monarch mapping understanding spatial patterns ... · many butterfly populations. the western...

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METHODS: Extraction of Landscape Characteristics: Here, I used ArcGIS to explore environmental varia- bles (wind intensity, light pollution, land use, habitat frag- mentation, and elevation) characterizing 10 km buffers sur- rounding overwintering sites. Each data layer was raster- ized with a cell size of 30 square meters. I calculated aver- age elevation and value of light intensity for each overwin- tering site using zonal spatial analyst tools. I tabulated the area of each landscape class (forest, urban, herbaceous/ crop, and open water) for each buffer zone, as well as the proportion of each buffer exposed to high winds. In order to determine habitat fragmentation, I calculat- ed heterogeneity of land use. By calculating the number of unique cells in a circular neighborhood using the block sta- tistics tool, I was able to create a new raster with values specifying the heterogeneousness of the environment sur- rounding each cell. Site Suitability Analysis: I created maps to visualize habitat suitability based on a combination of criteria identified by Pelton et al. (2016) and my wild extrapolations. Datasets were reclassified based on these criteria. Areas with suitable wind speed (below 5.86 m/s), and land cover (forest) were given high values. Elevations between 60—90 meters considered ide- al, and below 60 acceptable. Habitat fragmentation and light pollution were ranked, with lower numbers indicating increased fragmentation and pollution. Habitats a distance of 25 were considered acceptable, although a distance of 2.4 km was considered ideal. If a landscape characteristic was unsuitable for monarchs, it was given a value of 0. A new raster data set characterizing site suitability was creat- ed by multiplying raster values. I included all previously identified overwintering sites as suitable. MONARCH MAPPING UNDERSTANDING SPATIAL PATTERNS CHARACTERIZING MONARCH BUTTER- FLY OVERWINTERING SITES Habitat fragmentaon surrounding Monarch overwinter- ing sites (cell size 30 by 30 meters) Elevaon in meters surrounding Monarch overwintering sites (cell size 30 by 30 meters) Wind Intensity at 50 meter height surrounding Monarch overwintering sites (cell size 30 by 30 meters) Urban light polluon at Monarch overwintering sites (30 arc second grids, cell size reclassified 30 by 30 meters) Land use surrounding Monarch overwintering sites (cell size 30 by 30 meters) Habitat suitability of coastal overwintering sites for Monarch buerflies INTRODUCTION: Across North America, the pressures of habitat loss and agricultural intensification on have led to major declines in many butterfly populations. The Western Monarch butter- fly, one of the most charismatic and well-studied butterfly species, is no exception, with population declines of 74% since the 1990s (Pelton et al. 2016). Efforts to conserve monarch butterflies mainly focus on providing breeding and migratory habitat. However, loss of overwintering habitat due to development, increased pesticide use, and climate change may further threaten this species. Western Monarch butterflies are migratory. During the winter, colonies of butterflies and overwinter in tall trees along the California coast. These overwintering sites are commonly located no further than 1.5 miles from the ocean, at sunny sites with low elevation and without high winds. Butterflies mate and disperse from overwintering sites in February or March. During the spring and summer, butterflies migrate northward. Several generations of but- terflies may emerge during the summer: the last generation will return to the coast in the fall. Here, I will explore the landscape patterns of habitats surrounding monarch overwintering sites, using measures of landscape composition, habitat fragmentation, urban light pollution, wind intensity, and elevation. I will also identify suitable overwintering habitats based on landscape criteria. RESULTS AND CONCLUSIONS: Urbanized areas made up a considerable proportion of buffer zones surrounding overwintering sites, composing an average of 30% of raster cells within a buffer zones. For 12 study sites, urban environments made up >95% of the buff- er zone; only 21 of 485 buffer zones contained no urbanized raster cells. In comparison, forested areas composed an av- erage of 7.5 % of raster cells within a buffer zones. Most sites were affected by light pollution at some level (91%). Further analysis is necessary to determine the effects of ur- banization on overwintering butterflies. While urbanization is associated with habitat loss, the reduction of pesticide use may impact butterfly populations positively. A report by the Xerces society found that most Mon- arch butterfly overwintering sites are found at an elevation between 60 and 90 meters, and at areas with low wind speeds. My results confirm these findings. Elevations at monarch overwintering sites ranged between 0 and 469.5 meters. The average elevation for monarch overwintering sites was 60.5 meters (SD 53.2). Most overwintering sites were located in areas with low wind speeds at 50 meters. Most buffer zones (274 out of 488) contained no cells rep- resenting wind speeds of greater than 5.6 meters/second at 50 meters above ground. Site suitability for monarch butterflies should be ad- dressed at a fine scale, as microclimate factors may be im- portant in determining where monarchs aggregate. Howev- er, this site suitability analysis provides some insights to the locations of potential habitats. According to the criteria of this analysis, a low proportion of coastal habitats are suita- ble for monarch: this analysis may be used to aide research- ers in searching for monarch overwintering sites. Cartographer: Genevieve Pugesek Date: 5/9/17 Professor: Barbara Parmenter, Class: UEP 0232 Intro to GIS Projection: California Teale Albers, NAD83 projection Sources: The Xerces Society’s Western Monarch Overwintering Sites Database, The National Renewable Ener- gy Laboratory GIS Data, U.S. Geological Survey National Elevation Dataset, U.S. Geological Survey National Landcover Data Base, Defense Meteorological Satellite Program Nighttime Lights Time Series, ESRI, USGS National Assessment of Shoreline Change Vector Shorelines Literature cited: Pelton, Jepsen, Schultz, Fallon, Black. (2016). State of the Monarch Butterfly Overwintering sites in California. The Xerces Society for Invertebrate Conservation, Portland, Oregon.

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Page 1: MONARCH MAPPING UNDERSTANDING SPATIAL PATTERNS ... · many butterfly populations. The Western Monarch butter-fly, one of the most charismatic and well-studied butterfly species, is

METHODS:

Extraction of Landscape Characteristics:

Here, I used ArcGIS to explore environmental varia-

bles (wind intensity, light pollution, land use, habitat frag-

mentation, and elevation) characterizing 10 km buffers sur-

rounding overwintering sites. Each data layer was raster-

ized with a cell size of 30 square meters. I calculated aver-

age elevation and value of light intensity for each overwin-

tering site using zonal spatial analyst tools. I tabulated the

area of each landscape class (forest, urban, herbaceous/

crop, and open water) for each buffer zone, as well as the

proportion of each buffer exposed to high winds.

In order to determine habitat fragmentation, I calculat-

ed heterogeneity of land use. By calculating the number of

unique cells in a circular neighborhood using the block sta-

tistics tool, I was able to create a new raster with values

specifying the heterogeneousness of the environment sur-

rounding each cell.

Site Suitability Analysis:

I created maps to visualize habitat suitability based on

a combination of criteria identified by Pelton et al. (2016)

and my wild extrapolations. Datasets were reclassified

based on these criteria. Areas with suitable wind speed

(below 5.86 m/s), and land cover (forest) were given high

values. Elevations between 60—90 meters considered ide-

al, and below 60 acceptable. Habitat fragmentation and

light pollution were ranked, with lower numbers indicating

increased fragmentation and pollution. Habitats a distance

of 25 were considered acceptable, although a distance of

2.4 km was considered ideal. If a landscape characteristic

was unsuitable for monarchs, it was given a value of 0. A

new raster data set characterizing site suitability was creat-

ed by multiplying raster values. I included all previously

identified overwintering sites as suitable.

MONARCH MAPPING UNDERSTANDING SPATIAL PATTERNS

CHARACTERIZING MONARCH BUTTER-

FLY OVERWINTERING SITES

Habitat fragmentation surrounding Monarch overwinter-

ing sites (cell size 30 by 30 meters)

Elevation in meters surrounding Monarch overwintering

sites (cell size 30 by 30 meters)

Wind Intensity at 50 meter height surrounding Monarch

overwintering sites (cell size 30 by 30 meters)

Urban light pollution at Monarch overwintering sites (30

arc second grids, cell size reclassified 30 by 30 meters)

Land use surrounding Monarch overwintering sites (cell

size 30 by 30 meters)

Habitat suitability of coastal overwintering sites for Monarch butterflies INTRODUCTION:

Across North America, the pressures of habitat loss and

agricultural intensification on have led to major declines in

many butterfly populations. The Western Monarch butter-

fly, one of the most charismatic and well-studied butterfly

species, is no exception, with population declines of 74%

since the 1990s (Pelton et al. 2016).

Efforts to conserve monarch butterflies mainly focus

on providing breeding and migratory habitat. However, loss

of overwintering habitat due to development, increased

pesticide use, and climate change may further threaten this

species. Western Monarch butterflies are migratory. During

the winter, colonies of butterflies and overwinter in tall

trees along the California coast. These overwintering sites

are commonly located no further than 1.5 miles from the

ocean, at sunny sites with low elevation and without high

winds. Butterflies mate and disperse from overwintering

sites in February or March. During the spring and summer,

butterflies migrate northward. Several generations of but-

terflies may emerge during the summer: the last generation

will return to the coast in the fall.

Here, I will explore the landscape patterns of habitats

surrounding monarch overwintering sites, using measures

of landscape composition, habitat fragmentation, urban

light pollution, wind intensity, and elevation. I will also

identify suitable overwintering habitats based on landscape

criteria.

RESULTS AND CONCLUSIONS:

Urbanized areas made up a considerable proportion of

buffer zones surrounding overwintering sites, composing an

average of 30% of raster cells within a buffer zones. For 12

study sites, urban environments made up >95% of the buff-

er zone; only 21 of 485 buffer zones contained no urbanized

raster cells. In comparison, forested areas composed an av-

erage of 7.5 % of raster cells within a buffer zones. Most

sites were affected by light pollution at some level (91%).

Further analysis is necessary to determine the effects of ur-

banization on overwintering butterflies. While urbanization

is associated with habitat loss, the reduction of pesticide use

may impact butterfly populations positively.

A report by the Xerces society found that most Mon-

arch butterfly overwintering sites are found at an elevation

between 60 and 90 meters, and at areas with low wind

speeds. My results confirm these findings. Elevations at

monarch overwintering sites ranged between 0 and 469.5

meters. The average elevation for monarch overwintering

sites was 60.5 meters (SD 53.2). Most overwintering sites

were located in areas with low wind speeds at 50 meters.

Most buffer zones (274 out of 488) contained no cells rep-

resenting wind speeds of greater than 5.6 meters/second at

50 meters above ground.

Site suitability for monarch butterflies should be ad-

dressed at a fine scale, as microclimate factors may be im-

portant in determining where monarchs aggregate. Howev-

er, this site suitability analysis provides some insights to the

locations of potential habitats. According to the criteria of

this analysis, a low proportion of coastal habitats are suita-

ble for monarch: this analysis may be used to aide research-

ers in searching for monarch overwintering sites.

Cartographer: Genevieve Pugesek

Date: 5/9/17

Professor: Barbara Parmenter, Class: UEP 0232 Intro to GIS

Projection: California Teale Albers, NAD83 projection

Sources: The Xerces Society’s Western Monarch Overwintering Sites Database, The National Renewable Ener-

gy Laboratory GIS Data, U.S. Geological Survey National Elevation Dataset, U.S. Geological Survey National

Landcover Data Base, Defense Meteorological Satellite Program Nighttime Lights Time Series, ESRI, USGS

National Assessment of Shoreline Change Vector Shorelines

Literature cited: Pelton, Jepsen, Schultz, Fallon, Black. (2016). State of the Monarch Butterfly Overwintering

sites in California. The Xerces Society for Invertebrate Conservation, Portland, Oregon.