International Journal of Agronomy
Volume 2018 (2018), Article ID 5294295, 6 pages
https://doi.org/10.1155/2018/5294295

Research Article

Colonization and Spore Richness of Arbuscular Mycorrhizal Fungi in Araucaria Nursery Seedlings in Curitiba, Brazil

Carlos Vilcatoma-Medina,¹ Glaciela Kaschuk,² and Flávio Zanette¹

¹Programa de Pós-Graduação em Agronomia-Produção Vegetal, Departamento de Fitotecnia, Federal University of Paraná, Curitiba, PR, Brazil
²Programa de Pós-Graduação em Ciência do Solo, Departamento de Solos e Engenharia Agrícola, Federal University of Paraná, Curitiba, PR, Brazil

Correspondence should be addressed to Carlos Vilcatoma-Medina; carlos.vilcatoma@ufpr.br

Received 19 October 2017; Revised 19 January 2018; Accepted 5 February 2018; Published 1 April 2018

Academic Editor: Mathias N. Andersen

Copyright © 2018 Carlos Vilcatoma-Medina et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

Araucaria or Paraná pine [Araucaria angustifolia (Bertol.) Kuntze, 1898] is an endangered timber tree species of Atlantic Forest that naturally forms symbiosis with arbuscular mycorrhizal fungi (AMF). The objective of this experiment was to evaluate AMF colonization and spore AMF richness in araucaria seedlings produced in nursery at the metropolitan region of Curitiba, Brazil, with the interest of identifying a taxonomical AMF group. For that, soil and fine roots of 6-month-, 1-year-, 2-year-, 3-year-, and 5-year-old araucaria seedlings were sampled and evaluated. Evaluations indicated that araucaria seedlings were well colonized by AMF (with rates varying from almost 50 to over 85%) and produced an abundant number of mycorrhizal spores (from 344 to 676 spores per seedling). Samples contained spores of the species Acaulospora scrobiculata, Dentiscutata heterogama, and Glomus spinuliferum and unidentified species of genera Gigaspora and Glomus. The Glomus genus was the most abundant kind of AMF spores found under nursery conditions. Therefore, the experiment evidenced that Glomus is a promising genus candidate for being used as AMF inoculant in production of araucaria seedlings.

1. Introduction

Araucaria or Paraná pine [Araucaria angustifolia (Bertol.) Kuntze, 1898] is an endangered tree species of the Mixed Ombrophilous Forest, commonly known as “Mata das Araucárias,” located in southern and the southern east of Brazil and in portions of Argentina and Paraguay [1, 2]. The araucaria is a dioecious plant, and its propagation by seeds (pinhões) is conditioned to the existence of intraspecific genetic richness in natural habitat. The problem is that 97% of the Mata das Araucarias ecosystem has disappeared [3] and reminiscent araucaria trees are isolated from each other and may not form viable seeds. In addition, seeds are rich in carbohydrates and proteins may be consumed by wild animals and rapidly lose vigor when left on dry soil [4]. Reforestation by transplanting seed-formed seedlings is suitable strategy, but it takes too long before nursery seedlings reach adequate height for transplantation. Yet, adding fertilizer to the substrate to increase growth rates may result in lower root, shoot ratio, and consequently decrease the rates of survival in the field after transplantation.

Araucaria naturally establishes symbiosis with arbuscular mycorrhizal fungi (AMF) [4], in which the plant supplies photosynthates in exchange for competitive advantages of growth and survival [5–8]. Pioneer studies already reported AMF in fine araucaria roots [9]; however, it was only recently that the AMF has been considered as a strategy to increase araucaria growth under nursery conditions [10, 11]. In fact, the studies performed so far show two important facts: first, that araucaria is colonized by a large and diverse number of AMF species [10, 12]; and second that the araucaria positively respond to inoculation of some AMF species, both in high and low P supply [13]. However, we do not know precisely the most efficient and competitive AMF species under nursery seedling production [14].

Therefore, the objective of this experiment was to evaluate AMF colonization and spore AMF richness in nursery soil samples at the metropolitan region of Curitiba, Brazil, with the interest of identifying the most abundant taxonomical AMF groups that grow under those conditions.

2. Material and Methods

Araucaria seedlings were produced from seeds in the nursery of the Universidade Federal do Paraná, Curitiba (25°25′47′′S and 49°16′19′′W, 950 m), Brazil, under entirely random design, five replicates, and five treatments. The substrate used was a mixture of soil and organic residues (crop residues, organic compounds, and others) collected in the metropolitan area of the city. The experimental design was completely randomized, with five replications in each treatment. The seedlings were at the moment of harvesting, according to the respective treatments: 6-month, 1-year, 2-year, and 5-year old. Seedlings grew outdoors, under full light natural conditions, and were well watered during the whole period of experiment. The climate in the region is classified as Köppen Cfb [15] and the eventual climate events such as frost and storms did not damage any stage of plant growth.

Soil samples were submitted to chemical analyses, and the pH was measured in CaCl₂ 0.01 mol L⁻¹; Ca²⁺, Mg²⁺, and Al³⁺ were extracted with KCl 1 M; H⁺ + Al³⁺, with Ca(C₂H₃O₂)₂ 0.5 M; K⁺ and P, with the Mehlich-1 extractor; carbon (C), with the K₂Cr₂O₇ (Table 1).

Table 1: Chemical attributes of soils used in the nursery experiment with araucaria in Curitiba, Brazil.

Soil attribute
Seedling age

6 months
1 year
2 years
3 years
5-years

pH CaCl₂
5.5 ± 0.240
4.9 ± 0.081
5.5 ± 0.122
5.2 ± 0.173
4.3 ± 0.394

Al³⁺ (cmol/dm³)
0.0 ± 0.0
0.9 ± 0.176
0.0 ± 0.0
0.0 ± 0.042
2.7 ± 1.494

H + Al³⁺ (cmol/dm³)
5.1 ± 0.678
13.2 ± 1.327
7.4 ± 0.903
7.2 ± 0.537
13.9 ± 2.591

Ca²⁺ (cmol/dm³)
4.3 ± 0.221
6.1 ± 0.522
9.4 ± 0.685
7.1 ± 1.784
3.0 ± 1.338

Mg²⁺ (cmol/dm³)
1.8 ± 0.078
3.7 ± 0.355
4.3 ± 0.269
2.9 ± 0.930
1.6 ± 1.338

K⁺ (cmol/dm³)
1.1 ± 0.260
0.3 ± 0.151
1.0 ± 0.286
0.7 ± 0.443
0.2 ± 0.128

P (mg/dm³)
16.7 ± 5.390
78.2 ± 16.967
144.5 ± 16.408
87.5 ± 30.295
79.1 ± 42.421

C (g/dm³)
12.7 ± 3.457
85.3 ± 27.451
64.3 ± 11.419
46.7 ± 16.486
61.4 ± 55.447

pH measured in CaCl₂ 0.01 mol L⁻¹; Ca²⁺, Mg²⁺, and Al³⁺ extracted with KCl 1 mol L⁻¹; H⁺ + Al³⁺ extracted with calcium acetate 0.5 mol L⁻¹; K⁺ and P extracted with the Mehlich-1 extractor; C determined with K₂Cr₂O₇.

Mycorrhizal spores were extracted with minor modifications with the procedures of [16, 17] as follows: 100 g of soil sample was suspended in 100 ml and left resting for 60 min; soil suspensions were liquefied for 10 s and sequentially sieved through 500 and 53 μm mesh sieves; spores were recovered in tubes with 70% sucrose solution and centrifuged for four min twice and then sieved for 250 and 50 μm mesh sieves. Spores with similar morphology were assembled; then, they were spread on microscope slide and treated with polyvinyl alcohol-lactic acid-glycerol [18] and the Melzer reagent [19]. Spores were individually identified under microscope (Primo Star/Zeiss) according to the morphological characteristics using the criteria of taxonomical classification proposed by Invam [20].

Root fragments were preserved in lactoglycerol (lactic acid, glycerol, and water in the proportion 1 : 2 : 1) before measurements. The rates of mycorrhizal colonization were estimated by observing cleared and dyed root fragments under microscope (Stemi 305/Zeiss), considering a grid of 1 cm × 1 cm [21], with minor modifications, as follows: fine roots were soaked in KOH 10% at room temperature during 24 hours and then, in water bath at 80°C for an hour; roots were sequentially washed with H₂O₂ 100% and water twice and dyed with blue-pen ink in water bath at 80°C for five minutes.

Variance analyses and mean comparisons considered the statistical design of entirely random design, five replicates, and five treatments. Redundancy analyses were performed with Canoco for Windows 4.5 package 43, considering the abundance of spore taxonomic group and chemical attributes as the explanatory variables for the differences between the treatments.

3. Results

Araucaria seedlings with ages between 6 months and 5 years produced under nursery conditions in Curitiba were well colonized by AMF (rates varying from almost 50 to over 85%; Figure 1) and contained an abundant number of mycorrhizal spores (varying from 344 to 676; Table 2). Samples contained spores of the species Acaulospora scrobiculata, Dentiscutata heterogama, and Glomus spinuliferum and of four unidentified species of the genera Gigaspora (one species) and Glomus (four different species).

Table 2: Mean number of mycorrhizal spores of araucaria seedlings with ages between 6 months and 5 years grown in a nursery field in Curitiba, Brazil.

Mycorrhizal fungal species
Seedling age (year)

6 months
1 year
2 years
3 years
5 years

Acaulospora scrobiculata
13
46
44
70
33

Dentiscutata heterogama
11
16
15
17
15

Gigaspora sp.
9
29
8
12
11

Glomus spinuliferum
31
114
53
129
118

Glomus sp. 1
40
28
40
62
34

Glomus sp. 2
91
142
55
161
141

Glomus sp. 3
101
187
82
111
176

Glomus sp. 4
48
153
57
73
148

Total of species
344
715
355
635
676

Means followed by the same letter in the lines do not differ by the Tukey test at .

Figure 1: Root arbuscular mycorrhizal fungi (AMF) colonization araucaria seedlings with ages between 6 months and 5 years grown in a nursery in field in Curitiba, Brazil. Means followed by the same letter are not significantly different according to Tukey’s test (). The error bars represent the standard error of the mean. .

Mycorrhizal fungi colonization increases from 40 to around 80% in seedlings of 6 months–1 year old. From 1 year onwards, regardless of chemical differences in the soil used, rates of AMF colonization remained at levels of 80% over the years. At first sight, there was a trend in which older seedlings (3- and 5-year old) contained more spores than younger (e.g., 6 months and 2 years old) seedlings, but because 2-year old araucaria seedlings contained the largest number of spores, age was not the main factor affecting the number of spores in this experiment.

The dominant AMF species in the 6-month, 1-year, 2-year, and 5-year old seedlings was Glomus sp. 3 and in the 3 years old seedlings, it was Glomus sp. 2 (Table 2). The least abundant spores belonged to the family Gigasporaceae (Dentiscutata heterogama and Gigaspora sp.), and their numbers did not differ between treatments.

Redundancy analyses showed that AMF spore richness in 6-month old seedlings was not affected by soil chemical attributes, but it was so in older seedlings (Figure 2). Attributes related to potential soil acidity (Al⁺ and H+Al⁺) grouped AMF species Glomus sp. 3, Glomus sp. 4, and Gigaspora sp. Attributes related to good soil fertility (Ca, Mg, and P) grouped mycorrhizal fungi species Glomus sp. 1, Dentiscutata heterogama, Acaulospora scrobiculata, and Glomus sp. 1 (Figure 2).

Figure 2: Redundancy analyses with several species of arbuscular mycorrhizal fungi in relation to chemical soil attributes in soil used to produce araucaria seedlings in a nursery of Curitiba, Brazil. Note: Ascr: Acaulospora scrobiculata; Dhtg: Dentiscutata heterogama; Ggsp: Gigaspora sp.; Glof: Glomus spinuliferum; Glo1: Glomus sp. 1; Glo2: Glomus sp. 2; Glo3: Glomus sp. 3; Glo4: Glomus sp. 4.

4. Discussion

Perennial plants with slow growth like araucaria are not commonly taken into long-term experiments involving AMF because of the obvious difficulty of waiting for a long time for the first results (e.g., compared to annual crops) and also because araucaria is not the first choice of reforestation by companies. Therefore, although AMF colonization has been studied long ago [9], our experiment demonstrated that AMF colonization occurs under nursery conditions to seedlings from very young age up to 5-year old seedlings, without systematic inoculation and regardless of chemical soil attributes (Figure 1; Table 1). This implies that, in addition to field natural conditions [10, 22], araucaria seedlings are also benefited from AMF colonization under nursery conditions.

A great limitation in the application of AMF symbiosis is the fact that we do not have established recommendations of which AMF species are better adapted to nursery and field conditions. Previous studies indicated that araucaria is capable of supporting AMF symbiosis with a greater number of different fungal species [11, 22–25] than that we found in this experiment. To date, araucaria AMF spore richness varied from 8 [23] to 13 [11] in forests of the State of Rio Grande do Sul and from 26 [24] to 58 [25] in forests of Sao Paulo. The variation in spore AMF richness has been frequently attributed to heterogeneity in soil habitat and to the variable capacity of AMF species to adapt to climate and soil in different regions [10, 13]. Therefore, although the AMF richness is great under field conditions, only few species are probably well adapted to nursery conditions.

The genus Glomus represented 86% of the spores analyzed in our experiment (Table 2). Previously, it was observed that this genus represented between 40 and 60% of AMF spores in forests in the State of Sao Paulo [10, 22]. In fact, soil acidity associated with exchangeable soil Al (Al⁺) may affect spore germination, growth of germinative tube, hyphae, and root [26]. Furthermore, concentrations higher than 100 μm Al⁺ affect sporulation of certain species [27]. In this experiment, potential acidity determined by high concentrations of Al⁺ and H + Al⁺ was associated with Glomus sp. 3 and Glomus sp. 4 (Figure 2). The Glomus genus is the most commonly found and probably the most adapted AMF to Brazilian acidy soils [28, 29]. This dominancy indicates that Glomus is highly competitive among native spores and it has a high reproductive capacity [10].

The Acaulospora genus was the second most abundant AMF spore in the experiment (Table 2), corroborating with the fact that the Acaulospora AMF has been found in moderate acidy soils (pH lower than 6.2) [30] and very acidy forest soils [24]. The least abundant genus in this experiment belonged to the genus Gigaspora (Table 2). Gigaspora has been associated with moderate acidy soils and high levels of phosphate availability [13, 14]. In our experiment, however, Gigaspora was not related to phosphate but it was slightly associated with potential soil acidity (Al⁺ and H + Al⁺; Figure 2).

The traditional paradigm describes regulation of AMF symbioses in relation to phosphate availability, in which plants suppress AMF colonization once phosphate is available in enough quantities for being taken from the soil solution. However, this paradigm neglects some aspects of AMF physiology. Reference [31] gave evidence that after the AMF has colonized root wheat (Triticum aestivum L.) plants, it does not let it down, even if phosphate is available in enough quantities. It does not imply necessarily that AMF is always efficient regardless of P availability. In fact, P availability determines different AMF compositions and, therefore, different AMF efficiencies [32]. Earlier studies than that of [31] demonstrated that plant growth responses to AMF inoculation under low and high phosphate availability depend very much on the dominant AMF [33]. In that aspect, the genus Glomus had a much greater phosphate uptake efficiency than Gigaspora [33]. Interestingly, greater efficiency of Glomus over Gigaspora (increased mycorrhizal dependence of plants) was also measured on araucaria seedlings produced with 150 mg dm⁻³ soil of phosphate fertilizer [14]. Previous studies indicated that mycorrhizal colonization occurs when plants are grown in soils that contain less than 40 mg dm⁻³ [32]. In the present study, the substrate contained 62 mg of P dm⁻³, and even so Araucaria seedlings were well colonized by mycorrhizae, especially with the genus Glomus. This is an observation that should derive more research in our group.

Considering the greater abundance of Glomus in relation to other genera, our experiment suggested that other studies should search within Glomus diversity to identify AMF inoculants that promote growth of araucaria seedlings. The next step is selecting strains, checking for consistent plant growth responses, and evaluating the viability in inoculant production at commercial scale. As Glomus was not related to P soil concentrations in soil samples (Figure 2), it is important that selection occurs under reasonable soil chemical conditions. As a matter of fact, it has been shown that AMF symbioses may be favored by better plant growth [34] and high potential acidity (high Al⁺) inhibits root growth, damages cellular structure, and hampers water and nutrient [35, 36].

5. Conclusions

Araucaria seedlings are intensively colonized by AMF at least until the age of 5 years old, even when they are not systematically inoculated with specific AMF strains.

Glomus genus is the most abundant kind of AMF spores found under nursery conditions, and therefore other studies should search within Glomus diversity to identify AMF inoculants that promote growth of araucaria seedlings.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

Acknowledgments

Authors thank Dr. Celso Auer, Dr. Sidney Stürmer, and Dr. Raul M. Cesar, respectively, for the suggestions on the experimental setup, training on spore identification, and statistical analyses. Carlos Vilcatoma-Medina received a CAPES (Coordenação de Aperfeiçoamento de Pessoal de Nível Superior) scholarship to pursue his Ph.D. studies.

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