问题不在于我们如何计算酶的化学计量阈值,而在于我们如何计算它

IF 12 1区 环境科学与生态学 Q1 BIODIVERSITY CONSERVATION
Taiki Mori
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Furthermore, while Puissant (<span>2025</span>) suggests that addressing this issue would enable enzyme ratio calculations or vector analyses to serve as indicators of microbial nutrient limitation, I respectfully disagree with this conclusion. This is because multiple studies have shown that enzyme stoichiometry fails to reliably reflect nutrient limitation, and importantly, the enzyme stoichiometry framework has never been empirically validated.</p><p>Thresholds for carbon (C), nitrogen (N), and phosphorus (P) limitations were calculated using regression analyses of enzyme activity data measured under natural conditions. These analyses included: β-1,4-glucosidase (BG) versus N-acetylglucosaminidase (NAG) for C versus N limitation; BG versus acid or alkaline phosphatase (i.e., phosphomonoesterase, AP) for C versus P limitation; and NAG versus AP for N versus P limitation (Sinsabaugh et al. <span>2009</span>). This approach assumes that the enzyme activities used to establish the thresholds represent either conditions of no nutrient limitation or equal limitation by all nutrients. Based on this assumption, deviations from these thresholds can be interpreted as indicators of C, N, or P limitation. However, this assumption lacks theoretical justification (Mori et al. <span>2023</span>; Cui et al. <span>2024</span>). Why should natural conditions be free from nutrient limitation? In fact, ecological understanding suggests that microbial activity is often constrained by one or more limiting nutrients (Kaspari et al. <span>2008</span>). Furthermore, this underlying assumption—that typical or average natural conditions are nutrient-unlimited—is directly contradicted by how the thresholds are applied thereafter. In the application phase, the same type of enzyme data is used to test for nutrient limitations, based on the assumption that a specific nutrient is limiting. Consequently, the construction and application of the thresholds rest on fundamentally contradictory assumptions, leading to a methodological inconsistency.</p><p>Puissant (<span>2025</span>) suggested that enzymatic stoichiometry and vector analysis remain valid methods, provided that enzyme activity ratios are calculated without prior log transformation. However, I respectfully disagree with this conclusion. It is important to underscore that both approaches rest on questionable methodological assumptions. Notably, the enzyme stoichiometry framework has never been empirically validated, whereas multiple independent studies have demonstrated its limitations.</p><p>In particular, direct enzyme activity ratios have repeatedly been shown to inadequately represent microbial nutrient limitations. Several meta-analyses have revealed that the commonly used indicators—BG, NAG combined with leucine aminopeptidase (LAP), and AP—do not accurately represent microbial C, N, and P limitations, respectively (Mori et al. <span>2021</span>; Mor <span>2024b</span>). The enzymatic stoichiometry framework assumes that increasing C availability will lower BG:NAG(+LAP) and BG:AP ratios, while increasing N or P availability will raise these ratios. However, the observed patterns in meta-analyses often run counter to these predictions, calling into question the validity of the approach. It is worth noting that some of these meta-analyses addressed criticisms that short-term responses or fertilization treatments may be unsuitable for evaluating the enzyme stoichiometry approach (Moorhead et al. <span>2023</span>). In response, these meta-analyses relied exclusively on long-term field experiments (Mor <span>2024a</span>) or on C additions that naturally occur in the environment (Mor <span>2024b</span>). Another clear piece of evidence for the inadequacy of the enzymatic stoichiometry approach is that microbial growth responses to fertilization do not correspond with predictions based on enzyme stoichiometry (Rosinger et al. <span>2019</span>). This body of evidence highlights a fundamental limitation of the enzymatic stoichiometry approach: BG, NAG(+LAP), and AP represent only a subset of enzymes involved in microbial nutrient acquisition (Nannipieri et al. <span>2018</span>) and are not the exclusive terminal enzymes specific to each nutrient. Furthermore, these enzymes often participate in the acquisition of multiple nutrients, making them unreliable as proxies for specific nutrient limitations (Mori et al. <span>2023</span>; Cui et al. <span>2024</span>). Therefore, although these enzymes can indicate microbial investment in the acquisition of C, N, and P to some extent, the use of their activity ratios as proxies for nutrient limitation is problematic.</p><p>Vector analysis—which calculates vector length as (x<sup>2</sup> + y<sup>2</sup>)<sup>0.5</sup> and angle (in degrees) as atan2(y, x), where x = BG/(BG + AP) and y = BG/(BG + LAP)—suffers from the same fundamental issue as the direct use of enzyme activity ratios (noting that alternative ratios, such as those including NAG, are also commonly used). In this framework, an increase in BG increases the vector length, while increases in AP and NAG respectively increase and decrease the vector angle. 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In reality, the more fundamental issue lies in the validity of calculating thresholds based on enzyme data itself. Here, I first address the conceptual issues associated with calculating thresholds from regressions of enzyme activity data—even when the log-transformation problem is resolved. Furthermore, while Puissant (<span>2025</span>) suggests that addressing this issue would enable enzyme ratio calculations or vector analyses to serve as indicators of microbial nutrient limitation, I respectfully disagree with this conclusion. This is because multiple studies have shown that enzyme stoichiometry fails to reliably reflect nutrient limitation, and importantly, the enzyme stoichiometry framework has never been empirically validated.</p><p>Thresholds for carbon (C), nitrogen (N), and phosphorus (P) limitations were calculated using regression analyses of enzyme activity data measured under natural conditions. These analyses included: β-1,4-glucosidase (BG) versus N-acetylglucosaminidase (NAG) for C versus N limitation; BG versus acid or alkaline phosphatase (i.e., phosphomonoesterase, AP) for C versus P limitation; and NAG versus AP for N versus P limitation (Sinsabaugh et al. <span>2009</span>). This approach assumes that the enzyme activities used to establish the thresholds represent either conditions of no nutrient limitation or equal limitation by all nutrients. Based on this assumption, deviations from these thresholds can be interpreted as indicators of C, N, or P limitation. However, this assumption lacks theoretical justification (Mori et al. <span>2023</span>; Cui et al. <span>2024</span>). Why should natural conditions be free from nutrient limitation? In fact, ecological understanding suggests that microbial activity is often constrained by one or more limiting nutrients (Kaspari et al. <span>2008</span>). Furthermore, this underlying assumption—that typical or average natural conditions are nutrient-unlimited—is directly contradicted by how the thresholds are applied thereafter. In the application phase, the same type of enzyme data is used to test for nutrient limitations, based on the assumption that a specific nutrient is limiting. Consequently, the construction and application of the thresholds rest on fundamentally contradictory assumptions, leading to a methodological inconsistency.</p><p>Puissant (<span>2025</span>) suggested that enzymatic stoichiometry and vector analysis remain valid methods, provided that enzyme activity ratios are calculated without prior log transformation. However, I respectfully disagree with this conclusion. It is important to underscore that both approaches rest on questionable methodological assumptions. Notably, the enzyme stoichiometry framework has never been empirically validated, whereas multiple independent studies have demonstrated its limitations.</p><p>In particular, direct enzyme activity ratios have repeatedly been shown to inadequately represent microbial nutrient limitations. Several meta-analyses have revealed that the commonly used indicators—BG, NAG combined with leucine aminopeptidase (LAP), and AP—do not accurately represent microbial C, N, and P limitations, respectively (Mori et al. <span>2021</span>; Mor <span>2024b</span>). The enzymatic stoichiometry framework assumes that increasing C availability will lower BG:NAG(+LAP) and BG:AP ratios, while increasing N or P availability will raise these ratios. However, the observed patterns in meta-analyses often run counter to these predictions, calling into question the validity of the approach. It is worth noting that some of these meta-analyses addressed criticisms that short-term responses or fertilization treatments may be unsuitable for evaluating the enzyme stoichiometry approach (Moorhead et al. <span>2023</span>). In response, these meta-analyses relied exclusively on long-term field experiments (Mor <span>2024a</span>) or on C additions that naturally occur in the environment (Mor <span>2024b</span>). Another clear piece of evidence for the inadequacy of the enzymatic stoichiometry approach is that microbial growth responses to fertilization do not correspond with predictions based on enzyme stoichiometry (Rosinger et al. <span>2019</span>). This body of evidence highlights a fundamental limitation of the enzymatic stoichiometry approach: BG, NAG(+LAP), and AP represent only a subset of enzymes involved in microbial nutrient acquisition (Nannipieri et al. <span>2018</span>) and are not the exclusive terminal enzymes specific to each nutrient. 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引用次数: 0

摘要

Puissant(2025)最近的一篇论文适当地提出了对在确定酶化学计量阈值时使用对数转换数据的担忧——这是一个重要而有效的批评。然而,这种讨论给人一种误导的印象,即如果不进行对数变换就计算阈值,那么它们将准确地发挥作用。在现实中,更根本的问题在于基于酶数据本身计算阈值的有效性。在这里,我首先讨论与从酶活性数据的回归计算阈值相关的概念问题,即使对数转换问题已经解决。此外,尽管Puissant(2025)认为解决这个问题将使酶比计算或载体分析能够作为微生物营养限制的指标,但我不同意这一结论。这是因为多项研究表明,酶化学计量不能可靠地反映营养限制,重要的是,酶化学计量框架从未得到经验验证。对自然条件下测得的酶活性数据进行回归分析,计算碳(C)、氮(N)和磷(P)限制阈值。这些分析包括:β-1,4-葡萄糖苷酶(BG)与N-乙酰氨基葡萄糖苷酶(NAG)对C和N的限制;BG与酸性或碱性磷酸酶(即磷酸单酯酶,AP)对C和P的限制;NAG与AP的氮磷限制(Sinsabaugh et al. 2009)。这种方法假定用于建立阈值的酶活性要么代表没有营养限制的条件,要么代表所有营养的同等限制条件。基于这一假设,偏离这些阈值可以解释为碳、氮或磷限制的指标。然而,这一假设缺乏理论依据(Mori et al. 2023; Cui et al. 2024)。为什么自然条件应该不受营养限制?事实上,生态学的理解表明,微生物活动往往受到一种或多种限制性营养物质的限制(Kaspari et al. 2008)。此外,这一基本假设——即典型或平均的自然条件是不受营养限制的——与此后如何应用阈值直接矛盾。在应用阶段,相同类型的酶数据被用于测试营养限制,基于特定营养限制的假设。因此,阈值的构建和应用基于根本矛盾的假设,导致方法论上的不一致。Puissant(2025)认为,酶化学计量学和载体分析仍然是有效的方法,前提是酶活性比的计算不需要事先进行对数变换。然而,我不同意这个结论。必须强调的是,这两种方法都建立在有问题的方法论假设之上。值得注意的是,酶化学计量框架从未经过经验验证,而多个独立研究已经证明了其局限性。特别是,直接酶活性比已多次被证明不能充分代表微生物营养限制。几项荟萃分析显示,常用的指标- bg、NAG联合亮氨酸氨基肽酶(LAP)和ap -不能分别准确地代表微生物C、N和P的限制(Mori et al. 2021; Mor 2024b)。酶化学计量框架假设,增加C的有效性将降低BG:NAG(+LAP)和BG:AP的比率,而增加N或P的有效性将提高这些比率。然而,在荟萃分析中观察到的模式往往与这些预测背道而驰,这使人们质疑该方法的有效性。值得注意的是,其中一些荟萃分析解决了短期反应或受精处理可能不适合评估酶化学计量方法的批评(Moorhead et al. 2023)。作为回应,这些荟萃分析完全依赖于长期的现场实验(Mor 2024a)或环境中自然发生的C添加(Mor 2024b)。酶化学计量方法不足的另一个明显证据是,微生物对施肥的生长反应与基于酶化学计量的预测不一致(Rosinger et al. 2019)。这一证据凸显了酶化学计量学方法的一个基本局限性:BG、NAG(+LAP)和AP仅代表参与微生物养分获取的酶的一个子集(Nannipieri et al. 2018),并不是每种营养素特有的唯一终端酶。此外,这些酶通常参与多种营养物质的获取,因此它们作为特定营养限制的替代指标并不可靠(Mori et al. 2023; Cui et al. 2024)。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

The Problem Is Not How We Calculate Enzyme Stoichiometry Threshold—It Is That We Calculate It

The Problem Is Not How We Calculate Enzyme Stoichiometry Threshold—It Is That We Calculate It

A recent paper by Puissant (2025) appropriately raised concerns about the use of log-transformed data in determining enzymatic stoichiometry thresholds—an important and valid critique. However, this discussion gives the misleading impression that, if the thresholds are calculated without log-transformation, they would function accurately. In reality, the more fundamental issue lies in the validity of calculating thresholds based on enzyme data itself. Here, I first address the conceptual issues associated with calculating thresholds from regressions of enzyme activity data—even when the log-transformation problem is resolved. Furthermore, while Puissant (2025) suggests that addressing this issue would enable enzyme ratio calculations or vector analyses to serve as indicators of microbial nutrient limitation, I respectfully disagree with this conclusion. This is because multiple studies have shown that enzyme stoichiometry fails to reliably reflect nutrient limitation, and importantly, the enzyme stoichiometry framework has never been empirically validated.

Thresholds for carbon (C), nitrogen (N), and phosphorus (P) limitations were calculated using regression analyses of enzyme activity data measured under natural conditions. These analyses included: β-1,4-glucosidase (BG) versus N-acetylglucosaminidase (NAG) for C versus N limitation; BG versus acid or alkaline phosphatase (i.e., phosphomonoesterase, AP) for C versus P limitation; and NAG versus AP for N versus P limitation (Sinsabaugh et al. 2009). This approach assumes that the enzyme activities used to establish the thresholds represent either conditions of no nutrient limitation or equal limitation by all nutrients. Based on this assumption, deviations from these thresholds can be interpreted as indicators of C, N, or P limitation. However, this assumption lacks theoretical justification (Mori et al. 2023; Cui et al. 2024). Why should natural conditions be free from nutrient limitation? In fact, ecological understanding suggests that microbial activity is often constrained by one or more limiting nutrients (Kaspari et al. 2008). Furthermore, this underlying assumption—that typical or average natural conditions are nutrient-unlimited—is directly contradicted by how the thresholds are applied thereafter. In the application phase, the same type of enzyme data is used to test for nutrient limitations, based on the assumption that a specific nutrient is limiting. Consequently, the construction and application of the thresholds rest on fundamentally contradictory assumptions, leading to a methodological inconsistency.

Puissant (2025) suggested that enzymatic stoichiometry and vector analysis remain valid methods, provided that enzyme activity ratios are calculated without prior log transformation. However, I respectfully disagree with this conclusion. It is important to underscore that both approaches rest on questionable methodological assumptions. Notably, the enzyme stoichiometry framework has never been empirically validated, whereas multiple independent studies have demonstrated its limitations.

In particular, direct enzyme activity ratios have repeatedly been shown to inadequately represent microbial nutrient limitations. Several meta-analyses have revealed that the commonly used indicators—BG, NAG combined with leucine aminopeptidase (LAP), and AP—do not accurately represent microbial C, N, and P limitations, respectively (Mori et al. 2021; Mor 2024b). The enzymatic stoichiometry framework assumes that increasing C availability will lower BG:NAG(+LAP) and BG:AP ratios, while increasing N or P availability will raise these ratios. However, the observed patterns in meta-analyses often run counter to these predictions, calling into question the validity of the approach. It is worth noting that some of these meta-analyses addressed criticisms that short-term responses or fertilization treatments may be unsuitable for evaluating the enzyme stoichiometry approach (Moorhead et al. 2023). In response, these meta-analyses relied exclusively on long-term field experiments (Mor 2024a) or on C additions that naturally occur in the environment (Mor 2024b). Another clear piece of evidence for the inadequacy of the enzymatic stoichiometry approach is that microbial growth responses to fertilization do not correspond with predictions based on enzyme stoichiometry (Rosinger et al. 2019). This body of evidence highlights a fundamental limitation of the enzymatic stoichiometry approach: BG, NAG(+LAP), and AP represent only a subset of enzymes involved in microbial nutrient acquisition (Nannipieri et al. 2018) and are not the exclusive terminal enzymes specific to each nutrient. Furthermore, these enzymes often participate in the acquisition of multiple nutrients, making them unreliable as proxies for specific nutrient limitations (Mori et al. 2023; Cui et al. 2024). Therefore, although these enzymes can indicate microbial investment in the acquisition of C, N, and P to some extent, the use of their activity ratios as proxies for nutrient limitation is problematic.

Vector analysis—which calculates vector length as (x2 + y2)0.5 and angle (in degrees) as atan2(y, x), where x = BG/(BG + AP) and y = BG/(BG + LAP)—suffers from the same fundamental issue as the direct use of enzyme activity ratios (noting that alternative ratios, such as those including NAG, are also commonly used). In this framework, an increase in BG increases the vector length, while increases in AP and NAG respectively increase and decrease the vector angle. Thus, vector analysis is essentially a visual reformulation of the enzyme ratio approach and inherits its conceptual limitations.

Overall, while I fully agree with Puissant (2025)'s critique regarding the misuse of log-transformation in enzyme activity data, I argue that resolving this issue does not address the core problem. The fundamental limitations of the enzyme stoichiometry approach persist, even when the log-transformation concern is corrected.

The author declares no conflicts of interest.

This article is a Letter to the Editor regarding Jérémy Puissant https://doi.org/10.1111/gcb.70228. See also the Response to the Letter by Jérémy Puissant https://doi.org/10.1111/gcb.70517.

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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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