說明
The avocado environmental mosaic of Michoacán primarily spans the mountainous region of the upper basin of the Balsas River, at altitudes between 1400 and 2100 meters. Avocado (Persea americana) orchards cover approximately 186,813 ha across at least 45 municipalities (where 50% or more of their territory is dedicated to avocado orchards), from the borders with the state of Mexico (in the extreme east) to the borders with the state of Jalisco (in the extreme west)(SIAP 2023). Within this mosaic, avocado orchards alternate with patches of native forests of various ages and degrees of disturbance and other crops such as berries (raspberries, strawberries), traditional maize-agriculture systems (milpa), forestry areas and population centers (SIAP 2023). Notably, the avocado mosaic also encompasses five national protected areas such as the Monarch Butterfly Biosphere Reserve, the Pico de Tancítaro Flora and Fauna Protection Area, and the Barranca del Cupatitzio National Park.
Mexico is a country of bees! Mexico is home to approximately 2,100 wild bee species, representing 10% of the global richness of these insects (approx. 21,000 spp) (Michener 2000; Sagot et al. 2023). Wild bees, together with the honeybee (Apis mellifera) and other animal groups (e.g., Bats, Hummingbirds, Butterflies, Beetles) are recognised as pollinating agents for at least 1/3 of our food (Winfree et al. 2007; Ruiz-Toledo et al. 2020). In particular, at least 50 species of wild bees in Mexico have been documented as pollinating agents of high economic importance for their role in the production of chillies, tomatoes, beans, pumpkins, chayotes, oranges, and, of course, avocado (Vergara 2023). However, the richness of wild bees contributing to the pollination of agricultural products in Mexico is a growing field of applied research, so the number of species may be much greater.
Avocado is, together with agave (Agave tequilana), an agricultural crop of high economic value for Mexico. However, the unregulated establishment and expansion in certain regions of the avocado belt have been linked to increased deforestation, restricted water access and availability, and increased application of agrochemical inputs for pest and weed control (Denvir et al. 2021, Latorre-Cárdenas et al. 2023). However, we have only just begun to understand the extent, direction, and magnitude of the impact of avocado mosaic establishment on biodiversity. Indeed, despite its economic importance, information on avocado floral visitors is relatively limited. Data on the communities of floral visitors and native pollinators in the Mexican avocado mosaic is much scarcer (and scattered) (Ish-Am et al. 1999; Castañeda-Vildózola et al. 1999; Can-Alonzo et al. 2005; Villamil et al. 2017; Dymond et al. 2021).
In this sense, we need to increase our efforts to understand how the structure of native pollinating insect communities varies, which can not only visit avocado flowers but also contribute to the persistence of the (non-cultivated) flora associated with the avocado mosaic, and thus to the persistence of the ecosystem services they provide (e.g., pollination, insect pest control, water retention, maintenance of soil structure and nutrient fixation).
Regarding wild bees, studies have reported at least nine species of Stingless Bees (Tribe: Meliponini) (Ish-Am et al. 1999, Castañeda-Vildózola et al. 1999, Can-Alonzo et al. 2005), three genera of wild bees as floral visitors to avocado (Ish-Am et al. 1999, Castañeda-Vildózola et al. 1999), six genera and three species as avocado pollen carriers (Villamil-Echeverri et al. 2014), and 20 genera and 50 species of wild bees as floral visitors to herbaceous plants associated with the avocado mosaic in Michoacán (Cultid-Medina et al. 2021; AGUHA Project Team 2022). Despite this, a comprehensive list with a high taxonomic resolution of the wild bee species that can be floral visitors and potential effective native pollinators of Michoacán avocado crops (excluding the honeybee, Apis mellifera) is still lacking.
The most recent global review of avocado pollinating insects indicates that (Dymond et al. 2021): i) Although Mexico is part of the center of origin of avocado and one of the largest producers worldwide, only five studies have been formally published evaluating any aspect of insect contribution to avocado pollination ecology and ii) concerning bees, the few published studies have focused on Apis mellifera (a non-native species in the Americas) and at least four species of stingless bees (Tribe Meliponini). Therefore, we do not know the richness and structure of wild bee communities that may be associated with avocado cultivation and its agroecological environment.
This dataset provides a taxonomic list, ecomorphological traits of valid species, and known distributions of these species on a global scale (at the country level) and in Mexico (at the state level). Importantly, taxonomy and ecomorphological traits are unified with the GBIF dataset “Taxonomic Diversity and Ecomorphological Traits of Wild Bees in Mexico and Mesoamerica” (Sagot et al. 2023).
資料紀錄
此資源名錄的資料已發佈為達爾文核心集檔案（DwC-A），其以一或多組資料表構成分享生物多樣性資料的標準格式。 核心資料表包含 218 筆紀錄。
亦存在 2 筆延伸集的資料表。延伸集中的紀錄補充核心集中紀錄的額外資訊。 每個延伸集資料表中資料筆數顯示如下。
此 IPT 存放資料以提供資料儲存庫服務。資料與資源的詮釋資料可由「下載」單元下載。「版本」表格列出此資源的其它公開版本，以便利追蹤其隨時間的變更。
版本
以下的表格只顯示可公開存取資源的已發布版本。
如何引用
研究者應依照以下指示引用此資源。:
Vázquez Lenis E A, Cultid-Medina C A, Sagot P, Mérida-Rivas J, González-Vanegas P A, Guarín Anacona A, Flores Pérez L R, Vandame R (2025). Wild bee species of the avocado mosaic of Michoacan, Mexico: Taxonomic and ecomorphological traits. Version 1.5. Instituto de Ecología A.C. Centro Regional del Bajío. Checklist dataset. http://iptinecolbajio.inecol.mx/resource?r=abejas_nativas_mosaico_aguacatero_mich&v=1.5
GBIF 註冊
此資源已向GBIF註冊，並指定以下之GBIF UUID: 09481069-bcc4-4740-9882-077d120e16cc。 Instituto de Ecología A.C. Centro Regional del Bajío 發佈此資源，並經由Biodiversity Information System of Mexico同意向GBIF註冊成為資料發佈者。
關鍵字
Checklist wild bees; avocado environmental mosaics; ecomorphological traits; Mexican transitions zone; Inventory Regional; Michoacán Avocado Belt
聯絡資訊
- 出處 ●
- 連絡人
https://orcid.org/00-0003-1290-7454
- 作者
- 出處
- 出處
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地理涵蓋範圍
Between the municipalities of Tacámbaro (far east) and Peribán (far west) (19.372028°N, -102.440338°W; 18.970972°N, - -101.639468°) between 1470 m and 2552 m elevation. Thus, the sampling covers an area of influence of approximately 14300 ha, corresponding to 1.2% of the area currently surveyed and covered by avocado orchards in Michoacán (SIAP 2022). The area of sampling influence included agricultural areas adjacent or close to the outer limits of the Barranca del Cupatitzio National Park and Pico de Tancítaro Flora and Fauna Protection Area.
| 界定座標範圍 | 緯度南界 經度西界 [-90, -180], 緯度北界 經度東界 [90, 180] |
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分類群涵蓋範圍
The list includes 218 species (78 valid species and 140 morphospecies determined to genus level) and 49 genera from five families (Hymenoptera: Apoidea: Anthophila). Species and morphospecies were reviewed with the help of the Bee Collection (ECOAB) sensu Michener (2007) of the Abejas group of El Colegio de la Frontera Sur (ECOSUR, San Cristóbal de las Casas) under the direction of Dr. Rémy Vandame.
| Genus | Perdita sp.1, Perdita sp.2, Pseudopanurgus sp. 1, Deltoptila sp. 1, Deltoptila sp. 2, Deltoptila sp. 3, Deltoptila sp. 4, Deltoptila sp. 5, Deltoptila sp. 6, Eufriesea sp. 1, Melissodes sp.1, Colletes sp. 1, Colletes sp. 2, Colletes sp. 3, Colletes sp. 4, Colletes sp. 5, Colletes sp. 6, Colletes nr. skinneri, Augochlora sp. 1, Temnosoma sp. 1, Dinagapostemon sp. 1, Habralictus sp. 1, Sphecodes sp. 1, Sphecodes sp. 2, Sphecodes sp. 3, Sphecodes sp. 4, Sphecodes sp. 5, Sphecodes sp. 6, Sphecodes sp. 7, Sphecodes sp. 8, Sphecodes sp. 9, Sphecodes sp. 10, Anthodioctes sp. 1, Dianthidium sp. 1, Ashmeadiella sp. 1, Heriades sp. 1 |
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| Subgenus | Andrena (Callandrena) sp.1, Andrena (Callandrena) sp.2, Andrena (Callandrena) sp.3, Andrena (Callandrena) sp.4, Andrena (Callandrena) sp.5, Andrena (Callandrena) sp.6, Andrena (Callandrena) sp.8, Protandrena (Heterosarus) sp. 1, Protandrena (Heterosarus) sp. 2, Protandrena (Heterosarus) sp. 3, Protandrena (Heterosarus) sp. 4, Protandrena (Heterosarus) sp. 5, Protandrena (Heterosarus) sp.6, Protandrena (Heterosarus) sp. 7, Protandrena (Heterosarus) sp. 8, Protandrena (Heterosarus) sp. 9, Protandrena (Heterosarus) sp. 10, Protandrena (Heterosarus) sp. 11, Protandrena (Heterosarus) sp. 12, Protandrena (Heterosarus) sp. 13, Protandrena (Protandrena) sp. 1, Protandrena (Pterosarus) sp.1, Protandrena (Pterosarus) sp. 2, Protandrena (Pterosarus) sp. 3, Protandrena (Pterosarus) sp. 4, Protandrena (Pterosarus) sp. 5, Protandrena (Pterosarus) sp. 6, Protandrena (Pterosarus) sp. 7, Protandrena (Pterosarus) sp. 8, Protandrena (Pterosarus) sp. 9, Protandrena (Pterosarus) sp. 10, Protandrena (Pterosarus) sp. 11, Protandrena (Pterosarus) sp. 12, Protandrena (Pterosarus) sp. 13, Ceratina (Ceratinula) nr. trimaculata, Ceratina (Zadontomerus) sp. 1, Ceratina (Zadontomerus) sp. 2, Ceratina (Zadontomerus) sp. 3, Ceratina (Zadontomerus) sp. 4, Ceratina (Zadontomerus) sp. 5, Ceratina (Zadontomerus) sp. 6, Melissodes (Eumelissodes) sp. 1, Melissodes (Eumelissodes) sp. 2, Melissodes (Melissodes) sp. 1, Melissodes (Melissodes) sp. 2, Tetraloniella (Tetraloniella) sp. 1, Hylaeus (Hylaeana) sp1, Augochlora (Augochlora) sp. 1, Augochlora (Augochlora) sp. 2, Augochlora (Augochlora) sp. 3, Augochlora (Augochlora) sp. 4, Augochlora (Augochlora) sp. 5, Caenaugochlora (Caenaugochlora) sp. 1, Lasioglossum (Dialictus) sp. 1, Lasioglossum (Dialictus) sp. 2, Lasioglossum (Dialictus) sp. 3, Lasioglossum (Dialictus) sp. 4, Lasioglossum (Dialictus) sp. 5, Lasioglossum (Dialictus) sp. 6, Lasioglossum (Dialictus) sp. 7, Lasioglossum (Dialictus) sp. 8, Lasioglossum (Dialictus) sp. 9, Lasioglossum (Dialictus) sp. 10, Lasioglossum (Dialictus) sp. 11, Lasioglossum (Dialictus) sp. 12, Lasioglossum (Dialictus) sp. 13, Lasioglossum (Dialictus) sp. 14, Lasioglossum (Dialictus) sp. 15, Lasioglossum (Dialictus) sp. 16, Lasioglossum (Dialictus) sp. 17, Lasioglossum (Dialictus) sp. 18, Lasioglossum (Dialictus) sp. 19, Lasioglossum (Dialictus) sp. 20, Lasioglossum (Dialictus) sp. 21, Lasioglossum (Dialictus) sp. 22, Lasioglossum (Dialictus) sp. 23, Lasioglossum (Dialictus) sp. 24, Lasioglossum (Dialictus) sp. 25, Lasioglossum (Dialictus) sp. 26, Lasioglossum (Dialictus) sp. 27, Lasioglossum (Dialictus) sp. 28, Lasioglossum (Dialictus) sp. 29, Lasioglossum (Dialictus) sp. 30, Lasioglossum (Dialictus) sp. 31, Lasioglossum (Dialictus) sp. 32, Lasioglossum (Dialictus) sp. 33, Lasioglossum (Eickwortia) nyctere, Lasioglossum (Hemihalictus) sp. 1, Lasioglossum (Hemihalictus) sp. 2, Lasioglossum (Hemihalictus) sp. 3, Lasioglossum (Hemihalictus) sp. 4, Lasioglossum (Hemihalictus) sp. 5, Lasioglossum sp1, Lasioglossum (Sphecodogastra) sp. 1, Lasioglossum (Sphecodogastra) sp. 2, Lasioglossum (Sphecodogastra) sp. 3, Lasioglossum (Sphecodogastra) sp. 4, Lasioglossum (Sphecodogastra) sp. 5, Lasioglossum (Sphecodogastra) sp. 6, Paranthidium (Paranthidium) aff. gabbii, Paranthidium (Rapanthidium) sp. 1, Megachile (Leptorachis) sp. 1, Megachile (Chelostomoides) sp. 1 |
| Species | Andrena (Callandrena) aerifera, Andrena (Callandrena) discreta, Andrena (Callandrena) levigata, Andrena (Callandrena) micheneriana, Andrena (Callandrena) repanda, Calliopsis (Calliopsis) teucrii, Protandrena (Heterosarus) asperatus, Protandrena (Heterosarus) bakeri, Protandrena (Pseudopanurgus) mexicana, Bombus (Pyrobombus) ephippiatus, Bombus (Thoracobombus) pensylvanicus sonorus, Bombus (Thoracobombus) weisi, Centris (Centris) varia, Centris (Heterocentris) transversa Pérez, 1905, Centris (Melacentris) agiloides, Centris (Paracentris) laevibullata, Centris (Paracentris) nigrocaerulea, Centris (Xanthemisia) purepecha, Ceratina (Zadontomerus) ignara, Ceratina (Zadontomerus) indigovirens, Ceratina (Zadontomerus) kopili, Ceratina (Zadontomerus) nautlana, Ceratina (Zadontomerus) raquelitae, Ceratina (Zadontomerus) rehanae, Ceratina (Zadontomerus) tepetlana, Epeolus flavofasciatus, Epeolus obscuripes, Eufriesea rugosa, Euglossa (Euglossa) viridissima, Eulaema (Apeulaema) cingulata, Eulaema (Apeulaema) polychroma, Melitoma nudicauda, Peponapis atrata, Peponapis pruinosa, Thygater micheneri, Thygater montezuma, Xenoglossa fulva, Exomalopsis (Exomalopsis) analis, Exomalopsis (Exomalopsis) tepaneca, Geotrigona (Chthonotrigona) acapulconis, Nannotrigona perilampoides, Partamona (Partamona) bilineata, Plebeia manantlensis, Xylocopa (Xylocopoides) cyanea, Xylocopa (Neoxylocopa) fimbriata, Xylocopa (Neoxylocopa) gualanensis, Xylocopa (Notoxylocopa) guatemalensis, Xylocopa (Schonnherria) loripes, Augochlora (Augochlora) nigrocyanea, Augochlora (Augochlora) quiriguensis, Augochlora (Augochlora) smaragdina, Augochlorella (Augochlorella) neglectula, Augochloropsis (Paraugochloropsis) metallica, Caenaugochlora (Caenaugochlora) inermis, Pseudaugochlora graminea, Agapostemon (Notagapostemon) leunculus, Agapostemon (Agapostemon) texanus, Halictus (Odontalictus) ligatus, Halictus (Seladonia) lutescens, Lasioglossum (Lasioglossum) circinatum, Lasioglossum (Lasioglossum) manitouellum, Lasioglossum (Lasioglossum) transvorsum, Lasioglossum (Lasioglossum) tricnicos, Mexalictus (Mexalictus) mexicanus, Mexalictus (Mexalictus) verdazulus, Dianthidium (Adanthidium) anophrys, Coelioxys (Boreocoelioxys) pratti, Megachile (Acentron) albitarsis, Megachile (Argyropile) flavihirsuta, Megachile (Sayapis) inimica, Megachile (Cressoniella) zapoteca, Heriades (Neotrypetes) bruneri, Bombus (Thoracobombus) diligens |
| Subspecies | Xylocopa (Stenoxylocopa) micheneri decipiens, Xylocopa (Notoxylocopa) tabaniformis azteca, Xylocopa (Notoxylocopa) tabaniformis tabaniformis, Anthidiellum (Loyolanthidium) notatum gilense, Bombus (Thoracobombus) pensylvanicus sonorus |
時間涵蓋範圍
| 起始日期 / 結束日期 | 2022-10-01 / 2022-11-30 |
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計畫資料
To contribute to the taxonomic knowledge of insect floral visitors and potential pollinators in the primary geographical and ecosystemic region of global avocado production (Michoacán, Mexico). Thus, we mobilized the first curated and consensual list of wild bee species associated with the avocado mosaic in Michoacán, Mexico. In this way, it seeks to provide baseline information for the sustainable monitoring and regulation of the expansion of the avocado agricultural frontier in Mexico. This list is a product of the master thesis entitled "Avocado, forests and wild bees in Northeastern Michoacán, Mexico: A Taxonomic and Functional Approach", developed by Elder Andrés Vásquez Lenis under the direction of Dr. Carlos A. Cultid Medina (INECOL, Centro Regional del Bajío) and Dr. Rémy Vandame (ECOAB-ECOSUR, San Cristóbal de las Casas).
| 計畫名稱 | "Avocado, forests and wild bees in Northeastern Michoacán, Mexico: A Taxonomic and Functional Approach" |
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| 經費來源 | This thesis was conducted in the framework of the AGUHA Project: “Aguacate, Herbáceas y Abejas nativas” (2019 - 2023), co-funded by the Researchers for Mexico project (No. 673) under the direction of Dr. Cultid-Medina. |
參與計畫的人員:
取樣方法
Between September and November 2022, landscape-scale wild bee sampling was conducted in 11 hexagonal landscape samples (1300 ha each) spanning the municipalities of Tacámbaro (far east) and Peribán (far west) (19.372028°N, -102.440338°W; 18.970972°N, - -101.639468°) and an elevation range of 1470 to 2552 m. Thus, the sampling covers an area of influence of approximately 14300 ha, corresponding to 1.2% of the area currently surveyed and covered by avocado orchards in Michoacán (SIAP 2022). The sampled areas included agricultural lands adjacent to or near the boundaries of Barranca del Cupatitzio National Park and Pico de Tancítaro Flora and Fauna Protection Area.
| 研究範圍 | Avocado landscape between the municipalities of Tacámbaro (far east) and Peribán (far west) (19.372028°N, -102.440338°W; 18.970972°N, - -101.639468°) between 1470 m and 2552 m elevation. |
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| 品質控管 | Species and morphospecies were reviewed using the Bee Collection (ECOAB) and following Michener (2007). |
方法步驟描述:
- Trapping with nets was carried out ad libitum along the floral strips inside the orchards and at the orchard-forest edge. Pan-traps were distributed along six 100 m line transects per landscape sample; blue, yellow and white pan-traps alternated within each transect. Sampling sites within the landscape samples were separated by a distance between 300 m and 1 km. Sampling was carried out simultaneously by a team of three people on two effective capture days per landscape sample, with a sampling effort of 231 person-hours, 693 total net sampling hours, and approximately 700 total pan-trap sampling hours.
收藏資料
| 蒐藏名稱 | Anexo regional de la Colección Entomológica IEXA, Colección del Centro Occidente Mexicano (IEXA-CECOM). |
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| 蒐藏編號 | https://tic-inecol.mx/cecom/menu_publico/ |
| 上層採集品識別碼 | IEXA (VER.IN.048.0198) |
| 標本保存方法 | Pinned |
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| 管理單位 | 在...之間 5,765 和 12,979 Cornell Box |
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引用文獻
- Sagot P, Mérida J, González-Vanegas PA, Vandame R, Cultid-Medina CA, Barrios JM (2023). Diversidad taxonómica y rasgos ecomorfológicos de las abejas silvestres en México y Mesoamérica. Versión 1.5. Comisión nacional para el conocimiento y uso de la biodiversidad. Conjunto de datos de lista de verificación https://doi.org/10.15468/m78tu9, consultado a través de GBIF.org el 9 de abril de 2025. https://doi.org/10.15468/m78tu9
- Dymond, K., Celis‐Diez, J. L., Potts, S. G., Howlett, B. G., Willcox, B. K., & Garratt, M. P. (2021). The role of insect pollinators in avocado production: A global review. Journal of Applied Entomology, 145(5), 369-383. https://doi.org/10.1111/jen.12869
- SIAP. 2023. https://nube.agricultura.gob.mx/cierre_agricola/. Consultado el 17 de Junio de 2022. https://nube.agricultura.gob.mx/cierre_agricola/
- Michener, C.D. 2007. The Bees of the World. [2ª edition] Johns Hopkins University Press, Baltimore, MD; xvi+[i]+953 pp.+20 pls.
- Winfree, R., Williams, N. M., Dushoff, J., & Kremen, C. (2007). Native bees provide insurance against ongoing honey bee losses. Ecology letters, 10(11), 1105-1113. https://doi.org/10.1111/j.1461-0248.2007.01110.x
- Ruiz-Toledo, J., Vandame, R., Penilla-Navarro, P., Gómez, J., & Sánchez, D. (2020). Seasonal abundance and diversity of native bees in a patchy agricultural landscape in Southern Mexico. Agriculture, Ecosystems & Environment, 292, 106807. https://doi.org/10.1016/j.agee.2019.106807
- Vergara Briceño C. H. (coord.) (2023) Abejas nativas mexicanas como potenciales polinizadores manejados. Comunicación Científica. México. https://doi.org/10.52501/cc.126
- Latorre-Cárdenas, M. C., González-Rodríguez, A., Godínez-Gómez, O., Arima, E. Y., Young, K. R., Denvir, A., ... & Ghilardi, A. (2023). Estimating fragmentation and connectivity patterns of the temperate forest in an avocado-dominated landscape to propose conservation strategies. Land, 12(3), 631. https://doi.org/10.3390/land12030631
- Ish-Am, G., Barrientos-Priego, F., Castañeda-Vildozola, A., & Gazit, S. (1999). Avocado (Persea americana Mill.) pollinators in its region of origin. Revista Chapingo Serie Horticultura, 5, 137-143.
- Castañeda-Vildózola, A., Equihua-Martínez, A., Valdés-Carrasco, J., Barrientos-Priego, A. F., Ish-Am, G., & Gazit, S. (1999). Insectos polinizadores del aguacatero en los estados de México y Michoacán. Revista Chapingo Serie Horticultura, 5, 129–136.
- Can-Alonzo, C., Quezada-Euán, J. J. G., Xiu-Ancona, P., Moo-Valle, H., Valdovinos-Nunez, G. R., & Medina-Peralta, S. (2005). Pollination of ‘criollo’avocados (Persea americana) and the behaviour of associated bees in subtropical Mexico. Journal of Apicultural Research, 44(1), 3-8. https://doi.org/10.1080/00218839.2005.11101138
- Villamil L, Astier M, Merlín Y, Ayala-Barajas R, Ramírez-García E, Martínez-Cruz J, Mariano Devoto & Mayra E. Gavito (2017). Management practices and diversity of flower visitors and herbaceous plants in conventional and organic avocado orchards in Michoacán, Mexico, Agroecology and Sustainable Food Systems. https://doi.org/10.1080/21683565.2017.1410874
- Denvir, A., García-Oliva, F., Arima, E. Y., Latorre-Cárdenas, M. C., González-Rodríguez, A., Young, K. R., & De La Cruz, L. I. L. (2024). Sustainability implications of carbon dynamics on the avocado frontier. Agriculture, Ecosystems & Environment, 359, 108746. https://doi.org/10.1016/j.agee.2023.108746
- Cultid-Medina, C. A., González-Vanegas, P., Bedolla-García, B., & Equipo AGUHA. 2021. Proyecto AGUHA: Aguacate, Herbáceas y Abejas nativas. EcoLógico, 2(2): 35 – 41.
- AGUHA Project Team 2022: Carlos A. Cultid-Medina*; Brenda Bedolla García**, Paola A. González Vanegas; Javier Hernández Acosta; Philippe Sagot; Jorge Merida; Daniel Madrigal; Elder A. Vásquez Lenis. Autores de correspondencia:* carlos.cultid@inecol.mx; ** brenda.bedolla@inecol.mx https://www.inecol.mx/index.php/divulgacion/ciencia-hoy/abejas-nativas-herbaceas-y-huertas-de-aguacate
- Villamil, L., Astier, M., Merlín, Y., Ayala-Barajas, R., Ramírez-García, E., Martínez-Cruz, J., ... & Gavito, M. E. (2018). Management practices and diversity of flower visitors and herbaceous plants in conventional and organic avocado orchards in Michoacán, Mexico. Agroecology and Sustainable Food Systems, 42(5), 530-551. https://doi.org/10.1080/21683565.2017.1410874
額外的詮釋資料
| 替代的識別碼 | 09481069-bcc4-4740-9882-077d120e16cc |
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| http://iptinecolbajio.inecol.mx/resource?r=abejas_nativas_mosaico_aguacatero_mich |