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Effects of atmospheric acid deposition and single versus mixed leaf litters on foliar litter decomposition, carbon, nitrogen, phosphorus and calcium dynamics in a regenerating forest.

机译:大气酸沉降和单叶凋落物与混合叶凋落物对再生林中叶凋落物分解,碳,氮,磷和钙动力学的影响。

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Increases in atmospheric N deposition over the past decades have raised concerns over nitrogen (N) retention and carbon (C) and nutrient cycling in forest ecosystems. We conducted two litter decomposition studies at the Long-Term Soil Productivity (LTSP) study at the Fernow Experimental Forest (FEF) in West Virginia. In the LTSP study acid deposition is simulated by periodic ammonium sulfate additions (N+S). Other treatments include control (ref) (no additions or reference) and ammonium sulfate plus lime (lime). Fresh litter was collected from treatment plots in November. Air-dried litter was weighed, and placed in nylon litter bags. Litter bags were placed in treatment plots in March after snow melt. Mass loss, C, N, P and Ca dynamics were followed for 12 months.;Study 1: To understand how acid deposition interacts to affect ecosystem C, N, P, and Ca cycling and to assess the ability of lime to counteract that effect, we followed decomposition of a litter mix representative of the forest floor composition (oak 48%, yellow poplar 19%, maple 14%, magnolia 12%, cherry 4%, and birch 3%). At 6 and 7 months remaining N content in litter in N+S treatment was significantly lower than in reference and lime treatment (p 0.01) At 12 months, remaining mass was highest in lime treatment (43%) and it was significantly higher than the N+S (39%) and control (37%). Remaining C at 12 months was significantly higher in N+S (42%) treatment than in reference (36%) (p=0.0337). Remaining Ca was significantly higher in N+S treatment (42%) than in reference (36%) (p=0.0051). At 12 months, the remaining P in the N+S treatment (107%) was significantly higher than in the control (83%) and lime treatment (90%). Lower N immobilization and higher P immobilization during leaf litter decomposition in N deposition treatments indicate that high rates of atmospheric N deposition may affect nutrient dynamics during litter decomposition. Our results also showed that lime plays a significant role in decreasing litter decay, increasing N immobilization and decreasing P immobilization, which shows the potential of lime on counteracting the effects of acid deposition.;Study 2: To understand the effects of single versus mixed litters and their interaction with acid and lime treatments on the decomposition of Quercus rubra (oak) litter, we looked at oak in three different litter types. The three litter types: 1.ambient litter mix (48% oak, 19% poplar, 14% maple, 12% magnolia, 4% cherry, and 3% birch), 2. 50% oak and 50% maple leaves and 3. Pure oak. At each sampling oak leaves were sorted from other leaf litter species. Mass loss, C, N, P, and Ca dynamics were quantified in oak decomposing alone (Oak), oak decomposing with maple (Oak+), and oak decomposing with maple, yellow poplar, magnolia, cherry and birch (Oak++). The decay constant (k) was significantly higher in Oak++ (0.682) than in Oak+ (0.614) and in Oak (0.595) (p0.0030). Throughout the 12 months of decomposition, N and P were immobilized in Oak, Oak+, and Oak++ litters in all treatments. Mass loss of oak was significantly affected by litter type. At 12 months, remaining mass of oak was significantly lower in Oak++ (46 %) than in Oak (53 %) and Oak+ litter (51 %) (p0.0001). Presence of other species significantly influenced oak decomposition but had no significant effect on C, N, P or Ca dynamics.
机译:在过去的几十年中,大气中氮的沉积增加,引起了人们对森林生态系统中氮(N)的保留,碳(C)和养分循环的关注。我们在西弗吉尼亚州的Fernow实验森林(FEF)的长期土壤生产力(LTSP)研究中进行了两项凋落物分解研究。在LTSP研究中,通过定期添加硫酸铵(N + S)模拟酸沉积。其他处理方法包括对照(参考)(无添加或参考)和硫酸铵加石灰(石灰)。 11月从处理区收集了新鲜的垃圾。称重风干的垃圾,并放入尼龙垃圾袋中。积雪融化后,三月份将垃圾袋放在处理区。质量损失,碳,氮,磷和钙的动态变化进行了12个月的研究;研究1:了解酸沉降如何相互作用影响生态系统的碳,氮,磷和钙的循环,并评估石灰抵消这种影响的能力,我们接着分解了代表森林地​​面组成的凋落物混合物(橡木48%,黄杨19%,枫树14%,木兰12%,樱桃4%和桦木3%)。在N + S处理的6个月和7个月时,凋落物中的剩余N含量显着低于参考和石灰处理(p <0.01)在12个月时,石灰处理中的残留质量最高(43%),并且显着高于N + S(39%)和对照(37%)。 N + S治疗(12%)时12个月的残留C值显着高于参考值(36%)(p = 0.0337)。在N + S处理中,剩余的Ca显着高于参考指标(36%)(42%)(p = 0.0051)。在12个月时,N + S处理中的剩余P(107%)显着高于对照(83%)和石灰处理(90%)。在氮沉降处理中,凋落物分解过程中较低的固氮量和较高的P固定量表明,较高的大气氮沉积速率可能会影响凋落物分解过程中的养分动态。我们的研究结果还表明,石灰在减少凋落物腐烂,增加N固定化和降低P固定化方面起着重要作用,这表明了石灰具有抵消酸沉降影响的潜力。研究2:了解单一或混合凋落物的影响以及它们与酸和石灰处理对栎栎凋落物分解的相互作用,我们研究了三种不同凋落物类型的橡木。三种垃圾类型:1.环境垃圾混合(48%的橡木,19%的杨树,14%的枫树,12%的木兰,4%的樱桃和3%的桦树),2。50%的橡木和50%的枫树叶子和3。纯橡木。在每个采样中,橡树叶都与其他凋落物种类一起被分类。质量损失,C,N,P和Ca动力学通过单独分解的橡树(Oak),用枫树分解的橡树(Oak +)和用枫木,黄杨树,木兰,樱桃和桦树分解的橡树(Oak ++)进行定量。 Oak ++(0.682)的衰减常数(k)明显高于Oak +(0.614)和Oak(0.595)的衰减常数(p <0.0030)。在整个分解过程的12个月中,所有处理中N和P均固定在Oak,Oak +和Oak ++垫料中。橡树的质量损失受垫料类型的影响很大。在12个月时,Oak ++(46%)的橡树剩余质量显着低于Oak(53%)和Oak +凋落物(51%)(p <0.0001)。其他物种的存在显着影响橡树的分解,但对C,N,P或Ca动力学没有明显影响。

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