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"

IF 10.8 1区 环境科学与生态学 Q1 BIODIVERSITY CONSERVATION Global Change Biology Pub Date : 2024-09-20 DOI:10.1111/gcb.17510
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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 &lt;2 mm; Zweig &amp; 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. 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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 &lt;2 mm; Zweig &amp; 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. 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引用次数: 0

摘要

Hunn, J. G., Orr, J. A., Kelly, A.-M., Piggott, J. J., & Matthaei, C. D. (2024).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。Global Change Biology, 30, e17336. https://doi.org/10.1111/gcb.17336In 本手稿最初发表的版本中,作者全名被省略。他们是Julia G. Hunn、James A. Orr、Ann-Marie Kelly、Jeremy J. Piggott、Christoph D. Matthaei这一错误已在网上更正。此外,由于排版过程中出现的错误,文中某些位置省略了负号。更正后的文本如下: 2.2 实验设置八个 135 L 的集水槽均以 2 L/min 的恒定排水量向 16 个中样池注入溪水,该排水量是在定殖期开始时(第 -16 天)测量的,并每天重新校准。为了模仿新西兰小溪流(Matthaei 等人,2006 年)的河床底质,从河漫滩收集了 500 毫升中小型砾石,过筛去除细小沉积物(颗粒<2 毫米;Zweig & Rabeni,2001 年),然后添加到每个中观生态系统中,并在上面放置 14 块随机挑选的 40 至 50 毫米扁平鹅卵石。第 0 天,在剩余空间放置一根 PVC 管(长 80 毫米,直径 40 毫米)作为鱼类庇护所,并在出水口上放置一个 1 厘米的不锈钢网罩,以防止鱼类逃逸,每天用过滤的溪水擦洗,以去除任何滞留的有机物质。2.3 实验设计和程序CO2、细沉积物、流速变化和温度在一个全因子 2 × 2 × 2 × 2 设计中进行操作,每个处理组合有八个重复。中置池的水流从 2019 年 10 月 21 日(第 -17 天)开始,即 17 天定植期的开始。在此期间,二氧化碳(从第 -17 天开始)和沉积物(从第 -14 天开始)处理已经开始实施。随后是为期 35 天的 "实验 "期(从第 0 天开始),在此期间也对温度和流速进行了控制(图 2)。CO2 处理是在集流槽一级随机分配的,在四个空间区块(每个区块两个集流槽)中,每个区块都有一个富含 CO2 的集流槽。从定植期开始(第 17 天)起,持续向富含二氧化碳的集气罐中充入二氧化碳。第 14 天和第 28 天,从 16 个随机选取的水道(8 个环境水道和 8 个二氧化碳富集水道)中采集 1 升水样,保存在密封的玻璃瓶中,并用氯化汞保存,以进行 DIC 分析。取样后 5 分钟内,还使用手持式 pH 计(HI-98128;罗德岛汉纳)测量了这些水道的 pH 值和温度。第 -2 天,按照 Piggott、Townsend 和 Matthaei(2015a)中描述的方法,在每个中观生态系中加入一个 Kauru 河底栖无脊椎动物群落的标准样本,以补充漂流中代表性不足的无脊椎动物自然定殖。在第 -12、-1、4 和 11 天,使用精密流量计(MiniWater20;Schiltknecht,瑞士戈绍)测量了所有河道的流速。第 -12 天的近床平均流速为 20 ± 1.1 厘米/秒,随着时间的推移,流速逐渐降低,因为渠道中形成了大量的底栖藻类群落(包括丝状类群)。开始水流处理前(第 1 天)的平均流速为 17.9 ± 1.4 厘米/秒。第 4 天(第一个 "快 "时段),"恒定 "水道的平均流速为 7.0 ± 2.8 厘米/秒,"变化 "水道的平均流速为 14.9 ± 3.2 厘米/秒。第 11 天(第一个 "慢 "周期),"恒定 "和 "可变 "水道的平均流速分别为 9.3 ± 2.6 和 2.0 ± 1.5。根据这两个日期,"可变 "水道在 "快 "和 "慢 "期间的平均流速为 8.5 厘米/秒。对于 "恒定 "通道,相应的平均速度为 8.2 厘米/秒。
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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.

The publisher apologizes for this error.

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来源期刊
Global Change Biology
Global Change Biology 环境科学-环境科学
CiteScore
21.50
自引率
5.20%
发文量
497
审稿时长
3.3 months
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.
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