions, when compared with the CP system there and with the results from the Pelotas systems (Table 1).

Table 1: Percentage of radicular colonization by AMF in peach-trees submitted to Integrates Production (IP) System and Conventional Production (CP) System in four orchards of three municipalities of Rio Grande do Sul, Brazil.

Seasons of the year¹

Municipalities²

São Jerônimo

Charqueadas

Pelotas

Production systems¹

IP

CP

IP

CP

IP

CP

Summer/21

90.60aA

  75.50aB

70.25cB

70.62bA

46.56bA

34.87bB

Autumn/21

71.10cA

 69.10bB

67.50dA

67.37cA

42.50cA

32.50cB

Winter/21

70.90cA

  67.20cB

76.00bA

71.94bB

42.75cA

31.75eB

Spring/21

75.00bA

  71.00bB

92.62aA

78.00aB

59.95aA

41.50aB

Summer/22

91.19aA

  77.25aB

70.50cA

70.75bA

46.25bA

34.75bB

Autumn/22

71.81cA

 69.06bB

67.75dA

67.62cA

43.75cA

31.52eB

Winter/22

70.56cA

 67.81cB

76.12bA

72.00bB

42.50cA

31.87eB

Spring/22

75.69bA

  71.12bB

93.00aA

77.87aB

61.00aA

41.25aB

Summer/23

92.44aA

  77.62aB

71.00cA

70.25bA

46.50bA

34.00bB

Autumn/23

72.12cA

 70.00bB

68.00dA

67.75cA

42.00cA

32.00cB

Winter/23

70.69cA

  68.12cB

76.25bA

71.75bB

42.50cA

31.50eB

Spring/23

76.75bA

  71.62bB

92.71aA

77.00aB

60.00aA

41.34aB

Mean²

77.40  A

  71.28  B

76.81  A

71.45  B

48.02  C

34.90  D

C.V. (%)

     5.84

    5.80

   5.54

    5.86

    4.99

    4,94

¹Means followed by the same low case letter in the column (seasons of the year) and capital letter in the line (production system) do not differ among themselves by the test of Duncan at 5% of significance.

²Means followed by the same capital letter in the line (municipalities and production system) do not differ from each other using the Duncan test at the 5% significance level.

The most likely cause for the variation in the percentage of root colonization between regions and treatments is related to the type of soil and its management used on each property and production system. The effective benefits of AMF in agricultural production are more promising in circumstances where the infection potential of native fungi is indirectly manipulated through soil management and crop rotation16. Thus, agricultural management is decisive in the establishment and performance of native AMF, since several factors (pH, fertility level, humidity, aeration, soil management, degree of mycorrhizal dependence of the plant, and the interactions between fungi and other soil microorganisms) interfere, positively or negatively, in the ineffectiveness of the fungus and in the efficiency of association17.

In the São Jerônimo and Charqueadas region, soil management in the IP area used winter cover with oats and herbicide between the rows, without the use of harrows and controlled use of agricultural inputs such as fertilizers and pesticides, in accordance with the Specific Technical Standards for Production Integrated Peach (NTEPIP). In the CP area, on the São Jerônimo property, soil management consisted of light harrowing with a depth varying between 4 and 5 cm between rows, incorporating fertilizer on the periphery of the tree main. Subsequently, the farmer began to use only the brush cutter as a method of controlling the growth of natural cover between the rows.

On the Charqueadas property, the farmer only used the brushcutter, without harrowing in the CP. In IP, the use of a species for ground cover (oats) probably caused a decrease in biological diversity, which increased the possibility of root colonization in peach trees.

In the Pelotas region, oats were used as winter cover in IP and natural cover in CP. Until 2003, the producer used side harrows in the row and harrowing between CP lines to incorporate fertilizers, and natural coverage in IP. From the spring of 2004, the farmer started to use only natural cover in both production systems, without harrowing. The use of mulch or green manure promotes AMF colonization18. Furthermore, in agroecosystems with a low level of interference from agricultural practices, rates of mycorrhizal colonization are high19. On the other hand, root colonization rates and AMF spore density are lower in soils subjected to mechanical disturbances or kept uncovered20. The use of natural cover in CP allowed an increase in the diversity of host plant species and the diversity of AMF species, which increased competition between them. Many species of autochthonous AMF could show lower colonization responses in the presence of a cultivated crop, which would lead to a decrease in the percentage of colonization of these cultivated plants21. According to the same authors, species may be present in environments, but may not respond to the presence of roots of some plants. Furthermore, the diversity of host species promotes the establishment of a high number of colonization by AMF, due to the high number of hosts that can be colonized22. Thus, the community of plants on which fungi depend to obtain photoassimilates can also influence the structure of the AMF community, which suggests that the diversity of spontaneous vegetation in agroecosystems alters the diversity of AMF species, increasing the number of species and competitions with each other23.

It is worth noting that the high phosphorus content did not affect root colonization, especially in IP. Oats, under ideal pH conditions (around 6.0 to 6.5), extract large amounts of phosphorus from the soil, which would favor the action of mycorrhizae24. Furthermore, as there is a mixture of AMF in the soil of an orchard, it is plausible to assume that the different behaviors of these species may also have helped to ensure mycorrhizal colonization of the roots, regardless of the level of phosphorus present in the soil. This can be proven by the fact that, during the vegetative period of peach trees, the percentage of root colonization was higher in IP than in CP, even under similar fertility and pH conditions (Table 2).

Table 2: Chemical Analysis of the soil samples collected in the years 2021, 2022, 2023 in peach-orchards submitted to Integrates Production (IP) System and Conventional Production (CP) System in four orchards of three municipalities of Rio Grande do Sul, Brazil.

Regions  Systems/year

Clay

(%)

pH

OM3

(%)

P4

(mg.dm-3)

K5

(mg.dm-3)

Ca6

(cmolc.L-1)

Mg7

(cmolc.L-1)

SJ1

IP2/21

26

6.6

1.8

27

123

4.5

0.9

CP2/21

28

6.8

2.1

28

125

5.7

0.9

IP2/22

32

6.3

1.7

22

145

10.7

0.7

CP2/22

24

6.2

2.8

26

219

9.7

1.1

IP2/23

22

6.1

2.2

15

113

5.8

1.1

CP2/23

24

6.0

2.4

20

234

8.1

1.7

Ch1

IP2/21

32

6.3

2.4

61

324

6.9

2.1

CP2/21

29

6.7

2.3

84

353

7.8

2.2

IP2/22

30

6.5

2.5

47

344

6.3

1.9

CP2/22

32

6.2

2.5

60

378

5.4

1.7

IP2/23

34

6.2

2.4

31

357

6.9

2.1

CP2/23

32

6.1

2.5

53

354

6.8

2.0

Pel1

IP2/21

22

4.5

2.5

14

132

1.5

0.5

CP2/21

25

4.6

2.7

17

158

2.9

1.0

IP2/22

22

5.2

2.3

16

104

2.7

1.0

CP2/22

22

5.0

1.9

15

177

2.0

0.9

IP2/23

23

5.1

2.1

15

114

2.4

1.0

CP2/23

22

5.2

2.0

16

143

2.5

1.1

1Ch – Charqueadas; SJ – Sao Jerônimo; Pel – Pelotas; 2IPIntegrates Production; CP – Conventional Produtiction; 3OM – organic matter; 4P – Phosphorus; 5K – Potassium; 6Ca – Calcium; 7Mg – Magnesium.

On the other hand, the average colonization of the IP, in the Pelotas region, was lower than that of São Jerônimo and Charqueadas, which can be explained by the soil pH, which is lower on the Pelotas properties, which could harm the development of oats. and phosphorus absorption (Table 2). Under low pH, it is assumed that colonization would be guaranteed by the different behavior of the different mycorrhizal species present in orchards, since many AMF species prefer acidic soils or are indifferent to acidity. However, in Pelotas, the use of natural cover in the IP, combined with the high phosphorus content and low pH, maintained the average percentage of colonization throughout the year at 48.02%. In CP, these values ​​are 34.90%, largely due to the type of management used, with lateral harrowing towards the top of the tree, which would break the roots, damaging colonization (Table 1). Excessive soil disturbance reflects brightness in the AMF community and the establishment of the symbiotic association25.

The intensity of colonization, quantified by the presence of fungal structures (hyphae, vesicles and arbuscules) in the roots, was moderate for both systems in São Jerônimo. In PI, rates were higher than CP throughout the seasons of the years evaluated, except in the winter periods (Table 3).

Table 3: Presence of structures of colonization of AMF in roots of peach-trees submitted to Integrates Production (IP) System and Conventional Production (CP) System, collected in the years of 2021, 2022, and 2023, in the four seasons of the year at the property of Sao Jerônimo, RS, Brazil.

Structures

Seasons

Production systems

IP

CP

Hyphae

Summer/21

1.34aA

1.19aB

Autumn/21

1.12cA

0.98cB

Winter/21

1.01dA

0.97cA

Spring/21

1.25bA

1.12bB

Summer/22

1.35aA

1.20aB

Autumn/22

1.12cA

0.98cB

Winter/22

1.01dA

0.97cA

Spring/22

1.25bA

1.12bB

Summer/23

1.39aA

1.21aB

Autumn/23

1.14cA

1.01cB

Winter/23

1.01dA

0.98cA

Spring/23

1.26bA

1.13bB

Mean

1.19 A

1.07  B

C.V. (%)

6.75

7.22

Vesicles

Summer/21

1.02aA

0.80aB

Autumn/21

0.87cA

0.73bB

Winter/21

0.76dA

0.72bA

Spring/21

0.93bA

0.80aB

Summer/22

1.04aA

0.82aB

Autumn/22

0.85cA

0.73bB

Winter/22

0.76dA

0.72bA

Spring/22

0.93bA

0.80aB

Summer/23

1.05aA

0.82aB

Autumn/23

0.85cA

0.79aB

Winter/23

0.76dA

0.73bA

Spring/23

0.94bA

0.79aB

Mean

0.90  A

0.77  B

C.V. (%)

8.86

8.74

Arbuscules

Summer/21

1.25aA

1.09aB

Autumn/21

0.98cA

0.93bB

Winter/21

0.90dA

0.90cA

Spring/21

1.11bA

0.97bB

Summer/22

1.26aA

1.09aB

Autumn/22

0.96cA

0.91bB

Winter/22

0.91dA

0.88cA

Spring/22

1.09bA

0.97bB

Summer/23

1.27aA

1.10aB

Autumn/23

1.00cA

0.93bB

Winter/23

0.90dA

0.87cA

Spring/23

1.10bA

0.96bB

Mean

1.06  A

0.97 B

C.V. (%)

9.65

8.80

Means followed by the same low case letter in the column (seasons of the year) and capital letter in the line (production system) do not differ among themselves by the test of Duncan at 5% of significance.

In the case of the property in Charqueadas, the presence of fungal colonization structures was considered low to moderate in terms of the presence of hyphae and low in terms of vesicles and arbuscules, in both systems. In both systems, the presence of fungal structures was greater in spring, while the rate of root colonization by AMF was higher in the IP system compared to CP only in winter and spring of all years evaluated, this period also being the peak presence of structures (Table 4).

Table 4: Presence of structures of colonization of AMF in roots of peach-trees submitted to Integrates Production (IP) System and Conventional Production (CP) System, collected in the years of 2021, 2022, and 2023, in the four seasons of the year at the property of Charqueadas, RS, Brazil.

Structures

Seasons

Production systems

IP

CP

Hyphae

Summer/21

1.04cA

1.03cA

Autumn/21

0.99dA

0.98dA

Winter/21

1.26bA

1.12bB

Spring/21

1.41aA

1.22aB

Summer/22

1.04cA

1.03cA

Autumn/22

1.00dA

0.99dA

Winter/22

1.26bA

1.13bB

Spring/22

1.42aA

1.23aB

Summer/23

1.05cA

1.04cA

Autumn/23

1.02dA

1.00dA

Winter/23

1.26bA

1.14bB

Spring/23

1.42aA

1.23aB

Mean

1.17  A

1.09  B

C.V. (%)

9.67

9.99

Vesicles

Summer/21

0.76cA

0.74cA

Autumn/21

0.69dA

0.69dA

Winter/21

0.95bA

0.78bB

Spring/21

1.07aA

0.84aB

Summer/22

0.76cA

0.75cA

Autumn/22

0.70dA

0.69dA

Winter/22

0.96bA

0.77bB

Spring/22

1.08aA

0.84aB

Summer/23

0.76cA

0.75cA

Autumn/23

0.72cA

0.68dA

Winter/23

0.96bA

0.79bB

Spring/23

1,09aA

0,85aB

Mean

0.88 A

0.76 B

C.V. (%)

9.17

7.72

Arbuscules

Summer/21

0.89cA

0.88cA

Autumn/21

0.89cA

0.87cA

Winter/21

1.11bA

0.98bB

Spring/21

1.28aA

1.07aB

Summer/22

0.92cA

0.90cA

Autumn/22

0.90cA

0.87dA

Winter/22

1.13bA

0.99bB

Spring/22

1.27aA

1.07aB

Summer/23

0.92cA

0.91cA

Autumn/23

0.90cA

0.88dA

Winter/23

1.14bA

1.00bB

Spring/23

1,29aA

1,08aB

Mean

1.05  A

0.96  B

C.V. (%)

8.71

8.56

Means followed by the same low case letter in the column (seasons of the year) and capital letter in the line (production system) do not differ among themselves by the test of Duncan at 5% of significance.

With regard to the municipality of Pelotas, the presence of colonization structures was considered scarce, both in systems and properties. The IP production system presented the highest rates in relation to CP, in all seasons of the years evaluated, always being higher in spring (Table 5).

Table 5: Presence of structures of colonization of AMF in roots of peach-trees submitted to Integrates Production (IP) system and Conventional (CP), collected in the years of 2021, 2022, and 2023, in the four seasons of the year at the property of Pelotas, RS, Brazil.

Structures

Seasons

Production systems

IP

CP

Hyphae

Summer/21

0.58cA

0.46bB

Autumn/21

0.50dA

0.43cB

Winter/21

0.62bA

0.48bB

Spring/21

0.69aA

0.54aB

Summer/22

0.60cA

0.46bB

Autumn/22

0.51dA

0.43cB

Winter/22

0.67bA

0.48bB

Spring/22

0.71aA

0.55aB

Summer/23

0.60cA

0.47bB

Autumn/23

0.51dA

0.44cB

Winter/23

0.68bA

0.48bB

Spring/23

0,72aA

0,54aB

Mean

0.62  A

0.48  B

C.V. (%)

5.75

5.51

Vesicles

Summer/21

0.29cA

0.22bB

Autumn/21

0.27cA

0.21bB

Winter/21

0.33bA

0.24bB

Spring/21

0.39aA

0.30aB

Summer/22

0.27cA

0.23bB

Autumn/22

0.28cA

0.22bB

Winter/22

0.37bA

0.24bB

Spring/22

0.40aA

0.31aB

Summer/23

0.29cA

0.23bB

Autumn/23

0.30cA

0.22bB

Winter/23

0.34bA

0.25bB

Spring/23

0,38aA

0,30aB

Mean

0.33 A

0.25  B

C.V. (%)

8.86

5.41

Arbuscules

Summer/21

0.40cA

0.30cB

Autumn/21

0.36dA

0.31cB

Winter/21

0.45bA

0.39bB

Spring/21

0.55aA

0.48aB

Summer/22

0.40cA

0.35cB

Autumn/22

0.38cA

0.34cB

Winter/22

0.54bA

0.40bB

Spring/22

0.58aA

0.49aB

Summer/23

0.45cA

0.38cB

Autumn/23

0.38dA

0.34dB

Winter/23

0.50bA

0.39bB

Spring/23

0,57aA

0,49aB

Mean

0.46  A

0.39  B

C.V. (%)

                7.21

                   5.73

Means followed by the same low case letter in the column (seasons of the year) and capital letter in the line (production system) do not differ among themselves by the test of Duncan at 5% of significance.

These results relating to the municipality of Pelotas can be explained by the high levels of phosphorus found in soil samples, which has hampered the colonization and development of AMF structures in the roots26,27.

Were identified 21 species of AMF were identified in samples collected in orchards in both regions. There was no difference between the AMF communities in terms of the number of species, when evaluating the influence of the soil management systems used in each production system and season (Table 6).

Table 6: Number and relative occurrence (%) of species of AMF from peach-orchard submitted to Integrated Production (IP) and Conventional Production (CP) found in 84 samples (n) collected in the four-seasons of the years 2021, 2022, and 2023, in the municipalities of Charqueadas, Sao Jerônimo and Pelotas, Rio Grande do Sul State, Brazil.

Region

Season

Production system²

Total per region¹

Total of species

IP

CP

Charqueadas

Summer

13ns

12ns

13b

21

Autumn

12ns

11ns

Winter

11ns

10ns

Spring

13ns

12ns

Total  production system¹

12ns

11ns

Sao  Jerônimo

Summer

14ns

13ns

13b

Autumn

10ns

9ns

Winter

10ns

11ns

Spring

13ns

12ns

Total  production system¹

12ns

12ns

Pelotas

Summer

11ns

10ns

20a

Autumn

10ns

11ns

Winter

12ns

11ns

Spring

13ns

12ns

Total  production system¹

17ns

18ns

Species of AMF

Relative occurrence² (%)

Charqueadas

Sao  Jerônimo

Pelotas

IP    (n=14)

CP  (n=14)

IP      (n=14)

CP  (n=14)

IP (n=14)

CP (n=14)

Acaulospora bireticulata

14.28

Acaulospora denticulata

87.50

75.00

100.00

87.50

85.70

57.14

Acaulospora foveata

7.14

Acaulospora laevis

7.14

7.14

Acaulospora mellea

25.00

14.28

28.57

14.28

Acaulospora scrobiculata

100.00

50.00

Acaulospora tuberculata

37.50

42.85

14.28

21.42

7.14

Archaeospora leptoticha

100.00

100.00

100.00

100.00

100.00

85.71

Entrophospora colombiana

12.50

14.28

7.14

Gigaspora margarita

87.50

100.00

85.71

100.00

100.00

100.00

Glomus coremioides

37.50

37.50

42.86

28.57

Glomus claroideum

14.28

Glomus clarum

100.00

87.5

85.71

71.43

57.14

28.57

Glomus etunicatum

50.00

37.50

57.14

28.57

35.71

21.43

Glomus geosporum

87.50

62.50

85.71

100.00

50.00

35.71

Glomus glomerulatum

14.28

Glomus macrocarpum

87.50

100.00

85.71

57.14

100.00

35.71

Glomus microaggregatum

28.57

14.28

Glomus tortuosum

62.50

37.50

28.57

42.86

42.88

42.88

Scutellospora heterogama

75.00

100.00

71.43

100.00

57.14

71.43

Scutellospora weresubiae

57.14

42.86

1Means followed by the same letter in the column do not differ among themselves by the test of Duncan at 5% of significance. ns Non-significative.

2Number of samples in which the species was found divided by the total of samples collected in the municipality multiplied by 100.

Several authors21, when evaluating the influence of Conventional Production and Organic Production systems on the presence and composition of AMF species in citrus orchards, they realized that the organic soil management system, using conservation practices such as the use of plants to cover winter, presented more significant colonization rates, which coincides with the data obtained in this work. These authors also noted a greater number of AMF species under organic management, which disagrees with the results of this experiment. However, other research involving corn and soybeans maintained under conventional and organic soil management showed no differences in the number of AMF species between treatments, but found differences in the highest colonization rates in organic soil management28, which coincides with the results obtained in this work. When comparing regions, 13 species were found in the municipalities of Charqueadas and São Jerônimo, a value lower than that found in Pelotas, where 20 species of AMF were found.

The genus Glomus had the largest number of species (nine) followed by the genera Acaulospora (seven), Scutellospora (two), Archaeospora, Entrophospora and Gigaspora (one each) (Table 6). Regarding the species found, Archaeospora leptoticha and Gigaspora margarita appeared in 96.55% of the 58 samples analyzed, Acaulospora denticulate in 79.31%, Glomus macrocarpum and Scutellospora heterogama in 75.86%, Glomus clarum in 65.81%, Glomus geosporum in 63.79%, Glomus tortuosum in 43.10%, Acaulospora scrobiculata in 36.20%, Glomus etunicatum in 5.17%, Acaulospora bireticulata, Acaulospora laevis, Glomus glomerulatum and Glomus claraideum in 3.45% and Acaulospora foveata in 1.72% of the samples. Authors found that the most frequent species found in all samples collected in citrus groves under organic and conventional production were Glomus microaregtum and Acaulospora scrobiculata21, while others showed the presence of ten species in the samples, with Glomus macrocarpum being the most frequent (in 95% of samples) followed by Scutellospora heterogama (in 86%)3.

Some AMF species showed a significant correlation with soil chemical characteristics (Table 7).

Table 7: Correlation between the occurrence of species of AMF and the chemical characteristics of the soil belonging to the samples collected in the peach-orchards submitted to Integrated Production (IP) System and Conventional Production (CP) System during  Spring-Summer period in 2021, 2022 and 2023 in the municipalities of Charqueadas, Sao Jerônimo and Pelotas, Rio Grande do Sul State, Brazil.

Species of AMF

pH

M.O.

P

K

Ca

Mg

Acaulospora bireticulata

0.11ns

-0.13ns

-0.51*

-0.09ns

0.06ns

0.03ns

Acaulospora denticulata

0.02ns

0.15ns

0.10ns

0.13ns

-0.11ns

-0.14ns

Acaulospora foveata

0.04ns

-0.12ns

-0.48*

-0.06ns

0.14ns

0.08ns

Acaulospora laevis

0.01ns

-0.51*

-0.64**

-0.50*

0.06ns

0.14ns

Acaulospora mellea

0.02ns

-0.53*

-0.51*

-0.49*

0.08ns

0.05ns

Acaulospora scrobiculata

-0.09ns

0.14ns

0.12ns

0.10ns

-0.11ns

-0.18ns

Acaulospora tuberculata

0.02ns

-0.41*

-0.49*

-0.18ns

0.05ns

0.04ns

Archaeospora leptoticha

0.05ns

0.12ns

0.19ns

0.08ns

-0.07ns

-0.10ns

Entrophospora colombiana

-0.09ns

0.09ns

-0.50*

-0.11ns

0.06ns

0.07ns

Gigaspora margarita

0.15ns

0.18ns

0.14ns

0.16ns

-0.20ns

-0.19ns

Glomus coremioides

-0.59**

-0.02ns

-0.10ns

-0.08ns

0.13ns

0.09ns

Glomus claroideum

0.15ns

-0.18ns

-0.46*

-0.17ns

0.03ns

0.01ns

Glomus clarum

0.50*

0.11ns

0.08ns

0.13ns

-0.05ns

-0.07ns

Glomus etunicatum

0.06ns

-0.58*

-0.64**

-0.50*

0.12ns

0.15ns

Glomus geosporum

0.51*

0.06ns

-0.07ns

0.11ns

0.03ns

0.01ns

Glomus glomerulatum

0.05ns

-0.47*

-0.52*

-0.11ns

0.05ns

0.07ns

Glomus macrocarpum

0.09ns

0.12ns

0.05ns

0.04ns

-0.06ns

-0.02ns

Glomus microaggregatum

0.06ns

-0.11ns

-0.48*

-0.15ns

0.14ns

0.12ns

Glomus tortuosum

0.05ns

-0.52*

-0.56*

-0.47*

0.08ns

0.11ns

Scutellospora heterogama

0.08ns

0.10ns

0.08ns

0.06ns

-0.07ns

-0.09ns

Scutellospora weresubiae

0.05ns

-0.18ns

-0.51*

0.05ns

0.06ns

0.04ns

* and **Significative at 5% and at 1% of probability, respectively, by the test of Duncan. nsNon-significative.

The species Acaulospora bireticulata, Acaulospora foveata, Acaulospora laevis, Acaulospora mellea, Acaulospora tuberculata, Entrophospora colombiana, Glomus claroidium, Glomus etunicatum, Glomus glomerulatum, Glomus microaggregatum, Glomus tortuosum, and Scutellospora Weresubiae occurred in environment with lower contents of phosphorus, while Acaulospora laevis, Acaulospora mellea, Glomus etunicatum, and  Glomus tortuosum have shown themselves very sensitive also to the presence of high contents of organic matter and potassium. Several studies21 show the same correlation between the species Acaulospora mellea, Entrophospora colombiana, Glomus etunicatum and Glomus geosporum with phosphorus, in the same way29 that Acaulospora mellea and Glomus etunicatum prefer environments with lower phosphorus levels.

The species Acaulospora denticulata, Acaulospora scrobiculata, Archaeospora leptoticha, Gigaspora margarita, Glomus macrocarpum, and Scutellospora heterogama were indifferent to the soil characteristics. Glomus coremioides has shown itself sensitive to high pH, while Glomus clarum and Glomus geosporum have shown their preference for little acidic or neutral soils. Some species of the genus Gigaspora occurs in environments with pH lower than six29,30, while many species of the genera Acaulospora, Gigaspora and the species Glomus manihotis are particularly tolerant to conditions of high acidity31.

Conclusion

There is variation in the percentage of colonization of roots by AMF in function of the time of the year and system of production, where the Integrated Production presents higher colonization than the Conventional Production.

The type of soil and management used interfere in the colonization of the roots by AMFs and in the formation of their structures of colonization.

The use of oat as winter cover increases the possibility of colonization of plants cultivated.

There are not differences among the AMF communities regarding the number and composition of the species when assessing the influence of the systems of managements of soil employed in each system of production.

The chemical characteristics such as organic matter, phosphorus content, and the pH are determinant for the colonization of roots and for the formation of the spores, therefore influencing in the presence and response of the species of AMF.

Acknowledgment

The author thanks the Department of Horticulture and Forestry of the Faculty of Agronomy of the Universidade Federal do Rio Grande do Sul (UFRGS) and the Conselho Nacional de Pesquisa (CNPq).

Funding Sources

Conselho Nacional de Pesquisa (CNPq).

Conflict of Interest

The author has no conflicts of interest.

Data Availability Statement

This statement does not apply to this article.

Ethics Statement

This research did not involve human participants, animal, subject, or any material that requires ethical approval.

Informed Consent Statement

This study did not involve human participants, and therefore, informed consent was not required.

Authors’ Contribution

The author, Dr. José Luis da Silva Nunes, was responsible for the conception and design of the study, data acquisition, analysis and interpretation of the data and writing of the article.

References 

  1. Fachinello JC, Tibola CS, De Mio LLM, Monteiro LB (2004) Produção integrada de pêssego (PIP). In: Monteiro LB, De Mio LLM, Monte Serrat B, Motta AC, Cuquel FL (eds) Fruteiras de caroço: uma visão ecológica. UFPR, Curitiba, pp. 363-390.
  2. Medeiros CAB, Raseira MCB (1998) A cultura do pessegueiro. Embrapa, Brasília.
  3. Souza, PVD, Schimitz JA, Freitas RS, Carniel E, Carrenho R (2002) Identificação e quantificação de fungos micorrízicos arbusculares autóctones em municípios produtores de citros no Rio Grande do Sul. Ciência Rural, 37: 553 – 558.
    CrossRef
  4. Pinochet J, Campribí, A, Calvet C, Fernandez C, Rodriguez Cabana, R (1998) Inducing tolerance to the root-lesion nematode Pratilenchus vulnus by early mucorrhizal inoculation of micropagated Myrabolan 29C plum rootstock. Journal of the American Society for Horticultural Science, 123: 342–347.
    CrossRef
  5. Soil Survey Staff (1999) Soil Taxonomy: a basic system of soil classification for making and interpreting soil surveys, 2nd. ed. Government Printing Office (USDA, Handbook 436), Washington.
  6. Köppen WP, Geiger R (1939) Handbuch der Klimatologie. Gedruder Borntraeger, Berlin.
  7. Bergamaschi H, Guadagnin MR (1990) Agroclima da estação experimental agronômica/UFRGS. Departamento de Plantas Forrageiras e Agrometeorologia da UFRGS, Porto Alegre.
  8. Fachinello JC, Coutinho EF, Marodin GAB, Botton M, De Mio LLM (2003) Normas Técnicas e Documentos de Acompanhamento da Produção Integrada de Pêssego. Universidade Federal de Pelotas, Pelotas.
  9. Tedesco MJ, Gianello C, Bissani CA, Bohnen H, Volkweiss SJ (1995) Análises de solo, plantas e outros materiais (Boletim Técnico, 5), 2nd ed. UFRGS/Departamento de solos, Porto Alegre.
  10. Phillips JM, Hayman DS (1970) Improved procedure for clearing roots and staining parasitic and vesicular-arbuscular mycorrhizal fungi for rapid assessment of infection. Trans Br Mycol Soc, 55: 158-161.
    CrossRef
  11. Nemec S (1992) Glomus intraradix effects on citrus roostock seedling growth in various potting media. Journal of Agricultural Science, 118: 315-323.
    CrossRef
  12. Gedermann JW (1955) Relation of a large soil-borne spore to phytomycetous mycorrhizal infections. Mycologia, 47: 619-632.
    CrossRef
  13. Gedermann JW, Nicolson TH (1963) Spores of mycorrhizal Endogone extracted from soil by wet sieving and decantinf. Trans. Br. Mycol. Soc., 46: 235-244.
    CrossRef
  14. Jenkins WR (1964) A rapid centrifugal-flotation technique for separating nematodes from soil. Plant Dis. Rep., 48: 692.
  15. Schenck NC, Perez Y (1998) Manual for the identification of VA mycorrhizal fungi, 2nd edn. Synergistic, Gainesville, Fla.
  16. Marschner H (1995) Mineral nutrition of higher plants. 2 ed. Academic Press, San Diego.
  17. Silveira APD (2000) Avaliação de fungos micorrízicos arbuscurlares e sua importância ambiental. In: Frighetto RTS, Valari PJ (eds.) Manual técnico: Indicadores biológicos e bioquímicos da qualidadedo solo. Embrapa, Jagariúna, pp. 61-77.
  18. Jordan NR, Zhang J, Huerd S (2000) Arbuscular-mycorrhizal fungi: potential roles in weed management. Weed Research, 40: 397-410.
    CrossRef
  19. Boddington CL, Dodd JC (2000) The effect of agricultural practices on the development of indigenous arbuscular mycorrhizal fungi. I. Field studies in an Indonesian ultisol. Plant and soil, 218: 137-144.
    CrossRef
  20. Oliveira AAR, Sanders FE (1999) Effect of manegement practices on mycorrhizal infection, growth and dry matter partitioning in field-grow bean. Pesquisa Agropecuária Brasileira, 34: 1247-1254.
    CrossRef
  21. Focchi SS, Dal Soglio FK, Carrenho R, Souza PVD, Lovato PE (2004) Fungos micorrízicos arbusculares em cultivos de citros sob manejo convencional e orgânico. Pesquisa Agropecuária Brasileira, 39: 469-476.
    CrossRef
  22. Eriksson A (2001) Arbuscular mycorrhiza in relation to management history, soil nutrients and plant species diversity. Plant Ecology, 155: 129-137.
    CrossRef
  23. Sanders IR, Koide RT, Shumway DL (1995) Community-level interaction between plants and vesicular-arbuscular mycorrhizal fungi. In: Varma, A; Hock, B (eds.) Mycorrhiza: structure, function, molecular biology and biotechnology. Springer-verlag, New York, pp. 609-621.
    CrossRef
  24. Moraes YJB (1995) Forrageiras: conceitos, formação e manejo. Editora Metrópole, Guaíba .
  25. Kurle JE, Pfleger RL (1994) The effects of cultural practices and pesticidas on VMA fungi. In: Pfleger JE, Linderman RG (eds.) Mycorrhizal and plant health. The American Phytopathological Society, St. Paul, pp. 101-131.
  26. Graham JH, Leonard RT, Menge JA (1981) Membrane-mediated decrease in root exudation responsible for phosphorus inhibition of vesicular-arbuscular mycorrhiza formation. Phant Physiology, Rockville, 68: 548-552.
    CrossRef
  27. Miller RL, Jackson LE (1998) Survey of vesicular-arbuscular mycorrhizae in lettuce production in relation to management and soil factors. The Journal of Agricultural Science, 130: 173-182.
    CrossRef
  28. Franke-Snyder M, Douds Junior DD, Galvez L, Phillips JG, Wagoner P, Drinkwater L, Morton JB (2001) Diversity of communities of arbuscular mycorrhizal (AM) fungi present in conventional versus low-input agricultural sites in eastern Pennsylvania, USA. Applied Soil Ecology, 16: 35-48.
    CrossRef
  29. Siqueira JO, Colozzi-Filho A, Oliveira E (1989) Ocorrência de micorrizas vesicular-arbuscular em agro e ecossistemas do Estado de Minas Gerais. Pesquisa Agropecuária Brasileira, 24: 1499- 1506.
  30. Johnson NC (1993) Can fertilization of soil select less mutualistic mycorrhizae? Ecological Application, 3: 749-757.
    CrossRef
  31. Clark RB (1997) Arbuscular mycorrhizal adaptation, spore germination, root colonization, and host plant growth and mineral acquisition at low pH. Plant and soil, 192: 15 – 22.
    CrossRef
scroll to top