Species diversity of Trichoderma in Poland.

In the present study, we reinvestigate the diversity of Trichoderma in Poland utilizing a combination of morphological and molecular/phylogenetic methods. A total of 170 isolates were collected from six different substrata at 49 sites in Poland. These were divided among 14 taxa as follows: 110 of 170 Trichoderma isolates were identified to the species level by the analysis of their ITS1, ITS2 rDNA sequences as: T. harzianum (43 isolates), T. aggressivum (35), T. citrinoviride (11), T. hamatum (9), T. virens (6), T. longibrachiatum (4), T. polysporum (1), and T. tomentosum (1); 60 isolates belonging to the Viride clade were identified based on a fragment of the translation-elongation factor 1-alpha (tef1) gene as: T. atroviride (20 isolates), T. gamsii (2), T. koningii (17), T. viridescens (13), T. viride (7), and T. koningiopsis (1). Identifications were made using the BLAST interface in TrichOKEY and TrichoBLAST ( http://www.isth.info ). The most diverse substrata were soil (nine species per 22 isolates) and decaying wood (nine species per 75 isolates). The most abundant species (25%) isolated from all substrata was T. harzianum.

Introduction

The fungal genus Trichoderma (Ascomycetes, Hypocreales) includes cosmopolitan soil-borne species that are frequently found also on decaying wood, compost, or other organic matter (Harman et al. 2004; Samuels 2006). Several Trichoderma species are significant biocontrol agents against fungal plant pathogens either through direct parasitism, competition with pathogens for nutrients, stimulators of plant health, or inducers of plant systemic resistance to pathogens (Hjeljord and Tronsmo 1998; Harman et al. 2004; Bailey et al. 2006). The ability for mycoparasitism in some species also has a negative economic impact in the commercial production of Agaricus bisporus (J.E. Lange) Imbach and Pleurotus ostreatus (Paulet) Rolland mushrooms, both of which are reported for Poland (Samuels et al. 2002; Krupke et al. 2003; Hatvani et al. 2007; Szczech et al. 2008). While Trichoderma is not pathogenic towards healthy mammals, there is a growing number of immunocompromised individuals who suffer opportunistic infections by some species (Kuhls et al. 1999; Kredics et al. 2003; Piens et al. 2004; Druzhinina et al. 2008), and volatile compounds produced by some Trichoderma species can cause allergic reactions (Tang et al. 2003; Caballero et al. 2007). Trichoderma species produce a wide diversity of metabolites, most notably commercially important cellulase and hemicellulases, antibiotics, peptaibiotics, as well as the toxins (such as trichodermamides) and trichothecenes that display in vitro cytotoxicity (Kubicek and Penttilä 1998; Sivasithamparam and Ghisalberti 1998; Garo et al. 2003; Liu et al. 2005; Nielsen et al. 2005; Degenkolb et al. 2006, 2008).

Because of the intimate relationship between species of Trichoderma and human activity, there is a great need for the accurate identification of Trichoderma species. However, accurate species identification based on morphology is difficult at best because of the paucity and similarity of useful morphological characters (Druzhinina et al. 2005; De Respinis et al. 2010), and increasing numbers of morphologically cryptic species that can be distinguished only through their DNA characters are being described (Atanasova et al. 2010; Samuels et al. 2010). This has already resulted in incorrect identification and the propagation of errors for strains associated with the production of secondary metabolites (Humphris et al. 2002), with human diseases (Gautheret et al. 1995), and biological control (Kullnig et al. 2001). However, with the advent of molecular methods and identification tools, which are based on sequence analysis of multiple genes (rDNA and genes encoding actin, calmodulin, endochitinase, RNA polymerase II, and translation-elongation factor 1-alpha [tef1]), it is now possible to identify every Trichoderma isolate and/or recognize it as a putative new species (Druzhinina et al. 2005; Samuels 2006; Kubicek et al. 2008).

At present, the International Subcommission on Trichoderma and Hypocrea Taxonomy lists 104 species, all of which have been characterized at the molecular level (http://www.isth.info). Seventy-five species of Hypocrea have been identified in temperate Europe, in particular, in Austria (Jaklitsch 2009). Nevertheless, the information about the diversity of Trichoderma/Hypocrea in Poland is scarce. A preliminary checklist of micromycetes in Poland reported 20 Trichoderma species (Mułenko et al. 2008). However, all of these species were identified between 1903 and 2002 based on morphological characters.

The objective of the present study was to document the occurrence and species diversity of Trichoderma collected from different substrata and locations in Poland.

Materials and methods

Substrata, storage, and isolation of pure cultures

Fungal isolates investigated in this study were collected from pieces of decaying wood, cultivated mushroom compost, samples of soil (garden, forest), and cereal grain (triticale, maize) at 49 sites in Poland (Table 1). Samples of decaying wood with white or brown rot were collected in parks and forests of the Wielkopolska region of Poland, placed in paper bags, dried at room temperature if wet, and stored until isolation. The pieces of decaying wood were plated on saltwater nutrient agar (SNA, Nirenberg 1976) and incubated at 20°C for 6 days. Putative Trichoderma colonies were purified by two rounds of subculturing on potato dextrose agar (PDA, Oxoid). Pure culture were transferred to the tube containing SNA and stored at −4°C for further study. Trichoderma spp. originated from other substrata were isolated according to the method described by Mańka (1974). Thirty-seven isolates originating from mushroom compost at mushroom farms in Poznań and in Skierniewice, as well as from forest soil of the Wielkopolski National Park were kindly supplied by Profs. H. Kwaśna and M. Mańka, Department of Forest Pathology, Poznań University of Life Sciences, and by Dr M. Szczech, Department of Plant Protection, Research Institute of Vegetable Crops, Skierniewice.

Table 1

List of Trichoderma isolates included in this study

Culture code	Species	Sources/localization	Allelic groupa		NCBI GenBank accession number
			ITS1, ITS2	tef1	ITS1, ITS2	tef1
AN 13	T. atroviride	forest soil, WNPb	cV3	AT1	HQ292784	HQ292961
AN 14	T. atroviride	forest soil, WNP	cV3	AT1	HQ292785	HQ292962
AN 19	T. atroviride	forest soil, WNP	cV3	AT1	HQ292786	HQ292963
AN 21	T. hamatum	forest soil, WNP	HM1	–	HQ292850	–
AN 22	T. gamsii	forest soil, WNP	cV9	–	HQ292951	–
AN 35	T. atroviride	maize kernels, Radzików	cV3	AT2	HQ292787	HQ292953
AN 46	T. citrinoviride	soil	C1	–	HQ292839	–
AN 55	T. polysporum	soil	–	–	HQ292950	–
AN 59	T. citrinoviride	soil	C1	–	HQ292840	–
AN 61	T. harzianum	soil	HR7	–	HQ292866	–
AN 68	T. virens	compost, Puławy	VS3	–	HQ292943	–
AN 69	T. virens	compost, Puławy	VS3	–	HQ292944	–
AN 70	T. virens	compost, Puławy	VS1	–	HQ292947	–
AN 73	T. virens	compost, Puławy	VS3	–	HQ292945	–
AN 74	T. virens	compost, Puławy	VS3	–	HQ292946	–
AN 75	T. virens	compost, Puławy	VS1	–	HQ292948	–
AN 89	T. citrinoviride	garden soil, Poznań	C1	–	HQ292841	–
AN 90	T. atroviride	garden soil, Poznań	cV3	AT2	HQ292788	HQ292954
AN 91	T. harzianum	compost, Poznań	HR6	–	HQ292860	–
AN 92	T. harzianum	maize kernels, Radzików	HR5	–	HQ292867	–
AN 93	T. viridescens	forest soil, Malta, Poznań	cV5	VD3	HQ292927	HQ292995
AN 94	T. harzianum	forest soil, Malta Park, Poznań	HR3	–	HQ292873	–
AN 95	T. atroviride	compost, Poznań	cV3	AT2	HQ292789	HQ292955
AN 96	T. atroviride	compost, Poznań	cV3	AT2	HQ292790	HQ292956
AN 97	T. citrinoviride	forest wood, Wieluń	C1	–	HQ292842	–
AN 98	T. citrinoviride	forest wood, Wieluń	C1	–	HQ292843	–
AN 99	T. citrinoviride	forest wood, Wieluń	C2	–	HQ292848	–
AN 100	T. koningii	forest wood, Wieluń	cV1	KO1	HQ292903	HQ292975
AN 101	T. harzianum	forest wood, Wieluń	HR5	–	HQ292868	–
AN 102	T. citrinoviride	forest wood, Wieluń	C1	–	HQ292844	–
AN 104	T. koningii	forest wood, Dziewicza Góra, Poznań	cV1	KO1	HQ292904	HQ292976
AN 105	T. koningii	forest wood, Dziewicza Góra, Poznań	cV1	KO1	HQ292905	HQ292977
AN 106	T. koningii	forest wood, Dziewicza Góra, Poznań	cV1	KO1	HQ292906	HQ292978
AN 107	T. koningii	forest wood, Dziewicza Góra, Poznań	cV1	KO1	HQ292907	HQ292979
AN 108	T. harzianum	forest wood, Dziewicza Góra, Poznań	HR5	–	HQ292869	–
AN 111	T. atroviride	forest wood, Dziewicza Góra, Poznań	cV3	AT1	HQ292791	HQ292964
AN 113	T. koningii	forest wood, Żurawiniec Park, Poznań	cV1	KO1	HQ292908	HQ292980
AN 114	T. koningii	forest wood, Żurawiniec Park, Poznań	cV1	KO1	HQ292909	HQ292981
AN 115	T. koningii	forest wood, Żurawiniec Park, Poznań	cV1	KO1	HQ292910	HQ292982
AN 116	T. koningii	forest wood, Żurawiniec Park, Poznań	cV1	KO1	HQ292911	HQ292983
AN 117	T. koningii	forest wood, Żurawiniec Park, Poznań	cV1	KO1	HQ292912	HQ292984
AN 118	T. hamatum	forest wood, Rusałka Park, Poznań	HM2	–	HQ292854	–
AN 120	T. hamatum	forest wood, Rusałka Park, Poznań	HM2	–	HQ292855	–
AN 121	T. koningii	forest wood, Rusałka Park, Poznań	cV1	KO1	HQ292913	HQ292985
AN 122	T. viridescens	forest wood, Rusałka Park, Poznań	cV5	VD4	HQ292928	HQ292994
AN 124	T. koningii	forest wood, Rusałka Park, Poznań	cV1	KO1	HQ292914	HQ292986
AN 125	T. koningii	forest wood, Rusałka Park, Poznań	cV1	KO1	HQ292915	HQ292987
AN 126	T. koningii	forest wood, Rusałka Park, Poznań	cV1	KO2	HQ292916	HQ292991
AN 127	T. koningii	forest wood, Rusałka Park, Poznań	cV1	KO1	HQ292917	HQ292988
AN 128	T. koningii	forest wood, Rusałka Park, Poznań	cV1	KO1	HQ292918	HQ292989
AN 132	T. harzianum	forest wood, Rusałka Park, Poznań	HR5	–	HQ2928670	–
AN 133	T. harzianum	forest wood, Jeziory, WNP	HR4	–	HQ292874	–
AN 134	T. harzianum	forest wood, Jeziory, WNP	HR4	–	HQ292875	–
AN 135	T. harzianum	forest wood, Jeziory, WNP	HR4	–	HQ292876	–
AN 136	T. harzianum	forest wood, Jeziory, WNP	HR1	–	HQ292901	–
AN 137	T. harzianum	forest wood, Jeziory, WNP	HR4	–	HQ292877	–
AN 138	T. harzianum	forest wood, Jeziory, WNP	HR6	–	HQ292861	–
AN 141	T. viride	forest wood, Jeziory, WNP	cV6	V12	HQ292922	HQ293008
AN 142	T. viride	forest wood, Jeziory, WNP	cV8	V12	HQ292920	HQ293009
AN 143	T. koningiopsis	forest wood, Jeziory, WNP	cV4	–	HQ292929	HQ292992
AN 144	T. koningii	forest wood, Jeziory, WNP	cV1	KO1	HQ292919	HQ292990
AN 145	T. viridescens	forest wood, Jeziory, WNP	cV5	VD3	HQ292930	HQ292996
AN 146	T. viridescens	forest wood, Jeziory, WNP	cV5	VD3	HQ292931	HQ292997
AN 147	T. viridescens	forest wood, Jeziory, WNP	cV5	VD3	HQ292932	HQ292998
AN 148	T. viridescens	forest wood, Jeziory, WNP	cV5	VD3	HQ292933	HQ292999
AN 149	T. viridescens	forest wood, Jeziory, WNP	cV5	VD3	HQ292934	HQ293000
AN 150	T. harzianum	forest wood, Jeziory, WNP	HR4	–	HQ292878	–
AN 152	T. atroviride	triticale kernel, Choryń	cV3	AT2	HQ292792	HQ292957
AN 153	T. atroviride	triticale kernel, Choryń	cV3	AT2	HQ292793	HQ292958
AN 155	T. hamatum	rye rizosphera, Lublin	HM1	–	HQ292851	–
AN 171	T. aggressivum	mushroom compost, Skierniewice	AG2	–	HQ292807	–
AN 172	T. aggressivum	mushroom compost, Skierniewice	AG2	–	HQ292808	–
AN 176	T. viride	forest wood, Strzeszyn Park, Poznań	cV8	V13	HQ292923	HQ293010
AN 179	T. viride	forest wood, Strzeszyn Park, Poznań	cV8	V13	HQ292924	HQ293011
AN 182	T. atroviride	forest wood, Strzeszyn Park, Poznań	cV2	AT1	HQ292794	HQ292965
AN 188	T. atroviride	mushroom compost, Skierniewice	cV4	AT2	HQ292803	HQ292959
AN 197	T. longibrachiatum	mushroom factory, Skierniewice	L1	–	HQ292780	–
AN 198	T. citrinoviride	mushroom factory, Skierniewice	C1	–	HQ292845	–
AN 199	T. citrinoviride	mushroom factory, Skierniewice	C1	–	HQ2929846	–
AN 201	T. citrinoviride	mushroom factory, Skierniewice	C3	–	HQ292849	–
AN 203	T. harzianum	mushroom compost, Poznań	HR4	–	HQ292879	–
AN 205	T. harzianum	mushroom compost, Poznań	HR4	–	HQ292880	–
AN 206	T. atroviride	mushroom compost, Poznań	cV4	AT2	HQ292804	HQ292960
AN 207	T. harzianum	mushroom compost, Poznań	HR4	–	HQ292881	–
AN 208	T. aggressivum	mushroom compost, Poznań	AG1	–	HQ292805	–
AN 209	T. aggressivum	mushroom compost, Poznań	AG1	–	HQ292882	–
AN 211	T. harzianum	mushroom compost, Poznań	HR4	–	HQ292882	–
AN 212	T. atroviride	mushroom compost, Poznań	cV3	AT1	HQ292795	HQ292966
AN 213	T. longibrachiatum	mushroom compost, Poznań	L1	–	HQ292781	–
AN 215	T. atroviride	mushroom compost, Poznań	cV3	AT1	HQ292796	HQ292967
AN 216	T. aggressivum	mushroom compost, Poznań	AG2	–	HQ292809	–
AN 223	T. harzianum	forest soil, WNP	HR2	–	HQ292902	–
AN 225	T. hamatum	forest soil, WNP	HM21	–	HQ292856	–
AN 226	T. viridescens	forest soil, WNP	cV5	VD1	HQ292935	HQ293004
AN 227	T. viridescens	forest soil, WNP	cV5	VD5	HQ292936	HQ293001
AN 229	T. viridescens	forest soil, WNP	cV5	VD5	HQ292937	HQ293002
AN 231	T. viridescens	forest soil, WNP	cV5	VD2	HQ292938	HQ293003
AN 232	T. hamatum	forest soil, WNP	HM1	–	HQ292852	–
AN 234	T. tomentosum	forest soil, WNP	–	–	HQ292949	–
AN 235	T. viride	forest soil, WNP	cV7	VI1	HQ292921	HQ293013
AN 238	T. hamatum	forest soil, WNP	HM1	–	HQ292853	–
AN 257	T. harzianum	forest wood, Radojewo	HR4	–	HQ292883	–
AN 258	T. harzianum	forest wood, Radojewo	HR5	–	HQ292871	–
AN 259	T. harzianum	forest wood, Radojewo	HR5	–	HQ292872	–
AN 260	T. harzianum	forest wood, Radojewo	HR4	–	HQ292884	–
AN 261	T. harzianum	forest wood, Radojewo	HR4	–	HQ292885	–
AN 262	T. citrinoviride	forest wood, Radojewo	C1	–	HQ292847	–
AN 263	T. longibrachiatum	mushroom compost, Poznań	L1	–	HQ292782	–
AN 264	T. longibrachiatum	mushroom compost, Poznań	L2	–	HQ292783	–
AN 266	T. viride	mushroom compost, Poznań	cV8	VI3	HQ292925	HQ293012
AN 273	T. harzianum	forest wood, Kórnik	HR4	–	HQ292886	–
AN 274	T. harzianum	forest wood, Kórnik	HR4	–	HQ292887	–
AN 275	T. harzianum	forest wood, Kórnik	HR4	–	HQ292888	–
AN 276	T. harzianum	forest wood, Kórnik	HR4	–	HQ292889	–
AN 277	T. hamatum	forest wood, Kórnik	HM1	–	HQ292857	–
AN 278	T. harzianum	forest wood, Kórnik	HR4	–	HQ292890	–
AN 279	T. hamatum	forest wood, Kórnik	HM1	–	HQ292858	–
AN 281	T. atroviride	forest wood, Kórnik	cV2	AT3	HQ292804	HQ292974
AN 282	T. harzianum	forest wood, Kórnik	HR4	–	HQ292891	–
AN 283	T. harzianum	forest wood, Kórnik	HR4	–	HQ292892	–
AN 284	T. harzianum	forest wood, Kórnik	HR4	–	HQ292893	–
AN 285	T. harzianum	forest wood, Kórnik	HR4	–	HQ292894	–
AN 286	T. harzianum	forest wood, Kórnik	HR4	–	HQ292895	–
AN 287	T. atroviride	forest wood, Radojewo	cV3	AT1	HQ292798	HQ292969
AN 288	T. viridescens	forest wood, Kórnik	cV5	VD1	HQ292941	HQ293006
AN 425t	T. harzianum	forest wood, Radojewo	HR4	–	HQ292896	–
AN 426	T. harzianum	forest wood, Radojewo	HR4	–	HQ292897	–
AN 427	T. viridescens	forest wood, Radojewo	cV5	VD1	HQ292942	HQ293007
AN 430	T. viride	forest wood, Radojewo	cV8	VI1	HQ292926	HQ293014
AN 431	T. harzianum	forest wood, Radojewo	HR4	–	HQ292898	–
AN 435	T. harzianum	forest wood, Radojewo	HR4	–	HQ292899	–
AN 436	T. atroviride	forest wood, Radojewo	cV3	AT1	HQ292799	HQ292970
AN 437	T. harzianum	forest wood, Radojewo	HR4	–	HQ292900	–
AN 550	T. gamsii	forest wood, Poznań	cV9	–	HQ292952	–
AN 561	T. aggressivum	mushroom compost, Nowy Tomyśl	AG2	–	HQ292810	–
AN 562	T. aggressivum	mushroom compost, Ostróda	AG2	–	HQ292811	–
AN 563	T. aggressivum	mushroom compost, Toruń	AG2	–	HQ292812	–
AN 564	T. aggressivum	mushroom compost, Łomża	AG2	–	HQ292813	–
AN 565	T. aggressivum	mushroom compost, Siemiatycze	AG2	–	HQ292814	–
AN 566	T. aggressivum	mushroom compost, Olsztyn	AG2	–	–	–
AN 567	T. aggressivum	mushroom compost, Tychy	AG2	–	HQ292815	–
AN 568	T. aggressivum	mushroom compost, Bytom	AG2	–	HQ292816	–
AN 569	T. aggressivum	mushroom compost, Łosice	AG2	–	HQ292817	–
AN 570	T. aggressivum	mushroom compost, Biała Podlaska	AG2	–	HQ292818	–
AN 571	T. aggressivum	mushroom compost, Międzychód	AG2	–	HQ292819	–
AN 572	T. aggressivum	mushroom compost, Gorzów Wlkp.	AG2	–	HQ292820	–
AN 573	T. aggressivum	mushroom compost, Przemyśl	AG2	–	HQ292821	–
AN 574	T. aggressivum	mushroom compost, Siedlce	AG2	–	HQ292822	–
AN 575	T. aggressivum	mushroom compost, Sokołów Podlaski	AG2	–	HQ292823	–
AN 576	T. aggressivum	mushroom compost, Chojnice	AG2	–	HQ292824	–
AN 577	T. aggressivum	mushroom compost, Szczecinek	AG2	–	HQ292825	–
AN 578	T. aggressivum	mushroom compost, Krosno Lubuskie	AG2	–	HQ292826	–
AN 579	T. aggressivum	mushroom compost, Zielona Góra	AG2	–	HQ292827	–
AN 580	T. harzianum	mushroom compost, Pszczyna	HR6	–	HQ292862	–
AN 581	T. harzianum	mushroom compost, Marianów/Koło	HR6	–	HQ292863	–
AN 582	T. aggressivum	mushroom compost, Turek	AG3	–	HQ292835	–
AN 583	T. aggressivum	mushroom compost, Człuchów	AG3	–	HQ292836	–
AN 584	T. aggressivum	mushroom compost, Piła	AG3	–	HQ292837	–
AN 585	T. aggressivum	mushroom compost, Skierniewice	AG2	–	HQ292828	–
AN 586	T. aggressivum	mushroom compost, Świecie	AG2	–	HQ292829	–
AN 587	T. aggressivum	mushroom compost, Skierniewice	AG3	–	HQ292838	–
AN 590	T. harzianum	mushroom compost, Piasek/Pszczyna	HR6	–	HQ292864	–
AN 591	T. aggressivum	mushroom compost, Wolsztyn	AG2	–	HQ292830	–
AN 592	T. aggressivum	mushroom compost, Rzeszów	AG2	–	HQ292831	–
AN 593	T. atroviride	mushroom compost, Pszczyna	cV3	AT1	HQ292800	HQ292971
AN 594	T. aggressivum	mushroom compost, Rakoniewice	AG2	–	HQ292832	–
AN 595	T. aggressivum	mushroom compost, Wielichowo	AG2	–	HQ292833	–
AN 596	T. atroviride	mushroom compost, Jarocin	cV3	AT1	HQ292801	HQ292972
AN 597	T. harzianum	mushroom compost, Kalisz	HR6	–	HQ292865	–
AN 599	T. aggressivum	mushroom compost, Pszczyna	AG2	–	HQ292834	–
AN 600	T. atroviride	mushroom compost, Pszczyna	cV3	AT1	HQ292802	–

aThe group of isolates possessing identical alleles in the locus of ITS or tef1, analyzed in the present study(Figs. 1 and 2)

bWNP: Wielkopolski National Park

Fig. 1

Phylogenetic tree of the 170 Trichoderma isolates inferred by parsimony analysis of ITS1, ITS 2 sequences. Sequences obtained during this study are listed by their GenBank numbers in Table 1. The numbers given over branches indicate bootstrap coefficient >50%. The symbols given on the right (HR, AG, L, C, HM, cV) indicate the allelic groups of isolates, forming on the basis of ITS sequences identity. The isolates belonging to individual allelic groups are listed in Table 1

Fig. 2

Phylogenetic tree of the 60 Trichoderma isolates inferred by parsimony analysis of tef1 sequences. Sequences obtained during this study are listed by their GenBank numbers in Table 1. The numbers given over branches indicate bootstrap coefficient >50%. The symbols given on the right (KO, VI, AT, VD) indicate the allelic groups of isolates, forming on the basis of tef1 sequences identity. The isolates belonging to individual allelic groups are listed in Table 1

Morphological analysis

Fungal colonies were grown on PDA and SNA at 25°C for 7 days. Trichoderma species were identified according to Gams and Bissett (1998) and Samuels et al. (2002, 2009; http://nt.ars-grin.gov/taxadescriptions/keys/TrichodermaIndex.cfm).

Isolation of DNA

Mycelium for DNA extraction was obtained by inoculating Czapek-Dox broth (Sigma) with Yeast Extract (Oxoid) and streptomycin sulfate (50 mg/L−1, AppliChem), and after incubation at 25°C for 21 days on a rotary shaker (120 rpm). Mycelium was collected on filter paper in a Büchner funnel, washed with sterile water, frozen at −20°C, and freeze-dried.

Total DNA was extracted using the CTAB method (Doohan et al. 1998).

PCR amplification and sequencing

Primary identification was based on the sequencing of internal transcribed spacer regions 1 and 2 (ITS1 and ITS2) of the rRNA gene cluster. In cases where ITS1 and ITS2 did not provide unambiguous identification, a fragment of the translation-elongation factor 1-alpha (tef1) gene was sequenced. The ITS region of the rDNA of 170 isolates was amplified using primers ITS4, ITS5 (White et al. 1990). A fragment of tef1 gene containing the 4th and 5th introns was amplified using the primers Ef728M (Carbone and Kohn 1999) and tef1R (Kullnig-Gradinger et al. 2002). The PCR reaction was carried out in a 25-μl reaction mixture containing the following: 1 μl 50 ng/μl of DNA, 2.5 μl 10 × PCR buffer (50 mM KCl, 1.5 mM MgCl2, 10 mM Tris-HCl, pH 8.8, 0.1% Triton X-100), 1.5 μl 10 mM dNTP (GH Healthcare), 0.2 μl 100 mM of each primer, 19.35 μl MQ H2O, 0.25 μl (2 U/μl) DyNAzymeTM II DNA Polymerase (Finnzymes). Amplifications were performed in either a PTC-200 or PTC-100 thermocycler (MJ Research, USA) under the following conditions: initial denaturation 5 min at 94°C, 35 cycles of 45 s at 94°C, 45 s at 58°C (for the ITS region), or 63°C (for the tef1 fragment), 1 min at 72°C, with the final extension of 10 min at 72°C. Amplification products were separated on 1.5% agarose gel (Invitrogen) in 1 × TBE buffer (0.178 M Tris-borate, 0.178 M boric acid, 0.004 M EDTA) and stained with ethidium bromide. The 10-μl PCR products were combined with 2 μl of loading buffer (0.25% bromophenol blue, 30% glycerol). A 100-bp DNA Ladder Plus (Fermentas) was used as a size standard. PCR products were electrophoresed at 3 Vcm−1 for about 2 h, visualized under UV light, and photographed (Syngene UV visualizer). The 3-μl PCR products were purified with exonuclease I and shrimp alkaline phosphatase according to Chełkowski et al. (2003). Sequencing reactions were prepared using the ABI Prism BigDye Terminator Cycle Sequencing Ready Reaction Kit in 5 μl volume (Applied Biosystems, Switzerland). DNA sequencing was performed on an ABI PRISM 310 Genetic Analyzer (USA). Sequences were edited and assembled using Chromas v.1.43 (Applied Biosystems). CLUSTAL W (Thompson et al. 1994) and MUSCLE (Edgar 2004) were used to align the sequences; the resulting alignments were inspected and refined manually.

Molecular identification and phylogenetic analysis

For species identification, ITS1 and ITS 2 sequences were submitted to the BLAST interface in TrichOKEY (http://www.isth.info; Druzhinina et al. 2005; Druzhinina and Kubicek 2005). In ambiguous cases, the result was re-checked using the TrichoBLAST program based on tef1 gene sequences (Druzhinina and Kopchinskiy 2004a, b). All positions containing gaps and missing data were eliminated from the dataset. Phylogenetic analyses were performed in MEGA4 (Tamura et al. 2004). Both ITS1, ITS2 and tef1 gene sequences were analyzed using the maximum parsimony (Eck and Dayhoff 1966) approach of close-neighbor-interchange algorithm with search level 3 (Nei and Kumar 2000), in which the initial trees were obtained with the random addition of sequences (10,000 replicates). In total, there were 48 parsimony informative positions retained from an initial alignment of 368 for the ITS1, ITS2 sequences and 491 positions in the final dataset, of which 118 were parsimony informative for tef1 gene sequences. In both cases, to infer the consensus, phylogenetic trees bootstrapping with 10,000 data replicates was conducted (Felsenstein 1985).

Results

Species identification

A total of 170 isolates were obtained from the six different substrata at 49 localities in Poland. Of theses 170 Trichoderma isolates, 110 were identified at the species level by morphological characteristics and analysis of their ITS1, ITS2 nucleotide sequences as: T. harzianum Rifai (43 isolates), T. aggressivum Samuels & W. Gams (35), T. citrinoviride Bisset (11), T. hamatum (Bonord.) Bainier (9), T. virens (J.H. Mill., Giddens & A.A. Foster) Arx (6), T. longibrachiatum Rifai (4), T. polysporum (Link) Rifai (1), and T. tomentosum Bissett (1). In case of the remaining 60 Trichoderma isolates, where ITS1 and ITS2 did not provide unambiguous identification, the fragment of the tef1 gene was sequenced. Thereby, the following species were identified: T. atroviride P. Karst. (20 isolates), T. gamsii Samuels & Druzhin. (2), T. koningii Oudem. (17), T. viridescens (A.S. Horne & H.S. Will.) Jaklitsch & Samuels (13), T. viride Pers. (7), and T. koningiopsis Oudem. (1). The identification, origin, and NCBI GeneBank accession numbers of all isolates are given in Table 1.

Phylogenetic analysis

The result of the phylogenetic analysis based on the ITS sequences of 170 Trichoderma isolates is shown in Fig. 1. In the ITS tree, the Harzianum clade, with T. harzianum, T. aggressivum, and T. tomentosum, the Longibrachiatum Clade, with T. longibrachiatum and T. citrinoviride, and the species T. virens, T. hamatum, and T. polysporum were distinguished in a single moderately supported branch with bootstrap support of 79%. Forty-three strains were identified as T. harzianum, but this species is known to include several ITS alleles (Hermosa et al. 2004; Migheli et al. 2009) and is considered to be a species complex (Chaverri et al. 2003). In the present research, seven haplotypes of T. harzianum were found (HR1, HR2, HR3, HR4, HR5, HR6, and HR7, according to Table 1 and Fig. 1). With bootstrap support of only 53%, these seven haplotypes of T. harzianum formed a moderately well-supported (75%) clade with T. aggressivum and an unresolved polytomy with T. tomentosum. Two groups were distinguished within the Longibrachiatum clade with moderate to good bootstrap support. One group, with a bootstrap value of 70%, contains four strains of T. longibrachiatum. The second group, with a bootstrap value of 93% includes 11 strains of T. citrinoviride. Sixty isolates of Trichoderma, belonging to the Viride clade, formed a polytomy. A phylogenetic analysis based on tef1 sequences was performed for them (Fig. 2). As a result of this, the six species (T. koningii, T. atroviride, T. viride, T. viridescens, T. gamsii) were resolved with high bootstrap support.

Species diversity

Fourteen species of Trichoderma were identified among 170 isolates collected from six different substrata and 49 localities in Poland, using both morphological and molecular analysis. The highest diversity of Trichoderma species was detected in the set of 22 isolates originating from soil, which included nine species (T. atroviride, T. citrinoviride, T. gamsii, T. hamatum, T. harzianum, T. polysporum, T. tomentosum, T. viride, T. viridescens). Most of the isolates were collected from decaying wood (75), but among them, only nine species were found (T. atroviride, T. citrinoviride, T. gamsii, T. hamatum, T. harzianum, T. koningii, T. koningiopsis, T. viride, T. viridescens). The single strains of T. polysporum and T. tomentosum were isolated from soil, whereas all 17 strains of T. koningii were isolated from forest wood at several sites. The 58 isolates from mushroom compost and mushroom farms comprised seven species: T. aggressivum, T. atroviride, T. citrinoviride, T. harzianum, T. longibrachiatum, T. virens, and T. viride. In the limited samples from grains of Zea mays and Triticosecale Wittm. ex A. Camus as well as from garden compost, only three species were identified: T. atroviride, T. harzianum, and T. virens. T. harzianum was the most abundant species (25%) and was isolated from all substrata. It was the most common species isolated from pieces of decaying wood (40%, 30 isolates). After T, harzianum, T. atroviride, T. koningii, T. viridescens, and T. citrinoviride were the most abundant (respectively, 12%, 15%, 12%, and 7% of 112 isolates) Trichoderma species collected from soil, compost, forest wood, and cereal grains, respectively. The most common species isolated from mushroom compost was T. aggressivum (60% of isolates originated from mushroom compost and 20% of all isolates from the collection). T. hamatum, T. virens, T. viride, T. longibrachiatum, T. gamsii, T. koningiopsis, T. polysporum, and T. tomentosum were the most scarcely identified species of the genus (≤5% of all isolates from the collection).

Discussion

The present study is a preliminary domestic assessment of Trichoderma diversity in Poland. A collection of 170 isolates obtained from six different substrata and 49 localities in Poland were identified by phenetic observations and by analysis of the ITS 1, ITS 2 region of rRNA gene cluster and/or a fragment of the tef1 gene. A wide diversity of Trichoderma isolates was found (14 species were identified among 170 isolates) in comparison with the studies on the biodiversity of Trichoderma in South-East Asia (Kubicek et al. 2003), in Austria (Wuczkowski et al. 2003), in South America (Druzhinina et al. 2005), in China (Zhang et al. 2005), and on Sardinia (Migheli et al. 2009). The highest diversity of Trichoderma was found in Colombia, Mexico, Guatemala, Panama, Peru, Ecuador, and Brazil (Hoyos-Carvajal et al. 2009). Hoyos-Carvajal et al. (2009) recorded almost twice as many species from a comparably sized sample of 183 isolates collected in these neotropical regions.

Here and in a previous study, T. harzianum was the predominant taxon (Kubicek et al. 2003; Wuczkowski et al. 2003; Druzhinina et al. 2005, 2010; Zhang et al. 2005; Migheli et al. 2009). T. harzianum is the most commonly reported species in the genus, occurring in diverse ecosystems and ecological niches. However, it must be borne in mind that the name ‘T. harzianum’ applies to a species complex within which several morphologically cryptic phylogenetic species—haplotypes—are found (results presented here) and these ‘haplotype species’ may be seen to comprise a multiplicity of species when subjected to multilocus phylogenetic analysis (Chaverri et al. 2003; Gherbawy et al. 2004; Zhang et al. 2005; Druzhinina et al. 2010). In the present research, seven haplotypes (HR1–HR7) were evident in the analysis of ITS sequences for T. harzianum isolates. Haplotypes HR1, HR3, HR4, HR5, HR6, and HR7 correspond with ITS haplotypes, which are very common in Europe (Jaklitsch 2009, Chaverri et al. [unpublished]; Woo et al. [unpublished]). Haplotype HR2 (isolate AN 223) corresponds to the ex neo type strain of T. harzianum CBS 226.95, and, thus, represents T. harzianum sensu stricto. T. harzianum sensu stricto is also a species with a broad north temperate distribution, including at least North America, Europe, and Asia (Zhang et al. 2005; Chaverri and Samuels [unpublished]).

The second abundant species identified in the present study and the most prevalent species from mushroom compost was T. aggressivum (35 isolates). This result corresponds with the previous study of Szczech et al. (2008), who showed that, between 2004 and 2006, T. aggressivum was the most frequently isolated species of the genus identified in Polish mushroom farms. T. aggressivum has been isolated from mushroom compost used for A. bisporus cultivation in Europe and North America (Samuels et al. 2002). This species has only been isolated once from soil in Kenya (Samuels and Szakacs [unpublished]). It is not yet known whether this species also occurs in natural environments.

Other species identified in the present study were: T. atroviride (20 isolates), T. koningii (17), T. viridescens (13), T. citrinoviride (11), T. hamatum (9), T. viride (7), T. virens (6), T. longibrachiatum (4), T. gamsii (2), T. koningiopsis (1), T. polysporum (1), and T. tomentosum (1). These species are representative of a temperate Trichoderma biota (Kubicek et al. 2008). T. viride, T. viridescens, T. koningii, T. citrinoviride, T. aggressivum, T. tomentosum, and T. polysporum are rather restricted to temperate regions. However, T. longibrachiatum, T. virens, T. koningiopsis, T. hamatum, and T. atroviride were also found in the neotropical study (Hoyos-Carvajal et al. 2009).

The current results suggested that the most diverse habitats were soil (nine species per 22 isolates) and decaying wood (nine species per 75 isolates) gathered in parks and forests of the Wielkopolska region of Poland. The decaying wood was also the substrata from which the most isolates of Trichoderma (75) were collected. In this connection, we will continue to analyze the genetic and metabolic biodiversity of Trichoderma isolates originating from Polish mountains and isolated from forest wood with decay symptoms.