3个爱沙尼亚湖泊浮游植物生产力的估算/ futoplankton Productivity [j] . Hindamine Kolmes Eesti Jarves

T. Kauer, H. Arst, T. Nõges, L. Tuvikene
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引用次数: 3

摘要

光为浮游藻类和所有其他光自养植物将无机物转化为有机物提供了必要的能量。初级生产力是光合作用的直接产物,初级生产力是生态系统中所有光合速率的总和(Fee, 1998)。关于初级生产的信息有助于提高对水生生态系统中食物网关系的认识。由于光照条件的变化,初级生产具有明显的昼夜模式。为了获得较长时间(日、月、年)的综合结果,需要对瞬时光合速率进行多次连续测量并进行综合。在一些研究中(Joniak et al., 2003;吉田等人,2003;Forget et al., 2007)通过原位孵育估算了光区综合的每日初级产量值。然而,这种方法只有在清澈的水中才能得到可靠的结果,而在高产的水中,由于光合产物的呼吸作用(Lancelot & Mathot, 1986)和细胞外产物的释放(holler Jensen, 1985),在长期孵育过程中,部分c -标签会从细胞中丢失,因此不能长时间(例如从早上到晚上)进行孵育。生物光学模型计算可以替代耗时的14C方法。一些研究估计浮游植物色素的主要产量来自于光强和丰度(引自Arst等人,2008a)。如果感兴趣的过程发生在较长的时间尺度上,通常忽略日变化并使用平均每日光合有效辐照度(PAR)来强迫初级生产者的模式。广泛使用的方法包括用包含两个参数的方程来表示光合作用对可用光的依赖:初始斜率[[alpha].sup。[β]和同化数[P.sup.B.sub.][m] (Sathyendranath et al., 1989)。在这些模式中,光合有效辐射(PAR)的垂直剖面数据(Einst [h.sup.])。[m.sup. 2])是必需的。这是一种相当复杂的方法,其结果基于PAR区域的辐射积分。然而,为了可靠地描述初级生产剖面,最好使用“光谱方法”,其中模型基于水下量子辐照度和浮游植物吸收系数的光谱数据(Sathyendranath等人,1989;Smith et al., 1989;Schofield et al., 1990;Kyewalyanga等人,1992;柯克,1994;Sosik, 1996;Arst et al., 2006, 2008a)。Arst等人(2008a)阐述了用于计算湖泊初级生产垂直剖面的半经验模型的两个版本(光谱和积分)。两种模式的主要区别在于水下辐照度的数据(光谱或积分)。利用2003-2005年爱沙尼亚三个浑浊湖泊(佩普西、沃尔茨贾夫和哈库)生物光学参数的原位测量数据,对这些模型进行了量化。本研究的目的是:(1)通过计算三个湖泊不同深度在所有测量日的光谱和日变化来证明水下量子辐照度的变异性;(2)将2007 - 2008年现场初级产量测量结果与相应的模型结果进行对比;(3)利用模型计算估算初产垂向剖面的日变率及相应的综合(过水柱)值。材料和方法研究地点在爱沙尼亚的三个湖泊:Peipsi、Vortsjarv和Harku进行测量。湖泊的形态测量数据及其他参数见表1。佩普斯湖是爱沙尼亚和俄罗斯边界上的一个大浅湖。…
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Estimation of the Phytoplankton Productivity in Three Estonian Lakes/ Futoplanktoni Produktiivsuse Hindamine Kolmes Eesti Jarves
INTRODUCTION Light provides the energy necessary for the transformation of inorganic matter into organic matter by the planktonic algae and all other photoautotrophic plants. Primary production is the direct product of photosynthesis, and primary productivity is the sum of all photosynthetic rates in an ecosystem (Fee, 1998). Information on the primary production enables to improve the understanding of food web relationships in aquatic ecosystems. Because of changing light conditions, primary production has a pronounced diel pattern. In order to acquire integrated results over longer time periods (days, months, years), many consecutive measurements of instantaneous photosynthesis rate should be carried out and integrated. In some studies (Joniak et al., 2003; Yoshida et al., 2003; Forget et al., 2007) the values of daily primary production integrated over the photic zone were estimated from in situ incubations. However, such approach gives reliable results only in clear waters, while in highly productive waters incubation cannot be performed during a long period (e.g. from morning to evening) as part of the [sup.14]C-label gets lost from the cells during long-term incubation due to respiration of photosynthetic products (Lancelot & Mathot, 1986) and release of extracellular products (holler Jensen, 1985). Bio-optical model calculations could provide an alternative to the time-consuming 14C method. Several studies estimate primary production from light intensity and abundance of phytoplankton pigments (cited in Arst et al., 2008a). In cases the processes of interest occur on a longer time-scale, it is common to ignore diurnal variations and use mean daily photosynthetically available irradiance (PAR) to force models of primary producers. Widely used methods include those where the dependence of photosynthesis on available light is expressed by an equation containing two parameters: the initial slope [[alpha].sup.[[beta] and the assimilation number [P.sup.B.sub.m] (Sathyendranath et al., 1989). In these models also data on the vertical profiles of the photosynthetically active radiation (PAR) (Einst [h.sup.-1] [m.sup.-2]) are needed. This is a rather complicated way and gives results on the basis of radiation integrated over the PAR region. For reliable description of primary production profiles, however, it is preferable to use a 'spectral approach', in which the model is based on spectral data of underwater quantum irradiance and absorption coefficients of phytoplankton (Sathyendranath et al., 1989; Smith et al., 1989; Schofield et al., 1990; Kyewalyanga et al., 1992; Kirk, 1994; Sosik, 1996; Arst et al., 2006, 2008a). Two versions (spectral and integral) of a semi-empirical model for calculation of the vertical profiles of primary production in lakes were elaborated by Arst et al. (2008a). The main difference between the models resides in the data on underwater irradiance (spectral or integral). Quantification of these models was performed using the data of in situ measurements of bio-optical parameters in three turbid Estonian lakes (Peipsi, Vortsjarv, and Harku) in 2003-2005. The objectives of the present study were (1) to demonstrate the variability of underwater quantum irradiance by calculating its spectral and diurnal variations at different depths of three lakes for all measurement days; (2) to compare in situ primary production measurement results obtained in 2007 2008 with corresponding model results; and (3) using model calculations to estimate the diurnal variability of the vertical profiles of primary production as well as the corresponding integrated (over water column) values. MATERIALS AND METHODS Study sites The measurements were carried out in three Estonian lakes: Peipsi, Vortsjarv, and Harku. Morphometric data and other parameters of the lakes are shown in Table 1. Lake Peipsi is a large shallow lake on the border of Estonia and Russia. …
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