F. -Navarro* and -Vidal. *Phytopathology Phytopathology Program-Colegio de -Campus Montecillo, Franco Godinez **Phytopathology Program Postgraduados F. FrancoFranco-Navarro* and D. D. GodinezGodinez-Vidal. Program-Colegio de PostgraduadosPostgraduados-Campus Montecillo, Montecillo Montecillo 56230, 56230, Mexico Mexico State, -mail: [email protected]. State Mexico *E [email protected] State,, Mexico. Mexico.. *E*E-mail: [email protected].. Project: Conservation and Sustainable Management of BelowBelow-Ground Biodiversity [PROJECT FUNDED BY GEF] In Conservation and -Ground Below In the the context context ff the the Multinational Multinational Project Project ““Conservation and Sustainable Sustainable Management Management of of the the BelowBelow-Ground Biodiversity” ” (CSM/BGBD), ", Mexico, Biodiversity Tuxtlas Biodiversity” (CSM/BGBD), aa study study at at the the Biosphere Biosphere Reserve Reserve "Los "Los Tuxtlas", Tuxtlas", Mexico, to to determinate determinate the the effect effect of of different ed. Three conduct different land land use use intensities intensities on on the the soil soil nematodes nematodes was was conducted. conducted. Three localities localities into into the the Reserve Reserve were were chosen chosen as replications and from each of them, different fields belonging g to four land use intensities (Natural forest, belongin as replications and from each of them, different fields belonging to four land use intensities (Natural forest, Secondary selected Secondary forest, forest, Pasture Pasture fields fields and and Maize Maize fields) fields) were were selected. selected.. Ecological Ecological measures measures of of the the structure structure of of soil soil nematodes nd compared aand nematodes fauna, fauna, diversity, diversity, and and maturity maturity indices indiceswere wereassessed assessedand comparedamong among land land uses. uses.Fifty Fiftythree threefamilies families and and one one hundred hundred twenty twenty four four genera genera were were identified. identified. The The highest highest nematode nematode abundance, abundance, richness richness of of genera genera and and diversity condary forest. Se diversity corresponded corresponded to to Natural Natural forest, forest, closely closely followed followed by by Secondary Secondary forest. Intensive Intensive agricultural agricultural systems systems like like Maize -disturbed non Maize fields fields and and Pasture Pasture fields fields presented presented low low richness richness of of genera genera and and significant significant lower lower diversity diversity than than nonnon-disturbed systems. -parasitic nematodes plant systems. In In general, general, plantplant-parasitic nematodes and and bacterial bacterial feeders feeders were were the the most most dominant dominant and and abundant abundant in in the the study edators. The pr study area, area, followed followed by by fungal fungal feeders, feeders, omnivores omnivores and and finally finally predators. predators. The higher higher number number of of bacterial bacterial feeders feeders was was collected collected in in Pasture Pasture fields fields and and Maize Maize fields; fields; fungal fungal feeders feeders were were more more abundant abundant in in Maize Maize fields, fields, omnivores omnivores and and predators -parasitic in plant predators in in Natural Natural forest forest and and Secondary Secondary forest, forest, and and plantplant-parasitic in Secondary Secondary forest. forest. Some Some disturbance disturbance indices indices (Maturity (Maturity index, index, Plant Plant parasite parasite index, index, modified modified Maturity Maturity index, index, and and plant plant parasite parasite index/maturity index/maturity index index ratio) ratio) showed differences among land uses, corresponding most of the highest ghest values to nondisturbed systems hi non showed differences among land uses, corresponding most of the highest values to non-disturbed systems (Natural e food th (Natural and and Secondary Secondary forest). forest). In In general, general, the the conditions conditions of of the the food chain chain in in the the study study area area correspond correspond to to aa low low to -enriched, with eria, low non bact to moderate moderate disturbance, disturbance, nonnon-enriched, with canal canal of of decomposition decomposition balanced balanced by by fungi fungi and and bacteria, bacteria, low C/N C/N ratio and food chain in maturation. Most of the ecological indices es were ratio and food chain in maturation. Most of the ecological indic indices were useful useful to to establish establish significant significant effects effects of of different different land landuses uses on onsoil soil nematodes nematodes fauna fauna in in the the study study area. area. SAMPLING SAMPLING Soil disturbance indices based on soil nematodes fauna from sites sites with four land use intensities in the Biosphere Reserve “Los Tuxtlas” Tuxtlas”, Veracruz, Veracruz, Mexico. Index Natural forest Secondary forest Pasture fields Maize fields T Ff/Bf WI MI PPI mMI PPI/MI PPI/MI 2.57 ns 0.16 b 0.97 b 2.63 a 2.91 a 3.21 a 1.15 ns 2.31 ns 0.18 b 0.95 b 2.60 a 2.85 a 3.15 a 1.13 ns 2.11 ns 0.11 b 1.80 a 2.47 ab 2.68 b 2.93 a 1.18 ns Means followed by different letters are significantly different. ns= not significant. T= Trophic diversity index Ff/Bf= fungal feeders/bacterial feeders ratio WI= ratio of microbial feeder nematodes MI= maturity index PPI= plant parasite index mMI= mMI= modified maturity index PPI/MI= plant parasite index/maturity index ratio. BF 100% 90% 80% 70% 60% 50% 40% 30% 20% 10% 0% Natural forest FF OM Secondary forest 2.36 ns 0.45 a 3.49 a 2.37 b 2.68 b 2.87 b 1.18 ns PR PP Pasture fields Maize fields In each land use BIOSPHERE RESERVE “LOS TUXTLAS” TUXTLAS”, VERACRUZ, MEXICO 24 sampling points FOUR LAND USES BACTERIAL FEEDERS (distance: distance: 200 m) Maize fields Pasture fields PREDATORS Secondary forest Natural forest SUBSAMPLING POINT SAMPLING POINT IN THE GRID Mononchus Miconchus Prionchulus Mylonchulus Trypila Iotonchus Acrobeles Aphanolaimus Plectus Desmocolex Prismatolaimus Rhabditis Diploscapter EXTRACTION, EXTRACTION, COUNTING, COUNTING, PROCESSING PROCESSING & & MOUNTING MOUNTING EXTRACTION: Sieving– Sieving–Sugar flotation method (300 g per sample) sample) COUNTING: Three countings (1 ml) TOTAL: Average of 3 countings X 10. PERMANENT MOUNTINGS Nematodes killed by heat at 60° 60°C for 1 min, and then fixed with cold formalin 4% MASS DEHYDRATION OMNIVORES 53 Families & 124 Genera 12 a SIMPSON’ SIMPSON’S DIVERSITY INDEX ab 10 ab b 8 a 3 SHANNON’ SHANNON’S DIVERSITY INDEX ab 2.5 b ab 2 6 1.5 4 1 2 0.5 0 NATURAL FOREST SECONDARY FOREST PASTURE FIELDS 30 PLANTPLANTPARASITES a MAIZE FIELDS SECONDARY FOREST NATURAL FOREST GENERA RICHNESS b 25 0 b 20 b PASTURE FIELDS MAIZE FIELDS Helicotylenchus Criconema Ogma Discocriconemella Trophorus Hemicycliophora Xiphinema Pratylenchus Meloidogyne Trichodorus Mesodorylaimus Oriverutus Belondira Labronema Aporcelaimium FUNGAL FEEDERS Aphelenchus 15 10 5 0 NATURAL FOREST SECONDARY FOREST PASTURE FIELDS MAIZE FIELDS 1.1. ESQUIVEL, -145. 2. areas 131 ESQUIVEL, A. A. 2003. 2003. Nematode Nematode fauna fauna of of Costa Costa Rican Rican Protected Protected areas. areas.. Nematropica Nematropica 33(2): 33(2): 131131-145. 2. NEHER, NEHER, D. D. A. A. 2001. 2001. Role Role of of nematodes . Journal -168. 3.3.POWERS, indicators 161 nematodesin in soil soil health healthand andtheir their use use as as indicators. indicators. Journalof ofNematology Nematology33(4): 33(4): 161161-168. POWERS, T. T.O., O., NEHER, NEHER, D. D.A., A., MULLIN, MULLIN, P., P., ESQUIVEL, -DAVIS, R. -LORIO, L.. GIBLIN URIBE diversity ESQUIVEL,A., A., GIBLINGIBLIN-DAVIS, R. M., M., KANSAKI, KANSAKI, N., N., STOCK, STOCK,S.S. P., P.,MORA, MORA,M. M.M. M.&& URIBEURIBE-LORIO, L..2009. 2009.Tropical Tropicalnematode nematodediversity: diversity:: vertical -12. 4. rainforest Ecology 11-12. vertical stratification stratification of of nematode nematode communities communities in in aa Costa Costa Rican Rican humid humid lowland lowland rainforest. rainforest.. Molecular Molecular Ecology. Ecology.. pp. pp. 14. YEATES, YEATES, G. G. W., W., ng habits -an BONGERS, Feedi genera BONGERS, T., T., DE DE GOEDE, GOEDE, R. R. G. G. M., M., FRECKMAN, FRECKMAN, D. D. W. W. && GEORGIEVA, GEORGIEVA, S.S. S.S. 1993. 1993. Feeding Feeding habits in in soil soil nematode nematode families families and and generagenera-an outline -331. 315 outlinefor forsoil soilecologists. ecologists.Journal Journalof ofNematology Nematology25(3): 25(3):315315-331. 1
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