Impact of increased inorganic nitrogen deposition on the mycorrhizal community

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Eastern CANUSA Forest Science Conference Impact of increased inorganic nitrogen deposition on the mycorrhizal community Adam Bordeleau, Hubert Morin, Sergio Rossi et Daniel Houle 1

Ectomycorrhiza Symbiotic relation between fungi and root tips Symbiosis with trees (spruce, pine, fir, beech, oak, eucalyptus ) Sugars to the fungus Water and nutrition for the plant 2

Nitrogen depositions Nitrogen depositions remain high in North America - Transport and midwest farming 1860 1990 mg N m -2 y -1 2050 3

Nitrogen deposition Many forests show signs of nitrogen saturation in northeastern US N highly retained in most watershed in eastern Canada Forests have a high C:N ratio Low N residence time (<1 day) Nitrate Ammonium 4

Communities How ectomycorhizal (ECM) communities will react to the cumulative effect of high nitrogen depositions? Little information on the eastern ECM communities Biodiversity loss Impact on tree growth? 5

Nitrogen effects Diversity - Long-term nitrogen deposition (Lilleskov et al. 2002) - Nitrogen gradient (Lilleskov et al. 2009) - Nitrogen gradient (Taylor et al. 2000) Diversity - Nitrogen gradient (Kranabetter et al. 2009) No effect - Nitrogen gradient (Twieg et al. 2009) 6

Key factors Host Soil conditions - ph - Moisture - N, P, K, Ca 7

Nitrogen cycle Complex N molecules Ex. proteins ECM Simple N molecules Ex. amino acids ECM Ammonium (NH 4+ ) Trees 8

Nitrogen cycle Complex N molecules Ex. proteins ECM Simple N molecules Ex. amino acids ECM? Ammonium (NH 4+ ) Nitrate (NO 3- )? Trees 9

Objective To compare ECM communities at contrasting nitrogen deposition levels Root tip vitality ECM presence ECM diversity 10

Site Black spruce forest Mean temperature: 1,2 C Annual precipitation: 823 mm Forest age: 60 years Origin: Fire Annual N deposition: 3,0 kg ha -1 y -1 C:N 49 Lac Tirasse 11

Site 8 years Ammonium nitrate Every two weeks from may to october 12

Sites [N] applied represents 3 and 10 fold annual nitrogen deposition 3 quadrats (10m x 10m) per treatment 3 samples per quadrat 3 fold N (LN) 10 fold N (HN) Lake Tirasse (EPN) 9 kg ha -1 y -1 30 kg ha -1 y -1 13

Design Control (C) 10 fold N (HN) 3 fold N (LN) Sample 14

Methods Sampling in october 2009 Mineral Organic Identification Soil analysis Identification Soil analysis 15

Identification First cleaning 15 fines roots per sample Second cleaning Stereomicroscope 16

Identification 15 fines roots per sample 15 tips per root Morphotyping 15 13 14 12 11 9 10 8 7 6 4 5 2 3 1 17

Identification 18

Methods Vital Non vital Mycorrhizal Non mycorrhizal 19

Methods No branching 2 branchings 4 branchings 20

Methods Mantle Hyphae Rhizomorph Clamps 21

Preliminary results Root tip vitality and ECM frenquency increase with N application (SAS, Glimmix proc) 100 80 60 40 22 Vital root tips (%) 20 a b b 0 20 40 Non-vital root tips (%) Mycorrhized root tips (%) a b c 100 80 60 40 20 Non-mycorrhized root tips (%) C LN HN C LN HN 0 20 40

Preliminary results Morphotypes increase with N application (SAS, Glm proc) Number Number of anatomorphotypes of anatomotypes 18 16 14 12 10 8 6 4 2 a ab b 0 C LN HN 23

Discussion ECM communities doesn t act as a whole Each morphotype vary independently - Specialisation - Overlap Functional groups Site initial state Scale effect Need to know more about ECM ecological traits and ECM species themselves 24

Acknowledgment FQRNT Ministère des ressources naturelles et de la faune Laboratoire d écologie végétale et animale UQAC Field team Club CL 50 Catherine Cathie, Lucie et Donald 25

Questions and comments 26