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First report of Apiognomonia errabunda on Quercus ilex in Algeria


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Introduction

The holm oak (Quercus ilex) is a typical Mediterranean sclerophyllous species, dominating woody vegetation and occupying large areas, especially in the western part of the Mediterranean basin. This Fagaceae species is noted for its remarkable adaptive potentialities (Barbero and Loisel 1980; Barbero et al. 1992). Variability of Q. ilex populations was the subject of several investigations; in fact, Albert and Jahandiez (1908) described 31 varieties, but currently two morphotypes are recognized: Q. ilex and Q. rotundifolia Lam., which differ morphologically at the foliage level (veins number) (Saenz De Rivas 1967, 1970) vigour and shape (Barbero et al. 1992).

In Algeria in the 1950s, holm oak occupied an estimated area of approximately 700,000 ha (Boudy 1955) but had declined by the early 1980s to 354,000 ha (Dahmani-Megrerouche 2002). In the Belezma and the Aures mountains of eastern Algeria, Q. ilex is considered the main tree in the forest landscape, often associated with Pinus halepensis Mill., Juniperus oxycedrus L. and Fraxinus xanthoxyloides (G.Don) Wall. ex A.DC. in the semi-arid zones, with Cedrus atlantica (Endl.) Manetti ex Carrière in the subhumid zones situated on middle and high altitudes and with Juniperus phoenicea L. and J. oxycedrus on degraded lands influenced by the Sahara bioclimatic regime.

In recent years, natural events such as drought and irregular precipitation, anthropogenic actions (fires, overgrazing, and over-exploitation) have negatively affected Q. ilex forests in these regions. In addition, unusual development of the vegetation cover dominated by this species has been reported in Belezma, particularly in sites formerly occupied by C. atlantica, which had declined rapidly (Bensaci et al. 2015). In this situation, certain diseases and pests have increased greatly including anthracnose caused by Apiognomonia errabunda (Roberge ex Desm.) Höhn. (anamorph = Discula quercina (Westend.) Arx), known on Quercus species in the Mediterranean region (Morelet 1989; Ragazzi et al. 1999; Ragazzi et al. 2007; Linaldeddu et al. 2009).

Several studies highlighted the links between the aetiology of this disease and the trophic behaviour of the causal fungus, switching between the endophyte and pathogenic phase, as well as the phytosanitary state of the oak forests (Ragazzi et al. 2007; Moricca et al. 2012). Based on recent observations (2010 to 2016) in Belezma National Park, anthracnose in Q. ilex spread in parallel with recent outbreaks of the gall-forming mite Aceria ilicis Canestrini, which causes deformation, overgrowth, and browning of leaves, shoots, and inflorescences (Stork and Wüest 1996; Karioti et al. 2011).

The objectives of this work were to evaluate the extent of anthracnose on Q. ilex in the Belezma massif through the quantification of foliar symptoms, to determine the geographical variability of disease symptoms, and the influence of twig orientation and leaf position on twigs on the intensity of symptoms. To date, no studies have been conducted on the aetiology of this disease in North Africa.

Material and methods
Study areas

Four sites were examined: Bordjem, Tougurt, Ain Ali and Chelaâlaâ (Fig. 1). Leaves of Q. ilex showing typical symptoms of anthracnose (Morelet 1989; Moricca and Ragazzi 2011) were sampled at each site (Fig. 2). Each twig was subdivided into apical or distal (AP) and non-apical (NAP) parts. Twigs were sampled from four cardinal directions (North, South, East and West). Leaves were stored in paper bags for transfer to the laboratory.

Figure 1

Map depicting the study sites situated in Belezma National Park: BRG: Bordjem, TUG: Tougurt, CHL: Chelaâlaâ, AAL: Ain Ali

Figure 2

Leaves of Q. ilex showing characteristic brown-necrosis caused by D. quercina

Evaluation of anthracnose symptoms on Quercus ilex

The severity of the symptoms on the leaves was determined by direct quantification of the necrotic areas. The leaves were glued on to A4 white paper and scanned at 700 dpi resolution (Epson Perfection V370, Seiko Epson Co.). The scan was performed against a background of white light to maximize the contrast of the object before processing images with ImageJ software (Abràmoff et al. 2004; Ferreira and Rasband 2012). The resulting images were calibrated in mm against a ruler placed in the background. Image files were saved in TIFF format and analysed in the RGB (Red-Green-Blue) scale. A reference line (20 mm) was drawn to standardize the dimensions to the ruler and the object, and the set scale menu activated to set the measurement unit. Using the colour thresholds extraction method, selected necrotic areas of the leaf blade were extracted and measured (mm2).

Disease severity index (DSI) was determined as the ratio between the percentage of necrotic leaf area (%) and the corresponding severity scale (Horsfall and Barratt 1945; Nutter et Esker 2006), as follows:

DSI = (Σ Xi.ni / R Nt) x 100, here Xi: disease severity (scale score), ni: leaf number with i severity, R: the highest score of the scale and Nt: the total number of examined leaves.

Since the sampling of symptomatic leaves was based on the orientation of the twigs and the position of the leaf (insertion point) on, severity was also considered in relation to these two parameters.

Pathogen isolation and identification

To isolate and identify the causative agent, leaves were surface-sterilized in 10% H2O2 for 1 5 m in followed by threefold rinsing in sterile distilled water (Ragazzi et al. 2001). After sterilization, the leaves were dried on sterile filter paper and aseptically cut into small square pieces (5 mm2) containing for each both necrotic and non-necrotic areas. Leaf pieces were placed on malt extract agar (MEA), as 5 pieces per Petri dish incubated at 24°C for one week, with daily observations to characterize the appearance of hyphae giving the fungal colonies. Mycelium was identified on morphological traits (Hughes 1953; Monod 1983; Ellis and Ellis 1997; Sogonov et al. 2008). Characterization of morphotypes was based on macroscopic features including colony shape and colour (Ragazzi et al. 2000; Lacap et al. 2003). Once identified, the fungal cultures are subcultured by transferring to water agar (WA).

For molecular characterization, discs taken from three-week colonies were transferred to glass tubes of 15 ml WA. Tubes were incubated at 24°C. After 15 days, the purity of emerging colonies was tested according to Smith and Onion (1994). Subsequently, the mycelium was scraped from the agar surface and crushed on a sterilized stainless steel support. The crushed materials were placed in previously autoclaved glass tubes, alternating with layers of microgranules of autoclaved silica gel (Smith and Onion 1994). Tubes were sealed and stored at 4°C. Three days after, the crushed mycelia were recovered and resuspended in glass Petri dishes containing potato dextrose agar (PDA), then incubated at 26°C for 15 days, before subculturing to Erlenmeyer flasks containing 100 ml of potato dextrose broth. The flasks were incubated with shaking at 250 rpm at 25°C for one week prior to DNA extraction.

DNA extraction was performed according to Lee and Taylor (1990) using Tris-HCl (50 mM), EDTA (50 mM), 3% SDS, 1% 2-mercaptoethanol, chloroform-TE-saturated phenol 1:1 (v/v), NaOAc (3M)/pH: 8.0; isopropanol, and 70% ethanol as lysis buffer. PCR was carried out according to White et al. (1990), using ITS1, 5.8S and ITS2 regions (White et al. 1990; O’Donnell et al. 2000).

The sequences of the used primers were 5’-TCCGTAGGTGAACCTGCGG-3’ (ITS1) and 5’-TCCTCCGCTTATTGATATGC-3’ (ITS4) (White et al. 1990; O’Donnell et al. 2000).

Amplification cycles were carried out in a ProFlexTMPCR System (Applied Biosystems), with initial denaturation at 94°C (15 min) followed by three repeated phases (35 times): denaturation at 94°C for 2 min; annealing at 55°C for 1 min and elongation at 72°C for 3 min. A final elongation step of 72°C for 5 min was included. PCR products were examined on a 1% agarose gel in Tris-borate-EDTA buffer. DNA purification was carried out using the QiaQuick Gel Extraction kit (Qiagen, Germany). The product was stored at –20°C before sequencing.

Sequencing of the amplified fragments was performed in an ABI-Prism 373A DNA sequencer (Applied Biosystems) with enzymatic lysis and neo-amplification using the Big Dye Xterminator purification Kit (Applied Biosystems). Sequences were aligned using Bioedit Sequence Alignment Editor 7.0.0. (Hall 1999) and compared with those available in GenBank using BLAST search (http://blast.ncbi.nih.gov)

Statistical analyses

For phylogenetic analyses, multiple sequence alignment was performed including the genomic sequences of fungal isolates from the present study, compared with related mycotaxa in the Gnomoniaceae and Diaporthales using the ClustalW algorithm. The phylogenetic dendrogram was elaborated using MEGA 7.0 (Kumar et al. 2016) implying a Neighbour-joining statistical method. Evolutionary distances were computed using the Jukes-Cantor model (Yarza et al. 2017). The test adopted for phylogenetic analysis was the Bootstrap method with 1000 replicates. Statistical analyses were performed using XLSTAT 2014.5.03 (Addinsoft-Microsoft).

Results
Disease symptoms on leaves of Quercus ilex

Digital image analyses of the symptomatic leaves of Q. ilex allowed characterizing the severity of anthracnose (Tab. 1).

Mean severity (%) calculated for each sites according to digital image analyses of Q. ilex leaves affected by anthracnose

Sites Number of sampled trees Number of sampled leaves Severity (%) Severity index Horsfall-Barratt Scale
Bordjem 10 374 21.85 ± 0.18 b 0.10 3.99 ± 0.18
Tougurt 10 350 34.52 ± 0.15a 0.13 4.76 ± 0.15
Chelaâlaâ 10 396 21.96 ± 0.17b 0.11 4.01 ± 0.17
Ain Ali 10 319 13.66 ± 0.22c 0.03 3.03 ± 0.22

Values represent means ± SE. Means followed by the same letter(s) within the same column are not significantly different (α = 0.05) according to LSD Fisher test.

Anthracnose severity varied according to the site. The most intense severity was recorded in the leaves sampled from Tougurt (34.52%), followed by Chelaâlaâ and Bordjem, with 21.96% and 21.85’, respectively, while the leaves sampled from Ain Ali were recorded with severity of 13.66% (P < 0.0001) (Tab. 1). Severity index and the Horsfall-Barratt (HB) scale also differed according to the site. The most important severity index was recorded for Tougurt (0.13), unlike Ain Ali with a minimum scale of 0.03 (Tab. 1).

Severity was greater in the south-facing twigs for all the sites (Tab. 2), while minimum values were recorded for the west-facing twigs (Tab. 2).

Variability of anthracnose severity (%) on leaves of Q. ilex according to the orientation of twigs

Twig orientation Bordjem Tougurt Chelaâlaâ Ain Ali
East 20.61 ± 0.39ab 31.56 ± 0.32b 21.51 ± 0.35ab 12.63 ± 0.38b
West 18.35 ± 0.40b 26.80 ± 0.34b 17.53 ± 0.38b 9.79 ± 0.38b
North 20.53 ± 0.34ab 26.64 ± 0.34b 19.36 ± 0.64b 13.87 ± 0.51ab
South 25.79 ± 0.31a 43.87 ± 0.24a 26.08 ± 0.28a 21.60 ± 0.48a
P 0.0773 <0.0001 0.0075 0.0093

Values represent means ± SE. Means followed by the same letter(s) within the same column are not significantly different (α = 0.05) according to LSD Fisher test.

Regarding leaf position on a twig, we have found that anthracnose severity was more prominent apical leaves compared to non-apical leaves except for those sampled from Ain Ali (Tab. 3).

Severity (%) variation of Q. ilex anthracnose according to leaf position on twigs

Bordjem Tougurt Chelaâlaâ Ain Ali
NAP 20.02 ± 0.22b 32.93 ± 0.21a 21.55 ± 0.23a 14.08 ± 0.28a
AP 25.43 ± 0.63a 36.34 ± 0.22a 22.43 ± 0.25a 13.07 ± 0.33a
P 0.0193 0.1347 0.6597 0.6916

Values represent means ± SE. Means followed by the same letter(s) within the same column are not significantly different (α = 0.05) according to LSD Fisher test. NAP: non-apical leaves, AP: apical leaves.

Fungal isolation

The causal agent of anthracnose was isolated in all leaf samples in the anamorphic form and identified under species level as Apiognomonia errabunda. 35 isolates distributed over five morphotypes were characterized from 330 leaf pieces (Tab. 4, Fig 3).

Figure 3

Apiognomonia errabunda cultures on MEA medium. (A) AECS3 isolated from Chelaâlaâ. (B) AETS2 isolated from Tougurt. (C) AEBS5 isolated from Brdjem. (D) AEAN6 isolated from Ain Ali

Cultural characteristics of the 35 D. quercina isolates on MEA medium

Site Isolates Morphotype Sporulation Acervuli (Diam mm) CUps CLws Shape ConidiaL (μm) ConidiaW (μm)
Bordjem DQBS1 M1 S 37.00 LB LB Circular 9.00 5.00
DQBS2 M1 S 39.33 LB LB Circular 11.00 3.00
DQBS3 M1 S 47.00 LB LB Circular 9.00 3.00
DQBS4 M1 S 41.67 LB LB Circular 10.00 4.00
DQBS5 M3 S 41.00 LB LB Circular 9.00 3.00
DQBS6 M5 S 40.00 LB LB Circular 6.00 4.00
DQBN1 M5 NS 40.67 LB LB Circular n/a n/a
Tougurt DQTS1 M1 S 45.67 LB LB Circular 7.00 3.00
DQTS2 M1 S 43.33 BG LG Circular 8.00 3.00
DQTS3 M1 S 41.67 BG LG Circular 6.00 3.00
DQTN1 M1 NS 39.67 LB LB Circular n/a n/a
DQTS4 DQTN2 M2 M2 S S – – 45.33 44.00 LB LB LB LB Circular Circular 8.00 7.00 5.00 3.00
DQTS5 M2 S 46.67 LB LB Circular 8.00 2.00
DQTN3 M3 S 40.00 LB LB Circular 8.00 4.00
DQTN4 M3 NS 41.67 LB LB Circular n/a n/a
DQTS6 M5 S 47.67 LB LBCC Circular 9.00 3.00
Chelaâlaâ DQCN1 M1 NS 41.33 BG LG Circular n/a n/a
DQCS1 M3 S + 43.67 LB LB Circular 7.00 4.00
DQCS2 DQCS3 M4 M5 S S – – 43.67 43.33 LB BG LB LG Circular Circular 9.00 8.00 3.00 4.00
DQCS4 M5 S 42.67 LB LB Circular 9.00 3.00
DQCS5 M5 S 39.00 LB LB Circular 9.00 4.00
Ain Ali DQAN1 M1 S 33.00 LB LB Circular 11.00 3.00
DQAN2 M1 S 42.33 LB LB Circular 11.00 4.00
DQAN3 M4 S + 43.33 LB LB Circular 9.00 3.00
DQAS1 M1 S 35.33 LB LB Circular 8.00 4.00
DQAS2 M1 S 45.67 LB LBCC Circular 8.00 3.00
DQAS3 DQAN4 M1 M1 S NS – – 41.00 41.33 LB LB LB LB Circular Circular 9.00 n/a 4.00 n/a
DQAN5 M1 S + 49.67 BG LG Circular 6.00 3.00
DQAS4 M2 S + 50.00 BG LG Circular 7.00 3.00
DQAN6 M2 NS 46.00 LB LB Circular n/a n/a
DQAS5 M3 S 40.00 LB LB Circular 7.00 3.00
DQAS6 M3 S 50.67 LB LB Circular 7.00 4.00

CSup: colony color in the upper side of Petri dish. CLws: colony color in the lower side of Petri dish. ConidiaL: conidia length. ConidiaW: conidia width. n/a: not-applicable. NS: non-sporulating isolate. S: sporulating isolate. (+) presence. (-) absence. LB: light brown. BG: brownish-gray. LBCC: light brown with gray concentric circles. LG: light gray.

Morphological characterization

All the fungal colonies have a circular shape. After 15 days of growth at 25°C on MEA, colony diameters in Tougurt isolates averaged 43.57 mm; those of Bordjem have an average diameter of 40.95 mm. For Chelaâlaâ isolates, mean colony diameter was 42.28 mm and 43.19 mm for Ain Ali isolates (Tab. 4).

Colonies’ colour was usually light brown on both sides of the Petri dish, brownish-grey on the upper side and light grey on the underside, or light brown on the upper side and light-brown on the upper side with grey concentric circles on the lower side (Tab. 4). Conidia were ellipsoid, one-celled, 3.30–3.58 μm x 7.50–8.86 μm. Acervuli could not be detected, except in some isolates where they were spherical and grouped in clusters of 2 to 4.

Phylogenetic analyses

The identification of A. errabunda species by molecular characterization was confirmed by comparing ITS sequences against GenBank accessions (Tab. 4). The database search yielded two strains: MH111403 with approximately 613 bp and MG594496 with approximately 595 bp. The two sequences were deposited at GenBank. The MH111403 had ITS similarity of 99% with sequences of A. errabunda isolated from Quercus pubescens in Italy (GQ452265, GQ452259). The phylogenetic tree showed isolates MH111403 and MG594496 together in a single clad (Fig. 4).

Figure 4

Phylogenetic tree (rDNA ITS) of A. errabunda including the two isolates from Q. ilex in Belezma National Park. Dendrogram was elaborated implying the Neighbor-Joining method based on the Jukes-Cantor model. The bootstrap tree inferred from 1000 replicates (The optimal tree with the sum of branch length = 0.62132144). Two accessions of Ophiostoma novo-ulmi were considered in this tree as out-group taxa

Discussion

Prospection of the five sites in the Belezma massif has shown a considerable incidence of anthracnose in Q. ilex. The incidence of A. errabunda was determined for several Quercus spp. In Tuscany region (Italy), the incidence of anthracnose Q. pubesens Willd. was a recorded level of 15% to 20% (Moricca and Ragazzi 2011). In Italian oaks, the incidence of anthracnose was characterized by interannual variability: during the 1990s, it was particularly high among Fagaceae in mixed oak sites: (Quercus/Fagus; Quercus/Castanea and Quercus/ Ostrya) to a lesser degree in sites with monospecies or scattered oak trees (Ragazzi et al. 2007). While pathogenicity of this fungus was determined experimentally on several Quercus species (Hecht-Poinar and Parmeter 1986; Hanifeh et al. 2018).

The incidence of oak anthracnose is largely dependent on climatic conditions during the vegetative and reproductive growth seasons, including rainfall, spores-carrying winds, high temperatures, and humidity. In Italy, anthracnose was almost present in the southern parts; in Sicily, to regions with temperate Mediterranean conditions as for Tuscany (Moricca and Ragazzi 2008). While causal fungus was repeatedly isolated as an endophyte from several Fagaceae and more specifically Quercus spp. (Moricca and Ragazzi 2008), A. errabunda is one of the associated pathogens with recent decline phenomenon of oaks, as infection levels in declining trees far exceeded those recorded in healthy asymptomatic trees (Ragazzi et al 2003; Moricca and Ragazzi 2008). The causal fungus of anthracnose shares the same etiological characteristics compared to some endophytic fungi in that it can shift from asymptomatic (mutualistic) to the pathogenic symptomatic behaviour (La Porta et al. 2008).

Anthracnose severity was varied according to the site but more importantly in Tougurt, indicating that disease occurrence is probably dependent on certain site-related factors, which may include Q. ilex occurrence among tree species composition, age and its density. The calculated severity indexes indicate that holm oak was moderately sensitive for all studied sites, more particularly in Tougurt.

In terms of twigs direction, the severity of foliar symptoms was considerable for those exposed to the south. No work has addressed this parameter and its effect on the magnitude of anthracnose on Q. ilex. Infection occurs over a wide temperature range, but the leaves must be moistened for an extended period (Morelet 1989). We consider that a combination of leaf wetness during delayed spring rains and high temperatures, resulting in a prolonged time of twigs exposure to “energizing” effect of solar radiation leading to an amplified oak infection. The exceptional climatic conditions may influence not only the extent of oak infection by A. errabunda, but also the large-scale dissemination of the disease.

Our results prove that the most important severity was recorded in leaves inserted on the apical parts of twigs. It has been shown in several studies that foliar symptoms of anthracnose caused by fungi belonging to the genus Apiognomonia Höhn, Gloeosporium Desm. & Mont., and Gnomonia Ces. & De Not. were particularly concentrated in the distal leaves (Gregory and Redfern 1998). According to Morelet (1989), young organs are particularly susceptible to Apiognomonia quercina, especially on Q. bicolor Willd. and Q. macrocarpa Michx.

The asexual form of the causal agent of oak anthracnose (D. quercina) was described for the first time by Saccardo in 1884. This mycotaxon is commonly considered as a typical endophyte of the Mediterranean Fagaceae (Moricca and Ragazzi 2011). Colony growth on MEA suggests that A. errabunda respond by the same magnitude to the nutrient quality of the medium. According to the present work, the A. errabunda isolates from Q. ilex are less vigorous on cultures than other isolates characterized from Q. frainetto and Q. cerris by Ragazzi et al. (2000). Thus, host taxa may probably affect the growth potential of the fungus on synthetic medium (Toti et al. 1992).

The shape and colour of colonies are generally similar to that described by Moricca and Ragazzi (2011) on PDA as “very light-brown,” while conidia sizes are variable according to the geographical origin of the isolates.

In combination with the morphological data, the molecular characterization confirmed the identity of the causal agent as A. errabunda. The resulting ITS sequences of Belezma strains seem to be more related phylogenetically to those isolated from Q. cerris in Italy (Turco et al., unpublished data). We suggest expanding the geographical area of ​the sampled sites to check whether the populations of this fungus in North Africa are divergent or not compared to those of South European regions.

A. errabunda offers a typical example of the trophic behaviour shift of endophytes from mutualism or asymptomatic to the symptomatic pathogenetic aspect. If A. errabunda is considered as an element involved in Quercus decline (Bendixsen et al. 2015), it is necessary and essential to apply the best control strategies for anthracnose through reasonable silvicultural practices and preventive treatments if necessary, while giving importance to the climatic data that must be exploited by the forest manager in order to choose the appropriate timing of the intervention.

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