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ERRATUM article

Front. Environ. Sci., 12 January 2022
Sec. Conservation and Restoration Ecology

Erratum: Roadkills in Northern Peninsular Malaysia

  • Frontiers Media SA, Lausanne, Switzerland

An erratum on
Roadkills in Northern Peninsular Malaysia

by Hui, T. C. Y., Slade, E. M., and Chong, J. L. (2021). Front. Environ. Sci. 9:637462. doi: 10.3389/fenvs.2021.637462

Due to a production error, some vital values in Tables 13 were not marked in bold. Bold values in Table 1 signifies “Total values” and the bold values in Tables 23 signifies “The most parsimonious models.” The corrected Tables 13 appear below.

TABLE 1
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TABLE 1. Vertebrate roadkills found in the road segments listed by number of individuals per taxonomic group, species, and habitat type. A number of roadkills were unidentifiable because carcasses were too degraded. Bold values signifies “Total values”.

TABLE 2
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TABLE 2. Ranking of the best statistical models which were retained in each confidence set, where the Akaike’s difference (Delta) with the top-ranked model was less than 5.0, following the Information Theoretic approach, for (a) all habitats and taxa combined, (b) oil palm, (c) subsistence agriculture, (d) village, and (e) rainforest habitats. The most parsimonious models are in bold. Weight refers to the cumulative weight of the models starting from the top ranked model. Bold values signifies “The most parsimonious models”.

TABLE 3
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TABLE 3. Ranking of the best statistical models which were retained in each confidence set, where the Akaike’s difference (Delta) with the top-ranked model was less than 5.0, following the Information Theoretic approach, for (a) birds, (b) mammals, (c) amphibians, and (d) reptiles. The most parsimonious models are in bold. Weight refers to the cumulative weight of the models starting from the top ranked model. Bold values signifies “The most parsimonious models”.

Figures 13 in the article as published had low resolution and have been corrected and appear below.

FIGURE 1
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FIGURE 1. Map of the surveyed road segments within Terengganu (A) and Pahang (B), Peninsular Malaysia.

FIGURE 2
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FIGURE 2. Probability that a roadkill will occur with increasing distance from the nearest water body (A), tree (B), shrub (C) or human dwelling (D) in all habitats and for all taxa combined; water body (E), shrub (F) or human dwelling (G) in oil palm habitat; tree (H), shrub (I), fruit tree (J) or human dwelling (K) in subsistence agriculture habitat; water body (L), tree (M) or fruit tree (N) in village habitat; and water body (O), tree (P) or shrub (Q) in rainforest habitat.

FIGURE 3
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FIGURE 3. Probability that a bird roadkill will occur with increasing distance from the nearest tree (A); that a mammal roadkill will occur with increasing distance from the nearest shrub (B); that an amphibian roadkill will occur with increasing distance from the nearest water body (C), tree (D) or fruit tree (E); and that a reptile roadkill will occur with increasing distance from the nearest water body (F) or fruit tree (G).

The publisher apologizes for this mistake. The original version of this article has been updated.

Keywords: infrastructure impacts, threatened species, vertebrate, rural habitats, agriculture, oil palm, forest, land use planning

Citation: Frontiers Production Office (2022) Erratum: Roadkills in Northern Peninsular Malaysia. Front. Environ. Sci. 9:830603. doi: 10.3389/fenvs.2021.830603

Received: 07 December 2021; Accepted: 07 December 2021;
Published: 12 January 2022.

Approved by:

Frontiers Editorial Office, Frontiers Media SA, Switzerland

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