Methods for environmental variables. Article Swipe
David Samuel Johnson (22265021)
,
Manisha Pant (22265024)
,
Andrew Nemeth (22265027)
,
Emelie Foster (22265030)
,
Adam Gartelman (22265033)
,
Stacy Calhoun-Grosch (20438597)
,
Kehui Xu (361209)
,
Brian J. Roberts (2922885)
,
James Nelson (3180039)
·
YOU?
·
· 2025
· Open Access
·
· DOI: https://doi.org/10.1371/journal.pone.0332089.s001
YOU?
·
· 2025
· Open Access
·
· DOI: https://doi.org/10.1371/journal.pone.0332089.s001
In soft-sediment communities, benthic macroinfauna can recover quickly (sometimes < 1 year) from dredging. However, it’s unclear how recovery is influenced if dredging dramatically changes abiotic factors. We determined recovery of benthic macroinfauna from dredging on a sandy shoal (Ship Shoal, Louisiana, USA), six years after dredging. Because the dredged area infilled with mud instead of sand and changed local abiotic conditions, we hypothesized that the benthic community had not recovered. Our results support this hypothesis. Although the dredged community had, on average, 160% greater density and 170% greater macroinfaunal biomass than the reference community, these increases were driven by the opportunistic and seasonally variable dwarf clam, Mulinia lateralis. Community structure differed starkly between the regions. Haustoriid amphipods and amphioxus (Branchiostoma floridae) dominated the reference community. However, these taxa were largely absent from the dredged community, which was dominated by opportunistic species such as M. lateralis and the fringe-gilled mudworm Paraprionospio pinnata. Community differences were largely driven by bottom-water dissolved oxygen and sediment grain size. Our results suggest that the dredged areas are still in a transitional phase of recovery after six years – dominated by opportunistic, hypoxia-tolerant species. Our results suggest that abiotic factors such as grain size and hypoxia are important in structuring benthic communities and their recovery rates. Thus, to achieve faster recovery of the biological community, dredging should be conducted in a way that minimizes long-term impacts on abiotic conditions.
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Metadata
- Type
- article
- OA Status
- green
- OpenAlex ID
- https://openalex.org/W7111220391
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- OpenAlex ID
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https://openalex.org/W7111220391Canonical identifier for this work in OpenAlex
- DOI
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https://doi.org/10.1371/journal.pone.0332089.s001Digital Object Identifier
- Title
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Methods for environmental variables.Work title
- Type
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articleOpenAlex work type
- Publication year
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2025Year of publication
- Publication date
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2025-09-17Full publication date if available
- Authors
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David Samuel Johnson (22265021), Manisha Pant (22265024), Andrew Nemeth (22265027), Emelie Foster (22265030), Adam Gartelman (22265033), Stacy Calhoun-Grosch (20438597), Kehui Xu (361209), Brian J. Roberts (2922885), James Nelson (3180039)List of authors in order
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YesWhether a free full text is available
- OA status
-
greenOpen access status per OpenAlex
- Concepts
-
Dredging, Benthic zone, Abiotic component, Benthos, Ecology, Environmental science, Invertebrate, Biomass (ecology), Community structure, Sediment, Beach nourishment, Fishery, Biology, Oceanography, Ecosystem, Benthic habitat, Hypoxia (environmental), Macrobenthos, Fauna, Estuary, Shoal, Defaunation, DetritivoreTop concepts (fields/topics) attached by OpenAlex
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0Total citation count in OpenAlex
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| abstract_inverted_index.dredged | 50, 79, 135, 171 |
| abstract_inverted_index.factors | 195 |
| abstract_inverted_index.greater | 85, 89 |
| abstract_inverted_index.hypoxia | 201 |
| abstract_inverted_index.impacts | 231 |
| abstract_inverted_index.instead | 55 |
| abstract_inverted_index.largely | 131, 156 |
| abstract_inverted_index.mudworm | 150 |
| abstract_inverted_index.quickly | 8 |
| abstract_inverted_index.recover | 7 |
| abstract_inverted_index.results | 73, 167, 191 |
| abstract_inverted_index.species | 142 |
| abstract_inverted_index.starkly | 113 |
| abstract_inverted_index.suggest | 168, 192 |
| abstract_inverted_index.support | 74 |
| abstract_inverted_index.unclear | 17 |
| abstract_inverted_index.Although | 77 |
| abstract_inverted_index.However, | 15, 127 |
| abstract_inverted_index.average, | 83 |
| abstract_inverted_index.differed | 112 |
| abstract_inverted_index.dredging | 23, 35, 221 |
| abstract_inverted_index.factors. | 27 |
| abstract_inverted_index.infilled | 52 |
| abstract_inverted_index.recovery | 19, 30, 180, 210, 216 |
| abstract_inverted_index.regions. | 116 |
| abstract_inverted_index.sediment | 163 |
| abstract_inverted_index.species. | 189 |
| abstract_inverted_index.variable | 105 |
| abstract_inverted_index.Community | 110, 153 |
| abstract_inverted_index.amphioxus | 120 |
| abstract_inverted_index.amphipods | 118 |
| abstract_inverted_index.community | 68, 80 |
| abstract_inverted_index.conducted | 224 |
| abstract_inverted_index.dissolved | 160 |
| abstract_inverted_index.dominated | 123, 139, 185 |
| abstract_inverted_index.dredging. | 14, 47 |
| abstract_inverted_index.important | 203 |
| abstract_inverted_index.increases | 97 |
| abstract_inverted_index.long-term | 230 |
| abstract_inverted_index.minimizes | 229 |
| abstract_inverted_index.reference | 94, 125 |
| abstract_inverted_index.structure | 111 |
| abstract_inverted_index.(sometimes | 9 |
| abstract_inverted_index.<i>Mulinia | 108 |
| abstract_inverted_index.Haustoriid | 117 |
| abstract_inverted_index.Louisiana, | 42 |
| abstract_inverted_index.biological | 219 |
| abstract_inverted_index.community, | 95, 136, 220 |
| abstract_inverted_index.community. | 126 |
| abstract_inverted_index.determined | 29 |
| abstract_inverted_index.influenced | 21 |
| abstract_inverted_index.recovered. | 71 |
| abstract_inverted_index.seasonally | 104 |
| abstract_inverted_index.communities | 207 |
| abstract_inverted_index.conditions, | 62 |
| abstract_inverted_index.conditions. | 234 |
| abstract_inverted_index.differences | 154 |
| abstract_inverted_index.hypothesis. | 76 |
| abstract_inverted_index.structuring | 205 |
| abstract_inverted_index.bottom-water | 159 |
| abstract_inverted_index.communities, | 3 |
| abstract_inverted_index.dramatically | 24 |
| abstract_inverted_index.hypothesized | 64 |
| abstract_inverted_index.macroinfauna | 5, 33 |
| abstract_inverted_index.pinnata</i>. | 152 |
| abstract_inverted_index.transitional | 177 |
| abstract_inverted_index.floridae</i>) | 122 |
| abstract_inverted_index.fringe-gilled | 149 |
| abstract_inverted_index.lateralis</i> | 146 |
| abstract_inverted_index.macroinfaunal | 90 |
| abstract_inverted_index.opportunistic | 102, 141 |
| abstract_inverted_index.soft-sediment | 2 |
| abstract_inverted_index.lateralis</i>. | 109 |
| abstract_inverted_index.opportunistic, | 187 |
| abstract_inverted_index.hypoxia-tolerant | 188 |
| abstract_inverted_index.(<i>Branchiostoma | 121 |
| abstract_inverted_index.<i>Paraprionospio | 151 |
| cited_by_percentile_year | |
| countries_distinct_count | 0 |
| institutions_distinct_count | 9 |
| citation_normalized_percentile.value | 0.82199763 |
| citation_normalized_percentile.is_in_top_1_percent | False |
| citation_normalized_percentile.is_in_top_10_percent | True |