{"title":"更正 \"二氧化碳富集、热浪、流速变化和细沉积物沉积对溪流无脊椎动物群落的单独和综合影响\"","authors":"","doi":"10.1111/gcb.17510","DOIUrl":null,"url":null,"abstract":"<p>Hunn, J. G., Orr, J. A., Kelly, A.-M., Piggott, J. J., & Matthaei, C. D. (2024). Individual and combined impacts of carbon dioxide enrichment, heatwaves, flow velocity variability, and fine sediment deposition on stream invertebrate communities. Global Change Biology, 30, e17336. https://doi.org/10.1111/gcb.17336</p><p>In the originally published version of this manuscript, the full names of the authors were omitted. They are</p><p>Julia G. Hunn, James A. Orr, Ann-Marie Kelly, Jeremy J. Piggott, Christoph D. Matthaei</p><p>This error has been corrected online.</p><p>In addition, due to a mistake that occurred during the typesetting process, negative symbols were omitted from some locations in the text. The corrected text is below:</p><p>\n <b>2.2 Experimental setup</b>\n </p><p>Each of the eight 135-L header tanks gravity-fed stream water to 16 mesocosms at a constant discharge of 2 L/min, measured at the start of the colonization period (<b>Day −16</b>) and recalibrated daily, via 4-m length of 13-mm polythene pipe controlled by a tap regulator. To create a bed substratum emulating small New Zealand streams (Matthaei et al., 2006), 500 mL of small- to medium-sized gravel was collected from the river floodplain, sieved to remove fine sediment (particles <2 mm; Zweig & Rabeni, 2001), and added to each mesocosm with 14 randomly selected 40- to 50-mm flat cobbles placed on top. On Day 0, a piece of PVC pipe (80 mm length, diameter 40 mm) was placed in the remaining space to act as a fish shelter, and a 1-cm stainless steel mesh covering was placed over the outflow to prevent fish escaping, scrubbed daily with filtered stream water to remove any trapped organic material.</p><p>\n <b>2.3 Experimental design and procedures</b>\n </p><p>CO<sub>2</sub>, fine sediment, flow velocity variability, and temperature were manipulated in a full-factorial 2 × 2 × 2 × 2 design with eight replicates of each treatment combination. Flow to the mesocosms began on October 21, 2019 (<b>Day −17</b>), the start of a 17-day colonization period. During this, the CO<sub>2</sub> (from <b>Day −17</b>) and sediment (from <b>Day −14</b>) manipulations were already implemented. A 35-day “experimental” period (beginning on Day 0) followed, during which temperature and flow velocity were manipulated, as well (Figure 2).</p><p>CO<sub>2</sub> treatments were randomly assigned at the header tank level, with one CO<sub>2</sub>-enriched header tank in each of four spatial blocks of two tanks per block. CO<sub>2</sub> was bubbled into CO<sub>2</sub>-enriched header tanks continuously from the start of the colonization period (<b>Day −17</b>). On Days 14 and 28, 1-L water samples taken from 16 randomly selected channels (eight ambient and eight CO<sub>2</sub>-enriched) were stored in sealed glass bottles and preserved with mercuric chloride for DIC analysis. Within 5 min of sampling, pH and temperature were also measured in these channels using a handheld pH meter (HI-98128; Hanna, Rhode Island).</p><p>On Day <b>−2</b>, natural invertebrate colonization was supplemented with taxa underrepresented in the drift by adding one standard sample of the Kauru River benthic invertebrate community to each mesocosm, following the methods described in Piggott, Townsend, and Matthaei (2015a).</p><p>Flow velocities were measured in all channels on Days <b>−12</b>, <b>−1</b>, 4, and 11 using a precision flow meter (MiniWater20; Schiltknecht, Gossau, Switzerland). Average near-bed velocity was 20 ± 1.1 cm/s on Day <b>−</b>12, with velocity gradually decreasing over time as prolific benthic algal communities (including filamentous taxa) formed in the channels. Mean velocity prior to beginning flow treatments (Day <b>−1</b>) was 17.9 ± 1.4 cm/s. On Day 4 (the first “fast” period), average velocities were 7.0 ± 2.8 cm/s in “constant” channels and 14.9 ± 3.2 cm/s in “variable” channels. On Day 11 (the first “slow” period), average velocities were 9.3 ± 2.6 and 2.0 ± 1.5 in “constant” and “variable” channels, respectively. Based on these two dates, “variable” channels experienced a mean velocity of 8.5 cm/s across the “fast” and “slow” periods. For “constant” channels, the corresponding mean velocity was 8.2 cm/s.</p><p>The publisher apologizes for this error.</p>","PeriodicalId":175,"journal":{"name":"Global Change Biology","volume":"30 9","pages":""},"PeriodicalIF":10.8000,"publicationDate":"2024-09-20","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1111/gcb.17510","citationCount":"0","resultStr":"{\"title\":\"Correction to “Individual and combined impacts of carbon dioxide enrichment, heatwaves, flow velocity variability, and fine sediment deposition on stream invertebrate communities”\",\"authors\":\"\",\"doi\":\"10.1111/gcb.17510\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p>Hunn, J. G., Orr, J. A., Kelly, A.-M., Piggott, J. J., & Matthaei, C. D. (2024). Individual and combined impacts of carbon dioxide enrichment, heatwaves, flow velocity variability, and fine sediment deposition on stream invertebrate communities. Global Change Biology, 30, e17336. https://doi.org/10.1111/gcb.17336</p><p>In the originally published version of this manuscript, the full names of the authors were omitted. They are</p><p>Julia G. Hunn, James A. Orr, Ann-Marie Kelly, Jeremy J. Piggott, Christoph D. Matthaei</p><p>This error has been corrected online.</p><p>In addition, due to a mistake that occurred during the typesetting process, negative symbols were omitted from some locations in the text. The corrected text is below:</p><p>\\n <b>2.2 Experimental setup</b>\\n </p><p>Each of the eight 135-L header tanks gravity-fed stream water to 16 mesocosms at a constant discharge of 2 L/min, measured at the start of the colonization period (<b>Day −16</b>) and recalibrated daily, via 4-m length of 13-mm polythene pipe controlled by a tap regulator. To create a bed substratum emulating small New Zealand streams (Matthaei et al., 2006), 500 mL of small- to medium-sized gravel was collected from the river floodplain, sieved to remove fine sediment (particles <2 mm; Zweig & Rabeni, 2001), and added to each mesocosm with 14 randomly selected 40- to 50-mm flat cobbles placed on top. On Day 0, a piece of PVC pipe (80 mm length, diameter 40 mm) was placed in the remaining space to act as a fish shelter, and a 1-cm stainless steel mesh covering was placed over the outflow to prevent fish escaping, scrubbed daily with filtered stream water to remove any trapped organic material.</p><p>\\n <b>2.3 Experimental design and procedures</b>\\n </p><p>CO<sub>2</sub>, fine sediment, flow velocity variability, and temperature were manipulated in a full-factorial 2 × 2 × 2 × 2 design with eight replicates of each treatment combination. Flow to the mesocosms began on October 21, 2019 (<b>Day −17</b>), the start of a 17-day colonization period. During this, the CO<sub>2</sub> (from <b>Day −17</b>) and sediment (from <b>Day −14</b>) manipulations were already implemented. A 35-day “experimental” period (beginning on Day 0) followed, during which temperature and flow velocity were manipulated, as well (Figure 2).</p><p>CO<sub>2</sub> treatments were randomly assigned at the header tank level, with one CO<sub>2</sub>-enriched header tank in each of four spatial blocks of two tanks per block. CO<sub>2</sub> was bubbled into CO<sub>2</sub>-enriched header tanks continuously from the start of the colonization period (<b>Day −17</b>). On Days 14 and 28, 1-L water samples taken from 16 randomly selected channels (eight ambient and eight CO<sub>2</sub>-enriched) were stored in sealed glass bottles and preserved with mercuric chloride for DIC analysis. Within 5 min of sampling, pH and temperature were also measured in these channels using a handheld pH meter (HI-98128; Hanna, Rhode Island).</p><p>On Day <b>−2</b>, natural invertebrate colonization was supplemented with taxa underrepresented in the drift by adding one standard sample of the Kauru River benthic invertebrate community to each mesocosm, following the methods described in Piggott, Townsend, and Matthaei (2015a).</p><p>Flow velocities were measured in all channels on Days <b>−12</b>, <b>−1</b>, 4, and 11 using a precision flow meter (MiniWater20; Schiltknecht, Gossau, Switzerland). Average near-bed velocity was 20 ± 1.1 cm/s on Day <b>−</b>12, with velocity gradually decreasing over time as prolific benthic algal communities (including filamentous taxa) formed in the channels. Mean velocity prior to beginning flow treatments (Day <b>−1</b>) was 17.9 ± 1.4 cm/s. On Day 4 (the first “fast” period), average velocities were 7.0 ± 2.8 cm/s in “constant” channels and 14.9 ± 3.2 cm/s in “variable” channels. On Day 11 (the first “slow” period), average velocities were 9.3 ± 2.6 and 2.0 ± 1.5 in “constant” and “variable” channels, respectively. Based on these two dates, “variable” channels experienced a mean velocity of 8.5 cm/s across the “fast” and “slow” periods. For “constant” channels, the corresponding mean velocity was 8.2 cm/s.</p><p>The publisher apologizes for this error.</p>\",\"PeriodicalId\":175,\"journal\":{\"name\":\"Global Change Biology\",\"volume\":\"30 9\",\"pages\":\"\"},\"PeriodicalIF\":10.8000,\"publicationDate\":\"2024-09-20\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"https://onlinelibrary.wiley.com/doi/epdf/10.1111/gcb.17510\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Global Change Biology\",\"FirstCategoryId\":\"93\",\"ListUrlMain\":\"https://onlinelibrary.wiley.com/doi/10.1111/gcb.17510\",\"RegionNum\":1,\"RegionCategory\":\"环境科学与生态学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"BIODIVERSITY CONSERVATION\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Global Change Biology","FirstCategoryId":"93","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1111/gcb.17510","RegionNum":1,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"BIODIVERSITY CONSERVATION","Score":null,"Total":0}
Correction to “Individual and combined impacts of carbon dioxide enrichment, heatwaves, flow velocity variability, and fine sediment deposition on stream invertebrate communities”
Hunn, J. G., Orr, J. A., Kelly, A.-M., Piggott, J. J., & Matthaei, C. D. (2024). Individual and combined impacts of carbon dioxide enrichment, heatwaves, flow velocity variability, and fine sediment deposition on stream invertebrate communities. Global Change Biology, 30, e17336. https://doi.org/10.1111/gcb.17336
In the originally published version of this manuscript, the full names of the authors were omitted. They are
Julia G. Hunn, James A. Orr, Ann-Marie Kelly, Jeremy J. Piggott, Christoph D. Matthaei
This error has been corrected online.
In addition, due to a mistake that occurred during the typesetting process, negative symbols were omitted from some locations in the text. The corrected text is below:
2.2 Experimental setup
Each of the eight 135-L header tanks gravity-fed stream water to 16 mesocosms at a constant discharge of 2 L/min, measured at the start of the colonization period (Day −16) and recalibrated daily, via 4-m length of 13-mm polythene pipe controlled by a tap regulator. To create a bed substratum emulating small New Zealand streams (Matthaei et al., 2006), 500 mL of small- to medium-sized gravel was collected from the river floodplain, sieved to remove fine sediment (particles <2 mm; Zweig & Rabeni, 2001), and added to each mesocosm with 14 randomly selected 40- to 50-mm flat cobbles placed on top. On Day 0, a piece of PVC pipe (80 mm length, diameter 40 mm) was placed in the remaining space to act as a fish shelter, and a 1-cm stainless steel mesh covering was placed over the outflow to prevent fish escaping, scrubbed daily with filtered stream water to remove any trapped organic material.
2.3 Experimental design and procedures
CO2, fine sediment, flow velocity variability, and temperature were manipulated in a full-factorial 2 × 2 × 2 × 2 design with eight replicates of each treatment combination. Flow to the mesocosms began on October 21, 2019 (Day −17), the start of a 17-day colonization period. During this, the CO2 (from Day −17) and sediment (from Day −14) manipulations were already implemented. A 35-day “experimental” period (beginning on Day 0) followed, during which temperature and flow velocity were manipulated, as well (Figure 2).
CO2 treatments were randomly assigned at the header tank level, with one CO2-enriched header tank in each of four spatial blocks of two tanks per block. CO2 was bubbled into CO2-enriched header tanks continuously from the start of the colonization period (Day −17). On Days 14 and 28, 1-L water samples taken from 16 randomly selected channels (eight ambient and eight CO2-enriched) were stored in sealed glass bottles and preserved with mercuric chloride for DIC analysis. Within 5 min of sampling, pH and temperature were also measured in these channels using a handheld pH meter (HI-98128; Hanna, Rhode Island).
On Day −2, natural invertebrate colonization was supplemented with taxa underrepresented in the drift by adding one standard sample of the Kauru River benthic invertebrate community to each mesocosm, following the methods described in Piggott, Townsend, and Matthaei (2015a).
Flow velocities were measured in all channels on Days −12, −1, 4, and 11 using a precision flow meter (MiniWater20; Schiltknecht, Gossau, Switzerland). Average near-bed velocity was 20 ± 1.1 cm/s on Day −12, with velocity gradually decreasing over time as prolific benthic algal communities (including filamentous taxa) formed in the channels. Mean velocity prior to beginning flow treatments (Day −1) was 17.9 ± 1.4 cm/s. On Day 4 (the first “fast” period), average velocities were 7.0 ± 2.8 cm/s in “constant” channels and 14.9 ± 3.2 cm/s in “variable” channels. On Day 11 (the first “slow” period), average velocities were 9.3 ± 2.6 and 2.0 ± 1.5 in “constant” and “variable” channels, respectively. Based on these two dates, “variable” channels experienced a mean velocity of 8.5 cm/s across the “fast” and “slow” periods. For “constant” channels, the corresponding mean velocity was 8.2 cm/s.
期刊介绍:
Global Change Biology is an environmental change journal committed to shaping the future and addressing the world's most pressing challenges, including sustainability, climate change, environmental protection, food and water safety, and global health.
Dedicated to fostering a profound understanding of the impacts of global change on biological systems and offering innovative solutions, the journal publishes a diverse range of content, including primary research articles, technical advances, research reviews, reports, opinions, perspectives, commentaries, and letters. Starting with the 2024 volume, Global Change Biology will transition to an online-only format, enhancing accessibility and contributing to the evolution of scholarly communication.