Plymouth Marine Laboratory, Prospect Place, Plymouth PL1 3DH, UK.
Philos Trans R Soc Lond B Biol Sci. 2013 Aug 26;368(1627):20120441. doi: 10.1098/rstb.2012.0441. Print 2013.
Ocean acidification (OA), caused by the dissolution of increasing concentrations of atmospheric carbon dioxide (CO2) in seawater, is projected to cause significant changes to marine ecology and biogeochemistry. Potential impacts on the microbially driven cycling of nitrogen are of particular concern. Specifically, under seawater pH levels approximating future OA scenarios, rates of ammonia oxidation (the rate-limiting first step of the nitrification pathway) have been shown to dramatically decrease in seawater, but not in underlying sediments. However, no prior study has considered the interactive effects of microbial ammonia oxidation and macrofaunal bioturbation activity, which can enhance nitrogen transformation rates. Using experimental mesocosms, we investigated the responses to OA of ammonia oxidizing microorganisms inhabiting surface sediments and sediments within burrow walls of the mud shrimp Upogebia deltaura. Seawater was acidified to one of four target pH values (pHT 7.90, 7.70, 7.35 and 6.80) in comparison with a control (pHT 8.10). At pHT 8.10, ammonia oxidation rates in burrow wall sediments were, on average, fivefold greater than in surface sediments. However, at all acidified pH values (pH ≤ 7.90), ammonia oxidation rates in burrow sediments were significantly inhibited (by 79-97%; p < 0.01), whereas rates in surface sediments were unaffected. Both bacterial and archaeal abundances increased significantly as pHT declined; by contrast, relative abundances of bacterial and archaeal ammonia oxidation (amoA) genes did not vary. This research suggests that OA could cause substantial reductions in total benthic ammonia oxidation rates in coastal bioturbated sediments, leading to corresponding changes in coupled nitrogen cycling between the benthic and pelagic realms.
海洋酸化(OA)是由于大气二氧化碳(CO2)在海水中的溶解浓度增加而引起的,预计将对海洋生态和生物地球化学产生重大影响。对微生物驱动的氮循环的潜在影响尤其令人关注。具体来说,在接近未来 OA 情景的海水 pH 值下,氨氧化速率(硝化途径的限速第一步)已被证明在海水中显著降低,但在底层沉积物中没有降低。然而,以前的研究都没有考虑微生物氨氧化和大型底栖动物生物扰动活动的相互作用效应,这些效应可以提高氮转化速率。本研究使用实验中密度培养箱,研究了生活在泥虾 Upogebia deltaura 表面沉积物和洞穴壁内沉积物中的氨氧化微生物对 OA 的响应。与对照(pHT 8.10)相比,将海水酸化至四个目标 pH 值(pHT 7.90、7.70、7.35 和 6.80)之一。在 pHT 8.10 时,洞穴壁沉积物中的氨氧化速率平均是表面沉积物的五倍。然而,在所有酸化的 pH 值(pH ≤ 7.90)下,洞穴沉积物中的氨氧化速率均受到显著抑制(79-97%;p < 0.01),而表面沉积物中的速率不受影响。随着 pHT 的下降,细菌和古菌的丰度均显著增加;相比之下,细菌和古菌氨氧化(amoA)基因的相对丰度没有变化。这项研究表明,OA 可能导致沿海生物扰动沉积物中总底栖氨氧化速率的大幅降低,从而导致底栖和水层之间耦合氮循环的相应变化。