水生植物荇菜和菹草分解对物种混合的响应研究

EFFECT OF MIXED FLOATING AND SUBMERGED MACROPHYTES ON DECOMPOSITION RATE AND NUTRIENT DYNAMICS

  • 摘要: 为探讨水生植物混合的分解效应, 研究了浮叶植物荇菜(Nymphoides peltatum)、沉水植物菹草(Potamogeton crispus)及两物种混合的分解速率和养分动态。结果显示: (1)两单物种的分解速率与初始N含量呈显著正相关关系(P 0.05, r=0.862), 荇菜和菹草分解90d后的干重剩余率分别为24.74%和44.91%。物种混合干重剩余率在分解初期阶段的实测值比期望值高6.63% (P 0.05), 表明物种混合对分解速率具有拮抗效应, 但在随后的分解时间里无显著的混合效应, 分解90d后干重剩余率为30.39%; (2)在分解初期的N、P释放阶段, 物种混合的N、P剩余率实测值比其期望值分别高14.36%和12.88% (P 0.05), 表明物种混合对初期N、P元素释放具有拮抗效应, 在随后的分解过程中对N元素无显著的混合效应, 但分解后期P剩余率实测值比期望值低4.26% (P 0.05), 表现为协同效应; (3)物种混合N、P动态在分解初期呈一个快速释放的过程, 但在随后的分解阶段N元素释放或积累, P元素持续释放, 最终N、P均表现为净释放, 与两单物种分解的N、P动态的规律基本一致。另外, 总酚在物种混合分解初期释放迅速, 随后释放缓慢。研究结果表明, 荇菜和菹草混合分解存在非加和效应, 即单物种的分解速率和营养动态变化不能用来预测两物种混合的分解速率和营养动态变化。物种混合在分解的不同阶段其分解效应不同, 这说明混合效应具出一定的时间依赖性。此外, 混合效应与浮叶植物和沉水植物其初始质量特征有较密切的关系。

     

    Abstract: Decomposition of aquatic macrophytes can considerably influence nutrient cycling and energy flow in aquatic ecosystems, and may therefore alter aquatic ecosystem structure and functioning. Most studies of decomposition processes have focused on single species of aquatic macrophytes; however, most aquatic ecosystems consist of a mixture of aquatic plant species and fragments they produce which intermingle during decomposition. To explore the effect of species mixtures of aquatic macrophytes with different life forms, decomposition rate and nutrient dynamics were quantified in mixed-species litterbags (containing Nymphoides peltatum, a floating-leaved plant, and Potamogeton crispus, a submerged plant) and in litterbags containing fragments of a single species in a laboratory experiment. There were 10 g of materials used for each species in the litter bags, and for the mixture experiment, also 10 g of the dried macrophyte fragments were used at a mixtures rate of 5:5, Nymphoides:Potamogeton, w/w basis). The decomposition rates, nitrogen and phosphorus content of the remaining materials were determined after 10, 20, 30, 40, 60, and 90 days. Data from single-species litterbags were used to generate expected decomposition rates, nitrogen and phosphorus dynamics for mixed-species litterbags experiments. The result showed that the decomposition rates of N. peltatum (0.032/d) was pronounced higher than that of P. crispus (0.017/d), 24.74% and 44.91% dry mass remaining after 90 days, respectively. The decomposition rates of both N. peltatum and P. crispus were significantly and positively correlated with initial N content (P 0.05, r = 0.862). The decomposition rate of the mixture was 0.023/d which was intermediate between N. peltatum and P. crispus. The observed remaining mass of the mixture at the early stages of decomposition in ten days was 6.63% (P 0.05) higher than the expected, indicating the occurrence of negative, non-addtivie effects of mixed species early on. In contrast, there was no significant mixing effect after ten days in subsequent samplings. After 90 days, the remaining dry mass of the mixture was 30.39%. The N and P contents of both N. peltatum and P. crispus released rapidly at the early stages and then slowed down. The remaining percentage of N and P of N. peltatum were lower than that of P. crispus. During the early stages of decomposition of mixed material in ten days, the observed N and P remaining were 14.36% and 12.88% (P 0.05) higher than the expected, indicating the occurrence of antagonistic effects on N and P release in the mixture. However, there were no significant antagonistic mixing effects in subsequent times for N. After 90 days, the observed P remaining was 4.26% (P 0.05) lower than expected, indicating a synergistic effect on P release occurred. The remaining percentage of N and P were 43.60% and 15.88%, respectively. Nutrients and polyphenol concentrations in the mixture decreased rapidly at the early stages and then decreased slowly through the end of the study, in a manner similar to that of the single species. Our results indicated that there were negative, non-additive effects on decomposition rate, N and P releases when two species were mixed together at the early stages, while there was a synergistic effect on P release in the final stage of the decomposition. This suggests that neither decomposition nor nutrient release patterns can be assessed on basis of single species dynamics. In addition, there was a significant time-independent non-additive effect of species interactions. We further suggest that different aquatic macrophytes of contrasting life forms such as floating-leaved plants and submerged plants may differ in initial chemical quality and may exhibit major determinants for decomposition of mixed aquatic macrophytes.

     

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