Red Balear 2020
María Isidora Santia
Created on November 13, 2019
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Transcript
SERVICIO DE SANIDAD FORESTAL, www.sanidadforestal.caib.essanidadforestal@caib.es
RED DE SEGUIMIENTO Y EVALUACIÓN DE DAÑOS EN LAS MASAS FORESTALES DE LAS ISLAS BALEARESAÑO 2020
Es una red de seguimiento fitosanitario cuya implantación se inicia durante los años 2008-2009 en Mallorca y 2010 en Menorca, Ibiza y Formentera.Coincide, por desdoblamiento, con la Red Europea de Nivel I (1987) y basada en su metodología. Se origina al superponer una malla 8*8 km sobre superficie forestal arbolada. El objetivo es un inventario periodico del estado fitosanitario de las masas arboladas, mediante el estudio de un conjunto de indicadores: defoliación, decoloración, mortalidad, agentes nocivos, etc.
43 Parcelas distribuidas por todas las Islas Baleares :Mallorca: 22Menorca: 10Ibiza: 9Formentera: 2 Representatividad: 1 punto cada 4.334 ha / 1 punto cada 20.708 ha (Nivel I)14 en áreas protegidas2 parcelas de la Red de Nivel II( Mallorca)2 parcelas que no se han podido evaluar
02
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: parcelas de control
Las parcelas constan de 24 árboles (dominantes o codominantes), distribuidos de 6 en 6, en orden de distancia y por cuadrantes, alrededor de un centro permanente.Se marcan, describen, referencian, miden periodicamente y evaluan fitosanitariamente, siempre los mismos árboles, salvo mortalidad ( que se sustituyen). Sobre cada uno de ellos se lleva a cabo una revisión fitosanitaria completa, que incluye su defoliación, decoloración y agentes nocivos. A su vez y en la mayoría de las parcelas están instrumentalizadas: 2 dendrómetros de banda para la medición de crecimiento continuo, 1 trampa Crosstrap con atrayente de Ips sexdentatus, 1 pluviómetro de cuchara y 1 sensor de temperatura. Revisión mensual. Funciona para el total de las parcelas desde febrero de 2016 y el objetivo es ampliar el conocimiento de las parcelas, y en extensión de la zona.Se pretende conocer la relación entre el clima y la actividad vegetativa o la incidencia que tienen los factores meteorológicos en el estado de salud del arbolado a largo plazo. Se miden tb, parámetros de Gestión Forestal Sostenible: madera muerta, fijación de carbono, distribución por clases diametricas, volumen de madera.....Prospección de sintomatología asociadada a organismos de cuarantena
03
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: parcelas de control
68 % Coníferas32 % Frondosas
Pinus halepensis: 675 piesQuercus Ilex: 201 piesOlea europaea var. sylvestris: 123 piesJuniperus phoenicea: 31 piesCeratonia siliqua: 1 pieRhamnus alaternus: 1 pieTOTAL: 1.032 pies
04
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares : composición de la muestra
05
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: meteorología
El valor de defoliación media (DM) en el conjunto de la masa forestal, se encuentra estable con tendencia a la baja, con un valor del 26%, clase moderada (CL2: def. 26-60%). El valor de DM en 2020 es casi un 1% menor que el de la evaluación precedente, y sigue siendo algo peor que la tasa de referencia (25% IR). La información actual queda más cerca de los peores años de la serie (2016 y 2017) que de los más favorables (2012 y anteriores).
06
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: defoliación media
La defoliación media para la población de encina se sitúa en el 23%, un dato de tipo ligero (CL1), sin variación resaltable.
En el caso de la muestra de pino carrasco, la DM se sitúa ahora en el 26% por lo que el indicador mejora (-1%), alejándose de los peores niveles de 2017 y 2016. El valor actual se halla casi un punto por encima del valor esperado (25% IR) y persiste dentro de una clase moderado-baja (CL2) de defoliación.
Entre las especies principales y en cuanto sus valores medios de defoliación se aprecia una débil tendencia positiva respecto a 2019. Se obtienen datos estables para acebuche y encina, y ligeramente más favorables en pino (-1% DM) y sabina (-4%).
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correspondiente a 2020.<span style='font-size: 10.0pt;mso-no-proof:yes'><o:p></o:p></span></p> </div> <![if !mso]></td> </tr> </table> <![endif]></v:textbox> </v:shape><w:wrap type="square" anchorx="margin" anchory="margin"/> </v:group><![endif]--><!--[if !vml]--><img width="607" height="391" src="file:///C:/Users/u134881/AppData/Local/Temp/msohtmlclip1/01/clip_image002.gif" align="left" v:shapes="Grupo_x0020_55 Imagen_x0020_2 Cuadro_x0020_de_x0020_texto_x0020_54"><!--[endif]--><!--EndFragment-->
07
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: DM especies
En el caso de la muestra de acebuche, alcanza un valor relativamente alto (35%) de tipo moderado-bajo (CL2), retomando la tendencia al alza de los anteriores años. En estos momentos se está al nivel de los inventarios con peores registros (2016 y 2017),
La defoliación media para el conjunto de la muestra de sabina, mejora no significativamente hasta el 26% (-4%), se persiste en un nivel moderado-bajo (CL2). A partir del peor dato (2016, 32%) parece presentarse una discreta recuperación
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correspondiente a 2020.<span style='font-size: 10.0pt;mso-no-proof:yes'><o:p></o:p></span></p> </div> <![if !mso]></td> </tr> </table> <![endif]></v:textbox> </v:shape><w:wrap type="square" anchorx="margin" anchory="margin"/> </v:group><![endif]--><!--[if !vml]--><img width="607" height="391" src="file:///C:/Users/u134881/AppData/Local/Temp/msohtmlclip1/01/clip_image002.gif" align="left" v:shapes="Grupo_x0020_55 Imagen_x0020_2 Cuadro_x0020_de_x0020_texto_x0020_54"><!--[endif]--><!--EndFragment-->
08
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: DM especies.
Por especies, la mortalidad actual, como es lo más común, se advierte mayoritariamente sobre pino carrasco con algún caso aislado adicional de encina. Previamente, en otros taxones únicamente se ha registrado algún caso en acebuche (2016: 1,6%) y también encina (2014: 2%).
Respecto a la mortalidad sucedida en 2020 en los puntos de seguimiento del conjunto de la Red Balear se observa, al igual que en el inventario anterior, un apreciable descenso del orden del 50% menos que la registrada el año anterior. Así la tasa de mortalidad se coloca en un aceptable 0,4% (-0,4%), muy lejos de los valores más altos (2016: 2,9%) y
09
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: mortalidad
En la relación de agentes nocivos implicados en la desaparición de pinos, durante 2020 la interacción más frecuente es la oportunista del escolítido Tomicus destruens y otros perforadores. Esto se produce en el 60% de las ocasiones y siempre en colaboración con otros agentes o en situaciones que previamente han debilitado o dañado los elementos o han favorecido su proliferación puntual. Finalmente, la mortalidad en el caso de la encina (1 pie) supone un 0,5% de su muestra, dato que se califica como admisible.
10
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: mortalidad
Actualmente, la cuantía de arbolado sin clorosis asciende hasta el 79%, con una mejora de +12% respecto a la información precedente. Los casos de decoloración ligera (CL1) suman un apreciable 19%, mientras que situaciones más altas (CL2 y CL3) apenas superan el 1%.
Durante 2020, en general se produce cierta relajación del valor de decoloración media (DecM) respecto al año pasado (-0,13), para alcanzar un 0,23. No obstante, aunque la media del momento queda más alta que la tasa de referencia disponible (0,16 IR), sigue catalogándose a nivel general como de tipo nulo (CL0).
11
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: DecM (decoloración media)
Por especies, cabe destacar el importante repunte de 2016 a partir de unos niveles previos prácticamente nulos para todos los taxones principales. En la actualidad, la mayoría se encuentra comparativamente en mejor estado, con Q. ilex, J. phoenicea y O. europaea en valores nulos o casi nulos.Todas las especies principales mejoran o al menos se mantienen estables respecto a 2019.
Territorialmente, las clorosis (siempre de carácter ligero CL1) se encuentran preferentemente en el sur de Mallorca, algunas zonas meridionales de Menorca, la mitad occidental de Ibiza y en toda la isla de Formentera.
12
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: decoloració.
El arbolado sin daños se amplía en 2020 hasta el 36% (+6%) del total de la muestra en seguimiento.
Respecto a la incidencia de los agentes nocivos con más peso relativo, puede decirse que esta es apreciablemente menor que en 2019 y que los de tipo abiótico (T4) vuelven a presentar los datos más altos, llegando a registrarse un peso actual de más del 35% (-4%) sobre la muestra general. Los denominados “otros” (T8), los hongos (T3) y los insectos (T2) se mueven en una horquilla entre el 29% (T8) y el 22% (T2). El resto de los tipos no tiene una presencia significativa: caza/ganado (2%) y actividades humanas (2%).
13
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: agentes nocivos
Respecto a agentes nocivos concretos, se estima relevante la incidencia sobre encina del cerambícido Cerambyx sp. que aparece en un 44% de los elementos.La mayor incidencia de Cerambyx sp. se encuentra en Menorca (60% de los elementos) donde aparece un 32% de pies dañados y un 11% de situaciones graves. En Mallorca la colonización asciende al 37% y la suma de encinas dañadas es apreciablemente menor (9%) y sin casos graves.Se encuentra el díptero Dryomyia lichtensteini, si bien su alcance sobre elementos dañados queda en un escaso 7%. Prácticamente todos los registros de este agente se encuentran en Menorca, donde se observa con una presencia bastante amplia (31%)Otros agentes reseñables con menor relevancia: Kermes vermilio, Diplodia sp., defoliadoresOtros agentes mucho más escasos son: Aceria ilicis, Phellinus torulosus ,Biscogniauxia mediterranea
14
Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: agentes nocivos
En el caso de pino carrasco, resalta la incidencia de procesionaria del pino (T. pityocampa), que abarca al 10% de la muestra general disminuyendo respecto a 2019.En Mallorca es más abundante (17%) que en Menorca (9%), En esta revisión no se ha observado a este agente en los pinos en seguimiento de Ibiza y Formentera.
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Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: agentes nocivos
Otro agente particularmente abundante sobre pino carrasco es el patógeno Thyriopsis halepensis, cuya incidencia general resulta la más elevada para la especie, alcanzando el 32%, con un 19% de dañados y <1% de casos graves.El patógeno está bastante presente en todas las islas si bien se estima significativamente más abundante en Formentera (63% de la muestra) e Ibiza (40%) que en Mallorca (26%) o Menorca (19%).Con ≥5% de incidencia general se registra el escolítido Tomicus destruens (5%); este agente se encuentra en todas las islas, y su incidencia oscila entre el 7% (Ibiza) y el 3% (Formentera).Respecto a Shaeropsis sapinea, su presencia general en arbolado dañado suma un 9%, pero su relación con casos graves es muy reducida (<1%) y solo aparecen en Mallorca.Otros agentes reseñables con menor relevancia: Sirococcus conigenus , resinosis, Phellinus pini y Mycosphaerella sp.
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Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: agentes nocivos
En el caso de acebuche (O. europaea), el agente más abundante es la bacteria Xylella fastidiosa que aparece en el 21% de la muestra general (+5%). El arbolado dañado por este motivo suma un 13% de los elementos en seguimiento, no relacionándose con mortalidad y apreciándose solo un 2% de casos graves. En su distribución por islas únicamente se tienen evidencias de su presencia en Menorca.En cuanto a las sabinas (J. phoenicea) que están en seguimiento en las parcelas de la Red Balear (31 Uds.), el agente que más incidencia presenta es la roya Gymnosporangium sabinae, registrándose en el 16% de los elementos si bien solamente el 10% puede considerarse dañado.Respecto a otros agentes, cabe resaltar los problemas derivados de la falta de iluminación, en general bastante extendidos (35% de la muestra de sabina), Phloeosinus sp. se presenta con una incidencia general del 10%
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Red de seguimiento y evaluación de daños en las masas forestales de las Islas Baleares: agentes nocivos
XYLELLA FASTIDIOSA
CYDALIMA PERSPECTALIS
XYLOSANDRUS COMPACTUS
LAGARTA PELUDA
GRAN CAPRICORNIO
PERFORADORES DEL PINO
PROCESIONARIA DEL PINO
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Estado Sanidad Forestal de las Islas Baleares
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Estado Sanidad Forestal de las Islas Baleares: procesionaria del pino
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Estado Sanidad Forestal de las Islas Baleares: Cerambyx cerdo
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Estado Sanidad Forestal de las Islas Baleares: Lymantria dispar
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Estado Sanidad Forestal de las Islas Baleares: Tomicus destruens y Orthotomicus erosus.
28 especies hospedantes de X. fastidiosa en la ZI de les I. Balears: Acacia saligna, Calicotome spinosa (aliaga), Cistus albidus, Cistus monpeliensis, Clematis cirrhosa (atragene balearica), Ficus carica, Fraxinus angustifolia, Genista lucida, Juglans regia, Lavandula angustifolia, Lavandula dentata, Nerium oleander, Olea europea var. europeae, Olea europea var. sylvestris, Phagnalon saxatile (manzanilla yesquera), Phillyrea angustifolia, Polygala myrtifolia, Prunus avium, Prunus domestica, Prunus dulcis, Rhamnus alaternus, Rosmarinus officinalis, Ruta chalepensis, Santolina magonica (camamilla de muntanya o de Maó), Teucrium capitatum (tomillo macho), Ulex parviflorus (aliaga morisca), Vitis vinifera i Salvia officinalis.ee
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Estado Sanidad Forestal de las Islas Baleares: Xylella fastidiosa
En Baleares, dos especies de boj: Buxus sempervirens L, y Buxus balearica Lam, especie endémica del mediterranio occidental, presente únicament en Balears y Andalucia, Argelia y Marruecos. B. balearica: ocupa ambito natural, principalmente Sierra de Tramuntana en Mallorca, y la isla de Cabrera. Especie incluida dentro del Catálogo Balear de Especies Protegides, dentro de la categoria “de Especial Protección”.
ACTUACIONES :Seguimento de las bojedas, instalación de trampas, seguimiento de depredadores y enemigos naturales, inspección de viveros y estudio de parasitismo
Primera constancia presencia insecte: octubre 2018, Alaró, Mallorca. AMA
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Estado Sanidad Forestal de las Islas Baleares:Cydalima perspectalis
Más pequeños (0,8-1,9 mm, adultos) -Color marrón oscuro
El genero Xylosandrus esta compuesto por 54 especies, de amplia distribución mundial. Coleoptero: Cucurlionidae, Scolytinae Especie nativas del Asia oriental que han colonizado otras partes del mundo; Especies exoticas, alta capacidad invasora y muy polifagas. -Escarabajos del grupo de ambrosia: simbiosis con hongos saprofíticos. Antes incluida en el lista EPPO 2009, actualment no. Organismos de cuarantena, anexo II del RE, UE 2019/2017 (escolítidos no europeos).
Camparini y Leza, UIB. 2019
Nov. 2019: 1 algarrobo con exudaciones abundantes en el verano y orificios multiples, en el jardín de una casa particular en El Toro, Calvià (Mallorca).
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Estado Sanidad Forestal de las Islas Baleares: Xylosandrus compactus
GRACIAS POR VUESTRA ATENCIÓN