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Research article · 2026 · Full text

International Journal of Geography Geology and Environment

Distribution patterns and habitat associations of Spilomelinae (Crambidae) across arid ecosystems of the United Arab Emirates

Yousef Nai

Volume 8(6) · Pages 163–167 · DOI: 10.22271/27067483.2026.v8.i6b.818 ↗

Research areasLepidoptera: Biology and TaxonomyEntomological Studies and EcologyFreshwater macroinvertebrate diversity and ecology

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Abstract

Author-written

The arid landscapes of the United Arab Emirates harbor an unexpectedly diverse Lepidopteran fauna whose ecological determinants remain insufficiently characterized. This research examines the distribution patterns and habitat associations of Spilomelinae moths (Lepidoptera: Crambidae) across five habitat categories in the United Arab Emirates, encompassing desert scrub, oasis woodland, urban gardens, coastal mangroves, and mountain wadis. Standardized light-trapping surveys conducted over 24 months at 15 sampling stations yielded 187 specimens representing nine Spilomelinae species. Species richness was highest in oasis woodland habitats (mean 7.8 species per site), followed by coastal mangroves (6.2) and mountain wadis (5.9), while desert scrub supported the lowest diversity (2.8 species per site). Canonical correspondence analysis identified vegetation cover, soil moisture content, and proximity to permanent water sources as the primary environmental predictors of Spilomelinae species composition. Seasonal abundance patterns showed pronounced peaks during the post-monsoon period in eastern sites and during spring in western habitats. The results demonstrate that microhabitat heterogeneity within arid landscapes creates distinct environmental niches that support differential Spilomelinae assemblages, challenging the perception of desert environments as uniformly species-poor for microlepidopteran taxa. Conservation implications and the role of urban green spaces as secondary habitat for Spilomelinae are discussed.

Summary

Source-checked

Plain-language reading of the full paper, prepared with AI and checked against the text. Each point links to the authors' own words.

  1. Why it matters

    • Arid ecosystems, characterized by low annual precipitation (under 250 mm) and high evapotranspiration, are often incorrectly viewed as having very low species diversity compared to tropical or temperate regions. View evidence ↗

      Why it matters

      Arid ecosystems, characterized by low annual precipitation (under 250 mm) and high evapotranspiration, are often incorrectly viewed as having very low species diversity compared to tropical or temperate regions.

      In the paper's own words

      “Arid ecosystems, defined by annual precipitation below 250 mm and evapotranspiration rates exceeding moisture input, support ecological communities that are frequently dismissed as species-depauperate relative to temperate and tropical biomes”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Spilomelinae moths serve as a useful model for studying arid habitats because their distribution is closely tied to the availability and structure of the plants they feed on. View evidence ↗

      Why it matters

      Spilomelinae moths serve as a useful model for studying arid habitats because their distribution is closely tied to the availability and structure of the plants they feed on.

      In the paper's own words

      “The Spilomelinae (Lepidoptera: Crambidae) present an instructive model system for examining habitat associations in arid environments. As predominantly phytophagous moths whose larval development depends on specific host plant availability, Spilomelinae distribution is fundamentally linked to vegetation composition and structure”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Despite their presence, the specific environmental factors and habitat types that maintain Spilomelinae diversity in the Arabian region have not been previously quantified. View evidence ↗

      Why it matters

      Despite their presence, the specific environmental factors and habitat types that maintain Spilomelinae diversity in the Arabian region have not been previously quantified.

      In the paper's own words

      “However, the environmental factors governing species occurrence and abundance patterns remain unexamined for Arabian Spilomelinae, and the relative importance of different habitat types for maintaining regional diversity has not been quantified”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  2. The question

    • The study aims to describe how Spilomelinae are distributed across five UAE habitat types, determine the environmental factors associated with these habitats, and assess the conservation value of both natural and man-made areas. View evidence ↗

      The question

      The study aims to describe how Spilomelinae are distributed across five UAE habitat types, determine the environmental factors associated with these habitats, and assess the conservation value of both natural and man-made areas.

      In the paper's own words

      “The present research aims to characterize Spilomelinae distribution patterns across five habitat categories in the UAE, quantify species-habitat associations through multivariate ecological analyses, and evaluate the relative conservation value of natural and anthropogenic habitats for maintaining regional Spilomelinae diversity.”

      Page 2

      Found in: Introduction

      Read it in the full textOpen PDF at page 2 ↗
  3. What they did

    • Researchers surveyed 15 stations (three per habitat type) across desert scrub, oasis woodland, urban gardens, coastal mangroves, and mountain wadis in the UAE from February 2022 to January 2024. View evidence ↗

      What they did

      Researchers surveyed 15 stations (three per habitat type) across desert scrub, oasis woodland, urban gardens, coastal mangroves, and mountain wadis in the UAE from February 2022 to January 2024.

      In the paper's own words

      “Field surveys were conducted at 15 sampling stations distributed across five habitat categories in the United Arab Emirates between February 2022 and January 2024. Three replicate stations were established within each habitat type: desert scrub (Al Dhafra, Liwa, Madinat Zayed), oasis woodland (Al Ain, Hili, Al Buraimi border zone), urban gardens (Abu Dhabi Corniche, Dubai Creek Park, Sharjah National Park), coastal mangroves (Abu Dhabi Eastern Mangroves, Umm Al Quwain, Khor Kalba), and mountain wadis (Wadi Wurayah, Wadi Shawka, Wadi Al Helo).”

      Page 2

      Found in: Material

      Read it in the full textOpen PDF at page 2 ↗
    • Moths were collected using Robinson-pattern mercury vapor light traps, which were operated from sunset until midnight for two consecutive nights every month. View evidence ↗

      What they did

      Moths were collected using Robinson-pattern mercury vapor light traps, which were operated from sunset until midnight for two consecutive nights every month.

      In the paper's own words

      “At each station, standardized light-trapping was conducted using Robinson-pattern mercury vapor light traps operated from sunset to midnight on two consecutive nights per month”

      Page 2

      Found in: Material

      Read it in the full textOpen PDF at page 2 ↗
    • The study measured several environmental factors at each site, including soil moisture, vegetation cover, temperature, humidity, elevation, and distance to permanent water. View evidence ↗

      What they did

      The study measured several environmental factors at each site, including soil moisture, vegetation cover, temperature, humidity, elevation, and distance to permanent water.

      In the paper's own words

      “Environmental variables recorded at each station included vegetation cover percentage, soil moisture content, ambient temperature, relative humidity, distance to nearest permanent water source, and elevation.”

      Page 2

      Found in: Material

      Read it in the full textOpen PDF at page 2 ↗
    • Diversity was measured using Shannon-Wiener and Simpson indices, while species-habitat associations were analyzed using canonical correspondence analysis (CANOCO v5.0). View evidence ↗

      What they did

      Diversity was measured using Shannon-Wiener and Simpson indices, while species-habitat associations were analyzed using canonical correspondence analysis (CANOCO v5.0).

      In the paper's own words

      “Species diversity was quantified using the Shannon-Wiener diversity index (H') and Simpson dominance index (D) calculated for each habitat type. ... Species-habitat associations were evaluated using canonical correspondence analysis implemented in CANOCO v5.0”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
  4. What they found

    • The surveys collected a total of 187 specimens belonging to nine different Spilomelinae species. View evidence ↗

      What they found

      The surveys collected a total of 187 specimens belonging to nine different Spilomelinae species.

      In the paper's own words

      “Surveys across the 15 stations yielded 187 specimens representing nine Spilomelinae species.”

      Page 2

      Found in: Material

      Read it in the full textOpen PDF at page 2 ↗
    • Oasis woodlands were the most diverse habitat (mean 7.8 species per site, Shannon index 1.89), whereas desert scrub had the lowest diversity. View evidence ↗

      What they found

      Oasis woodlands were the most diverse habitat (mean 7.8 species per site, Shannon index 1.89), whereas desert scrub had the lowest diversity.

      In the paper's own words

      “Oasis woodland supported the highest mean species richness at 7.8 species per site and the greatest Shannon diversity index at 1.89, while desert scrub habitats yielded the lowest diversity metrics across all indices.”

      Page 2

      Found in: Discussion

      Read it in the full textOpen PDF at page 2 ↗
    • The primary environmental predictors of species composition were vegetation cover, soil moisture, and proximity to permanent water. View evidence ↗

      What they found

      The primary environmental predictors of species composition were vegetation cover, soil moisture, and proximity to permanent water.

      In the paper's own words

      “Vegetation cover emerged as the strongest predictor of species composition (F = 8.92, p = 0.001), followed by soil moisture content (F = 6.45, p = 0.003) and distance to permanent water sources (F = 4.21, p = 0.012).”

      Page 2

      Found in: Ecological niche characterization

      Read it in the full textOpen PDF at page 2 ↗
    • Specific species showed distinct associations: Palpita vitrealis was linked to oasis woodlands and Glyphodes stolalis to coastal mangroves, while Spoladea recurvalis acted as a generalist. View evidence ↗

      What they found

      Specific species showed distinct associations: Palpita vitrealis was linked to oasis woodlands and Glyphodes stolalis to coastal mangroves, while Spoladea recurvalis acted as a generalist.

      In the paper's own words

      “Indicator species analysis identified Spoladea recurvalis as a generalist species with no significant habitat association (IndVal < 0.4 for all habitats), while Palpita vitrealis was significantly associated with oasis woodland (IndVal = 0.78, p = 0.003) and Glyphodes stolalis with coastal mangrove habitat (IndVal = 0.85, p = 0.001).”

      Page 3

      Found in: Ecological niche characterization

      Read it in the full textOpen PDF at page 3 ↗
    • Abundance peaked twice (spring and autumn) in urban gardens and oasis woodlands, but coastal mangroves had only one peak in autumn, linked to monsoon moisture. View evidence ↗

      What they found

      Abundance peaked twice (spring and autumn) in urban gardens and oasis woodlands, but coastal mangroves had only one peak in autumn, linked to monsoon moisture.

      In the paper's own words

      “Oasis woodland and urban garden habitats exhibited bimodal abundance patterns with peaks in spring (March-April) and autumn (October-November), while coastal mangrove sites showed a single pronounced peak during autumn corresponding to monsoon-influenced moisture availability.”

      Page 4

      Found in: Ecological niche characterization

      Read it in the full textOpen PDF at page 4 ↗
    • Urban gardens hosted four of the nine species, with the generalist Spoladea recurvalis making up 62% of the captures in these areas. View evidence ↗

      What they found

      Urban gardens hosted four of the nine species, with the generalist Spoladea recurvalis making up 62% of the captures in these areas.

      In the paper's own words

      “Four of the nine recorded species were present in urban garden sites, with Spoladea recurvalis accounting for 62% of urban captures.”

      Page 4

      Found in: Urban habitat utilization

      Read it in the full textOpen PDF at page 4 ↗
  5. What it means

    • The authors recommend that conservation efforts for moths in arid zones prioritize protecting moisture-rich areas like mangrove margins and oasis woodlands, as these act as reservoirs for diversity. View evidence ↗

      What it means

      The authors recommend that conservation efforts for moths in arid zones prioritize protecting moisture-rich areas like mangrove margins and oasis woodlands, as these act as reservoirs for diversity.

      In the paper's own words

      “The recommendation emerging from this research is that conservation strategies for Lepidoptera in arid regions should prioritize the protection of moisture-rich microhabitats, particularly oasis woodlands and mangrove margins, which serve as diversity reservoirs.”

      Page 5

      Found in: Conclusion

      Read it in the full textOpen PDF at page 5 ↗
    • The authors state that long-term monitoring is needed to detect how climate change and land-use changes might shift species distributions over time. View evidence ↗

      What it means

      The authors state that long-term monitoring is needed to detect how climate change and land-use changes might shift species distributions over time.

      In the paper's own words

      “Looking forward, long-term monitoring programs incorporating standardized light-trapping protocols across these habitat types will be essential for detecting distributional shifts linked to climate change and land-use intensification”

      Page 5

      Found in: Conclusion

      Read it in the full textOpen PDF at page 5 ↗

Visual summary

1 visuals

Illustrations explain the paper; they do not show study data.

AI-generated illustration
AI-generated conceptual illustration (Spilomelinae moths in UAE arid ecosystems). It explains the idea and does not show study data.↗ Enlarge
Habitat Diversity Gradient
AI-generated conceptual illustration (Spilomelinae moths in UAE arid ecosystems). It explains the idea and does not show study data.

AI-generated conceptual illustration (Spilomelinae moths in UAE arid ecosystems). It explains the idea and does not show study data.

Open full-size image ↗

Habitat Diversity Gradient

AI-generated conceptual illustration (Spilomelinae moths in UAE arid ecosystems). It explains the idea and does not show study data.

View source evidence ↗

Figures & tables

From the original paper
Correlation matrix of environmental variables measured across 15 sampling stations in the UAETable 1Page 2Ranking of habitat types by Spilomelinae species richness and diversity indices in the UAETable 2Page 2Box plot of species richness distribution across five habitat types in the UAEFigure 1Page 3Radar diagram comparing habitat suitability indices between arid and oasis zones for SpilomelinaeFigure 2Page 3Seasonal abundance of Spilomelinae across three major habitat types in the UAEFigure 3Page 4Stacked species composition across five collection sitesFigure 4Page 4
FULL TEXT Original article · reflowed for reading

Introduction

Arid ecosystems, defined by annual precipitation below 250 mm and evapotranspiration rates exceeding moisture input, support ecological communities that are frequently dismissed as species-depauperate relative to temperate and tropical biomes [1] . This characterization, while statistically defensible at the landscape scale, obscures the considerable microhabitat-driven heterogeneity that sustains localized biodiversity within desert environments [2] . For insect communities in particular, the spatial distribution of moisture, vegetation, and thermal refugia creates a patchy mosaic of suitable habitats embedded within a matrix of inhospitable terrain, resulting in distribution patterns governed by fine-scale environmental gradients rather than broad climatic envelopes [3] . The Spilomelinae (Lepidoptera: Crambidae) present an instructive model system for examining habitat associations in arid environments. As predominantly phytophagous moths whose larval development depends on specific host plant availability, Spilomelinae distribution is fundamentally linked to vegetation composition and structure [3] . Seizmair documented eleven recently recorded species from the Arabian Peninsula, providing baseline faunistic data that highlighted the regional occurrence of the subfamily [3] . However, the environmental factors governing species occurrence and abundance patterns remain unexamined for Arabian Spilomelinae, and the relative importance of different habitat types for maintaining regional diversity has not been quantified [4] . The United Arab Emirates, situated at the southeastern corner of the Arabian Peninsula, encompasses a compact area of approximately 83,600 square kilometers but contains a remarkable diversity of habitat types. These range from the vast sand seas of the Liwa desert through the date palm oases of Al Ain, coastal mangrove stands along the Irrigated urban gardens in Abu Dhabi and Dubai, and the Hajar Mountain wadis of the eastern emirates [5] . This concentration of environmental variation within a relatively small geographical area provides an opportunity to examine how distinct habitat types influence Spilomelinae community structure under uniformly arid macroclimatic conditions [6] . The present research aims to characterize Spilomelinae distribution patterns across five habitat categories in the UAE, quantify species-habitat associations through multivariate ecological analyses, and evaluate the relative conservation value of natural and anthropogenic habitats for maintaining regional Spilomelinae diversity. The findings are expected to inform habitat management strategies and contribute to the broader understanding of invertebrate ecology in arid landscapes [7] .

Material and Methods

Material and Methods

Material

Field surveys were conducted at 15 sampling stations distributed across five habitat categories in the United Arab Emirates between February 2022 and January 2024. Three replicate stations were established within each habitat type: desert scrub (Al Dhafra, Liwa, Madinat Zayed), oasis woodland (Al Ain, Hili, Al Buraimi border zone), urban gardens (Abu Dhabi Corniche, Dubai Creek Park, Sharjah National Park), coastal mangroves (Abu Dhabi Eastern Mangroves, Umm Al Quwain, Khor Kalba), and mountain wadis (Wadi Wurayah, Wadi Shawka, Wadi Al Helo). At each station, standardized light-trapping was conducted using Robinson-pattern mercury vapor light traps operated from sunset to midnight on two consecutive nights per month [8] . Specimens were collected, pinned, and identified using morphological keys following the classification of Nuss et al. [9] . Voucher material was deposited at the Abu Dhabi Academy of Environmental Sciences. Environmental variables recorded at each station included vegetation cover percentage, soil moisture content, ambient temperature, relative humidity, distance to nearest permanent water source, and elevation. Research permits were obtained from the Environment Agency Abu Dhabi under authorization number EAD/SCI/2022-0218.

Methods

Species diversity was quantified using the Shannon-Wiener diversity index (H') and Simpson dominance index (D) calculated for each habitat type. Rarefaction curves were constructed to assess sampling completeness. Species-habitat associations were evaluated using canonical correspondence analysis implemented in CANOCO v5.0, with forward selection of environmental variables and Monte Carlo permutation testing (999 permutations) to assess statistical significance [10] . Indicator species analysis was performed using the IndVal procedure to identify species significantly associated with specific habitat types [11] . Seasonal abundance patterns were modeled using generalized linear mixed models with Poisson error distribution, including site as a random effect and season, habitat type, and their interaction as fixed effects. All statistical analyses were conducted in R v4.3.0 [12] .

Ecological niche characterization

The characterization of ecological niches occupied by Spilomelinae species in arid environments requires consideration of both fundamental niche parameters (physiological tolerances to temperature and aridity) and realized niche dimensions shaped by biotic interactions including host plant availability, parasitoid pressure, and interspecific competition. In the present research, realized niche parameters were approximated through the environmental variables measured at occupied versus unoccupied stations, providing a habitat-level characterization rather than a physiological assessment. This approach captures the environmental conditions under which species actually occur in the field, integrating the combined effects of abiotic filters and biotic constraints [13] . Vegetation cover emerged as the strongest predictor of species composition (F = 8.92, p = 0.001), followed by soil moisture content (F = 6.45, p = 0.003) and distance to permanent water sources (F = 4.21, p = 0.012). Temperature and elevation contributed marginally to the explained variance and were not statistically significant after forward selection [3] . Indicator species analysis identified Spoladea recurvalis as a generalist species with no significant habitat association (IndVal < 0.4 for all habitats), while Palpita vitrealis was significantly associated with oasis woodland (IndVal = 0.78, p = 0.003) and Glyphodes stolalis with coastal mangrove habitat (IndVal = 0.85, p = 0.001). Seasonal patterns showed distinct peaks across habitat types. Oasis woodland and urban garden habitats exhibited bimodal abundance patterns with peaks in spring (March-April) and autumn (October-November), while coastal mangrove sites showed a single pronounced peak during autumn corresponding to monsoon-influenced moisture availability.

Results

Results

Urban habitat utilization

Urban gardens emerged as the fourth-ranked habitat type by species richness but supported a distinctive assemblage composition characterized by higher relative abundance of generalist species and the near-absence of habitat specialists. Four of the nine recorded species were present in urban garden sites, with Spoladea recurvalis accounting for 62% of urban captures. The presence of irrigated ornamental vegetation and artificial lighting in urban parks created conditions favorable for attracting and sustaining common Spilomelinae species, suggesting that managed green spaces function as supplementary habitat rather than primary conservation areas for the subfamily [14,15] .

Discussion

The distribution patterns documented in this research demonstrate that Spilomelinae diversity within the arid UAE landscape is predominantly determined by moisture-related environmental gradients, with vegetation cover and soil moisture emerging as the primary predictors of species composition. These findings align with broader ecological theory predicting that water availability functions as the master environmental filter in desert ecosystems, structuring invertebrate communities through direct physiological constraints and indirect effects on host plant availability [1,6] . The prominence of oasis woodland as the richest habitat type for Spilomelinae reflects the concentration of host plant diversity within these irrigated refugia. Date palm oases in the UAE support understory vegetation communities that include representatives of Amaranthaceae, Cucurbitaceae, and Convolvulaceae, families known to host larvae of multiple Spilomelinae species [2,5] . The high species richness and diversity indices recorded in oasis habitats corroborate findings from analogous research in North African oases, where irrigated agricultural landscapes supported significantly higher moth diversity than surrounding desert terrain [8] . The significant association between Glyphodes stolalis and coastal mangrove habitat represents a novel finding for the Arabian region. This species has been previously documented in mangrove-associated habitats in South-East Asia, where its larvae feed on Ficus species occurring in mangrove margins [3,9] . The Khor Kalba mangroves, recognized as the northernmost mangrove stand in the Arabian Gulf, may represent a critical habitat for this species in the western portion of its range. Conservation of intact mangrove systems thus has relevance not only for marine biodiversity but also for maintaining terrestrial invertebrate diversity at the landscape scale [7,13] .

Conclusion

Contextualizing these findings within the broader understanding of arid-zone invertebrate ecology, the present research demonstrates that Spilomelinae distribution in the UAE is structured by fine-scale environmental heterogeneity rather than uniform aridity. The finding that oasis woodland, coastal mangrove, and mountain wadi habitats each support distinct assemblages highlights microhabitat diversity as a key factor. The recommendation emerging from this research is that conservation strategies for Lepidoptera in arid regions should prioritize the protection of moisture-rich microhabitats, particularly oasis woodlands and mangrove margins, which serve as diversity reservoirs. Looking forward, long-term monitoring programs incorporating standardized light-trapping protocols across these habitat types will be essential for detecting distributional shifts linked to climate change and land-use intensification in the rapidly developing UAE landscape.

Acknowledgement

AcknowledgementsThis research was funded by the Environment Agency Abu Dhabi Research. The Abu Dhabi Academy of Environmental Sciences provided access to field vehicles, laboratory equipment, and the entomological reference collection. OJM conceptualized the research and performed ecological analyses; RTK conducted fieldwork and specimen identification; YNA assisted with data collection and manuscript preparation.

Figures and tables from the paper

Table 1. Correlation matrix of environmental variables measured across 15 sampling stations in the UAE
VariableVeg. coverSoil moistureTemp.Distance water
Vegetation cover1.000.82**-0.45*-0.71**
Soil moisture0.82**1.00-0.38-0.85**
Temperature-0.45*-0.381.000.29
Distance to water-0.71**-0.85**0.291.00

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

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Correlation matrix of environmental variables measured across 15 sampling stations in the UAE↗ Enlarge
Table 1
Correlation matrix of environmental variables measured across 15 sampling stations in the UAE

Correlation matrix of environmental variables measured across 15 sampling stations in the UAE

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Original paper tableSource PDF · page 2 ↗
Table 2. Ranking of habitat types by Spilomelinae species richness and diversity indices in the UAE
RankHabitat typeMean species richnessShannon H'Simpson D
1Oasis woodland7.8 +/- 1.21.890.82
2Coastal mangrove6.2 +/- 0.91.720.78
3Mountain wadi5.9 +/- 1.41.650.76
4Urban garden4.5 +/- 0.81.380.68
5Desert scrub2.8 +/- 0.60.850.48

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

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Ranking of habitat types by Spilomelinae species richness and diversity indices in the UAE↗ Enlarge
Table 2
Ranking of habitat types by Spilomelinae species richness and diversity indices in the UAE

Ranking of habitat types by Spilomelinae species richness and diversity indices in the UAE

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Original paper tableSource PDF · page 2 ↗
Figure 1. Box plot of species richness distribution across five habitat types in the UAE
Box plot of species richness distribution across five habitat types in the UAE↗ Enlarge
Figure 1
Box plot of species richness distribution across five habitat types in the UAE

Box plot of species richness distribution across five habitat types in the UAE

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Original paper figureSource PDF · page 3 ↗
Figure 2. Radar diagram comparing habitat suitability indices between arid and oasis zones for Spilomelinae
Radar diagram comparing habitat suitability indices between arid and oasis zones for Spilomelinae↗ Enlarge
Figure 2
Radar diagram comparing habitat suitability indices between arid and oasis zones for Spilomelinae

Radar diagram comparing habitat suitability indices between arid and oasis zones for Spilomelinae

Open full-size image ↗
Original paper figureSource PDF · page 3 ↗
Figure 3. Seasonal abundance of Spilomelinae across three major habitat types in the UAE
Seasonal abundance of Spilomelinae across three major habitat types in the UAE↗ Enlarge
Figure 3
Seasonal abundance of Spilomelinae across three major habitat types in the UAE

Seasonal abundance of Spilomelinae across three major habitat types in the UAE

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Original paper figureSource PDF · page 4 ↗
Figure 4. Stacked species composition across five collection sites
Stacked species composition across five collection sites↗ Enlarge
Figure 4
Stacked species composition across five collection sites

Stacked species composition across five collection sites

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Original paper figureSource PDF · page 4 ↗

References

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