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Research ArticleResearch Article

Biocultural, Productive, and Ecocentric Restoration in La Mintzita Spring-fed Wetland, Michoacán, México

Esperanza Fuentes-Gutiérrez and Roberto Lindig-Cisneros
Ecological Restoration, March 2023, 41 (1) 44-54; DOI: https://doi.org/10.3368/er.41.1.44
Esperanza Fuentes-Gutiérrez
Escuela Nacional de Estudios Superiores, ENES-Morelia, Universidad Nacional Autónoma de México.
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Roberto Lindig-Cisneros
Laboratorio de Restauración Ambiental, Instituto de Investigaciones en Ecosistemas y Sustentabilidad, UNAM. Antigua Carretera a Pátzcuaro 8701, Ex-hacienda de San José de la Huerta, 58190 Morelia, Michoacan, México, .
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  • For correspondence: rlindig{at}iies.unam.mx
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    Figure 1.

    Species richness rarefaction curves for the 2005 and 2021 dry seasons showing a significant difference between years. Sampling unit was permanent plots along five transects.

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    Figure 2.

    Observed changes in total, wetland obligate, and wetland facultative species richness in the rainy seasons of the years 2005 and 2021. Sampling units for the period 2005 to 2015 are permanent plots and for 2021 the sampling units was the area defined by each transect length and a 1 m wide band centered in each transect.

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    Figure 3.

    Spatial distribution of the most abundant species in the La Mintzita wetland. Southern cattail (T. domingensis), common reed (P. australis), and tall fescue (F. arundinacea).

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    Figure 4.

    Areas impacted by low and high intensity grazing in the cover areas of the most abundant species. Southern cattail (T. domingensis), common reed (P. australis), and tall fescue (F. arundinacea).

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    Figure 5.

    Zoning proposed for environmental restoration of the La Mintzita wetland.

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    Softshell turtle. Source: Goodrich, S.G. 1859. Animal Kingdom Illustrated Vol 2. (New York, NY: Derby & Jackson), The Florida Center for Instructional Technology, College of Education, University of South Florida, fcit.usf.edu.

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    Table 1.

    Estimation of the potential productivity of handicraft units made from T. domingensis leaves in the La Mintzita per type of piece, hectare, and year. Except potential production data, all other values are means.

    ChestBoxMatSquare BasketBlowerCircular BasketTortilla Basket
    Embedded ImageEmbedded ImageEmbedded ImageEmbedded ImageEmbedded ImageEmbedded ImageEmbedded Image
    Weight (g)895.7355.4246.3160.1   87.4   73.3   31.3
    Leaves required per handicraft164.7   65.3   45.3   29.4   16.0   13.4    5.7
    Remnant material (length in cm) 4080 2720   680 1440   430   620   370
    Number of leaves needed for remnant material   20.2   13.5    3.3    7.1    2.1   03.0    1.8
    Total number of leaves needed for handicraft185.0   78.8   48.6   36.6   18.2   16.5    7.5
    Area of cattail needed for handicraft (m2)   4.74   2.02   1.24   0.93   0.46   0.42   0.19
    Potential production per hectare 2110 4950 806510753217392381052632
    Potential production for maximum usable cattail area in one year (1.2 ha) 2532 5941 967712903260872857163158
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Ecological Restoration: 41 (1)
Ecological Restoration
Vol. 41, Issue 1
March 2023
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Biocultural, Productive, and Ecocentric Restoration in La Mintzita Spring-fed Wetland, Michoacán, México
Esperanza Fuentes-Gutiérrez, Roberto Lindig-Cisneros
Ecological Restoration Mar 2023, 41 (1) 44-54; DOI: 10.3368/er.41.1.44

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Biocultural, Productive, and Ecocentric Restoration in La Mintzita Spring-fed Wetland, Michoacán, México
Esperanza Fuentes-Gutiérrez, Roberto Lindig-Cisneros
Ecological Restoration Mar 2023, 41 (1) 44-54; DOI: 10.3368/er.41.1.44
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  • Lessons Learned and Value of Early Post-Construction Monitoring of a Large Tidal Wetland Restoration Project
  • Strategic Pathways for Environmental Restoration
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Keywords

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