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ICEL. AGRIC. SCI. 25 (2012), 51-58

Effectiveness of five fungal isolates as mycorrhizal inoculants of seedlings

Úlfur Óskarsson

Agricultural University of , Reykir, IS-810 Hveragerði, Iceland ([email protected])

ABSTRACT Five fungal isolates were tested under nursery and field conditions as potential ectomycorrhizal inoculants for Downy birch () seedlings for a harsh site. Thirteen inoculum treatments, along with non-inoculated control seedlings, were randomly selected for the experiment. In the nursery, inocula- tion treatments were variably effective in enhancing mycorrhization and the inclusions of either Laccaria laccata, or terrestris into inoculum treatments increased mycorrhization. Mycorrhization increased seedling height and reduced seedling root collar diameter relative to seedling height. In the field, mycorrhization and the inclusion of L. laccata into inoculation treatments in the nursery had positive effects on seedling survival while the isolate diversity and the inclusion of Cadophora finlandica into inoculation treatments in the nursery had negative effects. Furthermore, the isolate diversity and the inclusion of T. terrestris into inoculation treatments in the nursery had negative effects on growth in the field. The results indicate that three of the isolates tested: Hebeloma velutipes, L. laccata and P. involutus, could potentially be used as mycorrhizal inoculants of birch seedlings for reclamation areas in Iceland, but further studies are needed.

Keywords: Container seedlings, Betula pubescens, , nursery, reclamation.

YFIRLIT Áhrif af smitun fimm svepprótamyndandi sveppa á birkiplöntur Svepprótamyndun fimm sveppastofna og áhrif þeirra á vöxt og lífslíkur birkiplantna (Betula pubescens) var könnuð í gróðrarstöð og á erfiðu uppgræðslusvæði. Þrettán tilviljunarvaldar smitmeðferðir voru prófaðar ásamt ósmituðum samanburðarplöntum. Svepprótamyndun í gróðrarstöð var breytileg eftir smitmeðferðum. Þær meðferðir sem ollu marktækt aukinni svepprótamyndun innihéldu ýmist Laccaria laccata, Paxillus involutus eða Thelephora terrestris. Vöxtur plantna jókst við aukna svepprót í gróðrarstöð. Eftir gróðursetningu juku svepprótamagn og meðferðir með L. laccata lifun, en Cadophora finlandica og fjölbreytni sveppa í upphaf- legum smitmeðferðum höfðu neikvæð áhrif. Fjölbreytni sveppasmits og smitmeðferðir sem innihéldu T. terrestris drógu úr sprotavexti plantna eftir gróðursetningu. Niðurstöðurnar sýna að þrír af þeim sveppastofn- um sem prófaðir voru: Hebeloma velutipes, L. laccata og P. involutus gætu komið til greina til að smita plöntur sem ætlaðar eru í landgræðsluskógrækt, en þörf er á frekari rannsóknum. 52 ICELANDIC AGRICULTURAL SCIENCES

INTRODUCTION nogaster tener Berk., Inocybe spp., Laccaria Mycorrhizal seedlings raised in forest nurser- spp., Lactarius spp., Leccinum spp., Paxillus ies generally have greater chances of becom- spp., Peziza spp., Ramaria spp., Russula spp., ing established in the field than those without Scleroderma spp., Thelephora terrestris Ehrh. mycorrhizae (Khasa et al. 2009). This is be- and Tricholoma spp. mycorrhizae with cause the mutualistic association forms an birch, (Dighton & Mason 1985, Atkinson essential root interface with the surrounding 1992). Of these, Hebeloma spp., Inocybe spp., soil. Systematic mycorrhizal management Laccaria spp., Paxillus involutus (Batsch) Fr. should, therefore, be a key part of forest - and T. terrestris are able to form ling production. This is possible to achieve if on young birch seedlings under unsterile con- the chemical and biological conditions in the ditions (Flemming 1985, Fox 1986). These rooting substrate are set to promote fungal fungi are commonly found in forest nurseries growth and mycorrhizal development in forest and are often used for inoculating forest seed- nurseries (Quoreshi & Timmer 1998, Óskars- lings. In addition, Cadophora finlandica son 2010). Ideally, seedlings leaving the (C.J.K. Wang & H.E. Wilcox) T.C. Harr. & nursery should be equipped with a of McNew is among numerous less known ecto- mycorrhizal fungi which offer functional bene- mycorrhizal fungi that can be common in for- fits both in the nursery and the field (Perry et est nurseries (Menkis et al. 2005). al. 1987). In the present study, five fungal isolates, The selection of fungal isolates (different belonging to five fungal that common- species or different strains within species) for ly form ectomycorrhizae with birch seedlings inoculation can influence growth and health of and were commercially available, were tested nursery seedlings and their subsequent field as potential mycorrhizal partners of birch dur- survival and growth (Stenström & Ek 1990, ing seedling production and after planting in Pera et al. 1999, Brundrett et al. 2005). Certain the field. The object of the study was to com- isolates are better suited than others for ham- pare the effectiveness of the fungi to increase pering root diseases or are better capable of mycorrhization in the nursery and to improve improving nutrient and water acquisition for seedling survival and growth after planting at a given tree species and conditions (Thomas et difficult reclamation site in Iceland. al. 1983, LeTacon & Bouchard 1986, Sousa et al. 2012). The fungal isolates chosen can also MATERIALS AND METHODS be very variable in their ability to form mycor- Four week old Downy birch seedlings (seed rhizae and to compete with each other under source Næfurholt, 64°00’ N, 19°53’W; eleva- the conditions in which the seedlings are grow- tion 132 m), a total of 210 , were trans- ing (Parlade et al. 1996, Jonsson et al. 2001). planted into 1.5 L pots, three seedlings per pot. This ability depends, at least partly, on the The potting substrate was local sedge peat fungal carbohydrate requirements. Plants can (source location: 64°00’N, 21°10’W) mixed control mycorrhizal colonization by control- with rhyolitic pumice (1 part pumice in 2 parts ling carbon allocation to short roots, depend- peat; pumice grain size 0.5-0.7 cm). The ac- ing on the efficiency of the symbionts (Hoek- idity of the substrate mixture was pH 5.2. sema & Kummel 2003). Thus, fungi with low Thirteen randomly chosen inoculation treat- carbohydrate requirements are often best suit- ments out of 21 possible arrangements of five ed for inoculation in forest nurseries. fungal isolates were tested in the experiment Theoretically, the choice of potential inocu- (Table 1). During transplanting into the pots, lants is large for each tree species, for ex- two millilitres of diluted ectomycorrhizal ino- ample, several fungi: Amanita spp., Boletus culum (1 part vegetative mycelium [- spp., Cenococcum spp., spp., Works Ltd., Sittingbourne, UK] in 4 parts tap Cortinarius spp., Hebeloma spp., Hyme- water; v:v) were injected into the planting FIVE FUNGAL ISOLATES 53

Table 1. Relative amounts of each fungal isolate and the resulting diversity of fungal isolates in each inocula- tion treatment. Inoculation treatments Isolates 1* 2 3 4 5 6 7 8 9 10 11 12 13 14 C. finlandica 0.5 0.33 0.33 0.33 0.33 H. velutipes 1 0.5 0.33 0.33 0.25 L. laccata 1 0.5 0.33 0.33 0.33 0.25 P. involutus 1 0.5 0.5 0.33 0.33 0.33 0.33 0.25 T. terrestris 0.5 0.5 0.5 0.33 0.33 0.25 Isolate diversity 0 1 1 1 2 2 2 2 3 3 3 3 3 4 * Non-inoculated control seedlings holes, a method adapted from Boyle et al. g L-1 P and 0.40 g L-1 K. Every day the pots (1987). A few seedlings, not included in the were watered with the nutrient solution, study, were also inoculated with each of the through a drip watering system, until the field isolates separately for examination of ectomy- capacity of the potting mixtures was exceeded corrhizae. Non-inoculated seedlings served as and excess water seeped through the underside controls. The isolates tested included Hebe- drain holes of the pots. loma velutipes Bruchet (isolate PW Hv1; Each pot represented one treatment unit, rep- belonging to the H. crustuliniforme [Bull.] licated five times in blocks. After cessation of Quel.) complex, Laccaria laccata (Scop. ex shoot growth, the root systems of plants in Fr.) Berk. & Bromme (isolate PW Lal1), Pax- each pot were carefully separated and during illus involutus (isolate PW Pax1), Thelephora the process most of the potting substrate fell terrestris and Cadophora finlandica (syn. off the roots. Seedling height and root collar Phialophora finlandia C.J.K. Wang & H.E. diameter were measured. Random samples (ca. Wilcox; Mycelium radicis atrovirens Melin). 10% of root systems) were removed from each The H. velutipes and C. finlandica isolates plant and then pooled per pot to estimate the were isolated in Iceland from a sporocarp asso- amount of mycorrhizae. The number of myc- ciated with a 2 year old birch transplant and a orrhizal short roots was counted and expressed mycorrhizal short root in natural birch wood- as a ratio of total number of short roots in each land, respectively. Information on the origins sample (Brundrett et al. 1996). of the other isolates was not available. In October 2005, all bare root seedlings were Inoculation treatments were arranged ran- planted in a reclamation area (Óskarsson 2012) domly in a heated greenhouse and grown for near Hekla volcano in south Iceland (64°05’ 75 days (14°C night and ≥16°C day) from N, 19°41’ W; elevation 260 m). The site was a June to September 2005. Fertilizers were fed pumice field that had been seeded with Ber- through the watering system. For the first 20 ing’s tufted hairgrass (Deschampsia beringen- days, seedlings were fed with a dilute (0.2 sis Hultén) a few years earlier to stabilize the g L-1) Superex (Nursery Stock Superex [19-10- soil surface. The experiment in the field had 24], Kekkila Oyj, ) solution along with the same layout as in the greenhouse. At 0.08 g L-1 monopotassiumphosphate (0-52-34; planting, each seedling received 0.17 g of Haifa Chemical Ltd, Israel). This correspond- granular fertilizer (12-15-17; Áburdarverk- ed to 0.04 gL-1 N, 0.03 g L-1 P and 0.06 g L-1 K. smidjan, Reykjavík, Iceland) placed at the After this the nutrient solution was slowly seedling base. This equalled 0.02 g N, 0.01 g P strengthened, without the monopotassium- and 0.02 g K. phosphate, and was eventually applied as 2.0 g The field experiment was surveyed for 6 L-1 Superex towards the end of the nursery years. Surviving plants were counted and their period. This corresponded to 0.38 g L-1 N, 0.08 total height, root collar diameter and the length 54 ICELANDIC AGRICULTURAL SCIENCES of current year terminal shoot were measured RESULTS at the end of each growing season. The length All fungal isolates tested were able to form of dieback on the previous year’s terminal abundant ectomycorrhizae on birch seedlings shoot was also measured. under the conditions provided in the nursery. The effects of inoculation treatments in the Inoculation treatments significantly influenc- nursery and the number of isolates added to the ed seedling mycorrhization (F value= 10.29, inoculum (isolate diversity) on seedling myc- P <0.001, DF= 13). Individual treatments pro- orrhization and plant parameters in the nursery duced ectomycorrhizae on 34% to 76% of and the field were tested using one-way seedling root ends in the nursery. At the same ANOVA and Tukey’s test to find significant time, 6% of short roots became ectomycor- differences between means. The correlation rhizal on the control seedlings. Two treat- between individual fungal isolates, mycor- ments, a mixture of L. laccata and T. terrestris rhization and plant parameters was investigat- and a mixture of P. involutus, C. finlandica ed using Pearson correlation method, corrected and T. terrestris, produced significantly more for the effect of seedling position within the mycorrhiza than five other inoculum treat- experiments in the nursery and the field. Sta- ments and control seedlings (Figure 1). Fur- tistical analyses were done by SAS 9.2 for thermore, a single isolate inoculation of P. Windows (SAS 2002-2010). involutus produced significantly more mycor- rhiza than three inoculum treat- ments (Figure 1). Control seed- lings had significantly lower my- corrhizal colonization than all but the lowest inoculum treatment (Figure 1). The inclusion of any of three fungal isolates in the original in- oculum was positively correlated with mycorrhizal colonization in the nursery. These were: L. lac- cata (r=0.14, P=0.044, n= 208), P. involutus (r=0.23, P=0.001, n= 208) and T. terrestris (r=0.15, P=0.035, n= 208). Isolate divers- ity in the original inoculum >0 did not influence mycorrhizal coloniz- ation in the nursery. In the nursery, inoculation treat- ments significantly influenced the ratio between seedling root collar diameter (RCD) and seedling Figure 1. Ectomycorrhizal colonization of seedlings at the end of the height (relative RCD; F value= nursery period by inoculation treatments. Each column represents 2.14, P= 0.014, DF= 13). Further- treatment means (n= 15), error bars indicate standard deviations of more, mycorrhizal colonization means, and different letters to the right of the bars denote signifi- was positively correlated with cant difference of means (Tukey’s test P< 0.05). Fungal isolates in seedling height (r= 0.27, P< inoculation treatments are abbreviated to the left of the columns; Cf= 0.001, n= 208) and seedling RCD C. finlandica, Hv= H. velutipes, Ll= L. laccata, Pi= P. involutus, (r= 0.18, P>0.001, n= 208), but Tt= T. terrestris. negatively with relative RCD FIVE FUNGAL ISOLATES 55

(r= 0.29, P< 0.001, n= 208). The relationship time, the inclusion of T. terrestris in the inocu- between mycorrhizal colonization, height and lum treatments in the nursery correlated nega- relative RCD is presented in Figure 2. tively with shoot growth (r= -0.26, P= 0.035, After planting in the field, only one third of n= 70). all seedlings survived the first winter. Seedling survival in the field was only slightly positive- DISCUSSION ly correlated with mycorrhizal colonization in The present study agrees with other studies the nursery (r= 0.14, P=0.037, n=208) and showing that inoculation with mycorrhizal also with the inclusion of L. laccata in the fungi is necessary in order to increase mycor- inoculum treatments in the nursery (r= 0.15, rhization of young forest seedlings in container P= 0.027, n= 208). However, the isolate diversity in the inoculum was negatively correlated with seedling sur- vival in the field (r=-0.14, P=0.032, n=208) and the inclusion of C. finlandica in the inoculum treatments also reduced seedling survival (r= -0.28, P<0.001, n= 208). About half of the surviving seedlings suffered shoot die- back during the first wint- er, but neither plant parameters, treatments nor isolates corre- lated with the degree of shoot dieback. Figure 2. The relationship between ectomycorrhizal colonization and Shoot growth in the field seedling height (left hand axis, o) and relative RCD (right hand axis, () generally dwindled with time at the end of the nursery period. (Figure 3). Seedlings inoculat- ed with one, two or three fungal isolates, which had grown better than seedlings in other treatments in the nurs- ery, grew successively slow- er with time, and so did seed- ling receiving four fungal iso- lates (Figure 3). Non-inoculat- ed seedlings, however, grew at a similar rate for the first two years in the field as in the nursery (Figure 3). In the 6th summer in the field, a nega- tive correlation appeared be- tween shoot growth and isolate diversity in the nursery treat- Figure 3. Seedling annual shoot increment in the nursery and the field by ments (r= -0.27, P= 0,025, isolate diversity (number of fungal isolates included in treatments in the n=70; Figure 3). At the same nursery). Vertical bars denote standard deviation of the means. 56 ICELANDIC AGRICULTURAL SCIENCES nurseries. Peat deposits that are commonly ents and carbohydrates. One of the factors that used as rooting substrates for containers usual- can influence the competitive abilities of a par- ly lack mycorrhizal propagules (Tammi et al. ticular fungal isolate is its inoculum potential 2001) whereas soils in nursery beds, where (Kennedy & Burns, 2005). In some cases, bare root seedlings are repeatedly raised, can where a fungal isolate has a slight advantage in contain numerous mycorrhizal fungi (Menkis competition, it can eliminate other isolates and et al. 2005). Although the sedge peat used in colonize whole root systems (Hönig et al. the present study is deficient in mycorrhizal 2000, Jonsson et al. 2001, Kennedy & Burns propagules, this substrate along with the ferti- 2005). In other cases, the mycorrhizal coloniz- lization regime employed, provides excellent ation of each isolate decreases relative to the conditions for mycorrhization of forest seed- number of isolates (Baxter & Dighton 2001, lings (Óskarsson 2010). Jonsson et al. 2001). The fungal isolates in the present study were In the present study, inoculation treatments variably effective as mycorrhizal colonizers. only had an effect on seedlings in the nursery While isolate numbers >0 in the inoculum and isolates that were synergistic became neu- didn’t cause differences in the total mycorrhiz- tral or even antagonistic in the field. Similar al colonization, the results showed that one observations were made by Jackson et al. isolate, L. laccata was less effective in a single (1995), where differences in mycorrhization isolate treatment than in dual combination with and growth in the nursery due to fungal iso- T. terrestris. Interestingly, Sudhakara Reddy lates did not translate into differences in the & Natarajan (1997) obtained similar results; L. field. laccata and T. terrestris were more effective With time, new roots become colonized with together than separately in increasing the rate mycorrhizal fungi in the field, which are often of mycorrhizal colonization and growth of better adapted to the field conditions, and the seedlings. Conversely, in the present mycorrhiza from the nursery may give way to study, however, P. involutus was more effec- a greater variety of fungi (Dighton & Mason tive alone than in combination with T. terres- 1985). Nonetheless, already established myc- tris. orrhizal isolates can be very persistent. For Variable outcomes in such studies are com- example, isolates of Laccaria spp. that were mon and depend on numerous factors. For used for inoculation in a nursery persisted for example, in studying pine and birch seedlings many years in the field on root systems with- and several mycorrhizal isolates, the only posi- out preventing the colonization of other myc- tive effects of isolate diversity that Jonsson et orrhizal species (Selosse et al. 2000). T. terres- al. (2001) found was on the growth of birch tris has also been reported to be persistent on seedling in a low fertility substrate, whereas plants, perhaps mostly in environments poor the effects on pine growth were negative in in mycorrhizal competitors (Hilszczanska & high fertility substrate. Kennedy et al. (2007) Zbigniew 2006). also found that increased diversity of Rhizopo- In the present study, the antagonistic effects gon spp. isolates negatively affected mycor- in the field associated with the inoculation of rhizal biomass, shoot growth and N of T. terrestris in the nursery awaits further study, pine seedlings. Similarly, even though Baxter but could possibly be related to its persistence and Dighton (2001) found that higher isolate on roots and the investment of the mutualistic diversity increased total mycorrhizal coloniza- system in root mass and explorative mycelium tion and uptake of P and N of birch seedlings, which T. terrestris is known to develop (Ager- shoot biomass was negatively affected. er 2001). The slower shoot growth of isolate In multi-isolate combinations, the substrate diversity > 1 in the 6th summer can also be condition can determine the outcome of com- attributed to T. terrestris, since this isolate was petition between isolates for root ends, nutri- not part of the single isolate treatments. It is FIVE FUNGAL ISOLATES 57 also possible that more beneficial mycorrhizal REFERENCES fungi for seedling shoot growth were better Agerer R 2001. 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