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完整後設資料紀錄
DC 欄位 | 值 | 語言 |
---|---|---|
dc.contributor.advisor | 關秉宗 | |
dc.contributor.author | Ya-Hui Lin | en |
dc.contributor.author | 林雅慧 | zh_TW |
dc.date.accessioned | 2021-06-15T00:23:16Z | - |
dc.date.available | 2009-02-10 | |
dc.date.copyright | 2009-02-10 | |
dc.date.issued | 2009 | |
dc.date.submitted | 2009-02-02 | |
dc.identifier.citation | 王子定 (1966) 應用育林學。國立編譯館。
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Ogawa, and K. Hozumi. 1963. Self-thinning in overcrowded pure stands under cultivation and natural conditions. Jounal of Biology, Osaka City University 14:107-129. Zhao, D., M. Wilson, and B. E. Borders. 2005. Modeling response curves and testing treatment effects in repeated measures experiments: a multilevel nonlinear mixed-effects model approach. Canadian Journal of Forest Research 35:122-132. | |
dc.identifier.uri | http://tdr.lib.ntu.edu.tw/jspui/handle/123456789/41566 | - |
dc.description.abstract | 本研究以台大實驗林溪頭營林區173號柳杉(Cryptomeria japonica)造林地內之栽植距離試驗林分為試驗區,採用非線性混合效應模式結合2個含有3個參數的Logistic 生長模式,分析2m×2m、3m×3m、4m×4m及 5m×5m等不同栽植距離之小區胸高斷面積(BA)生長資料。第一個生長模式公式為 ,BA(t)為t時間的胸高斷面積(m2 0.1-ha-1),asymp (m2 0.1-ha-1)為模式之漸近線,b 為形數參數,rc (year-1)為生長速率參數。第二個生長模式公式為 ,BA(t)為t時間的胸高斷面積,asymp為模式之漸近線,b1為到達反曲點的時間,b2為從反曲點到達3/4漸近線所花的時間。
分析結果為漸近線(asymp)在兩個模式下皆為混合效應。在第一個模式下,栽植距離對漸近線及形數參數b有顯著影響,但不影響速率參數rc。在第二個模式下,栽植距離對於漸近線及b1有顯著影響,但不影響b2。兩個模式所預測的漸近線結果一致。55年生時,2m栽植距離下平均胸高斷面積為最大(7.29 m2 0.1-ha-1),5m栽植距離下平均胸高斷面積為最小(4.32 m2 0.1-ha-1)。根據第二個模式,四個栽植距離下到達反曲線的時間分別是試驗建立後的第16、19、22及24年,初始的栽植密度愈密,愈早到達生長反曲點。無論在哪一種栽植距離下,林木的內在增殖率皆為0.13,且從反曲點到達3/4漸近線的時間為8年,且各種栽植距離至50年後,胸高斷面積年生長量都接近0。 研究的結果表示最適宜的栽植密度為每公頃2500至3000株,疏伐宜於15至20年施行,輪伐期約為30年,和現今對於柳杉的撫育及經營慣例相似。 | zh_TW |
dc.description.abstract | Using a nonlinear mixed-effects modeling approach, this study analyzed the basal area (BA) growth of a long-term Japanese cedar (Cryptomeria japonica, aka sugi) spacing trial in Sitou District of the Experimental Forest, National Taiwan University. The spacings analyzed were 2m×2m, 3m×3m, 4m×4m, and 5m×5m. To reveal different aspects of BA growth, two 3-parameter logistic growth models were used to analyze the data. The first model was the traditional logistic model with the form , where BA(t) is the BA (m2 per 0.1 ha) at time t (year), asymp (m2) is the asymptote of the model, b is a scale parameter, rc (year-1) is the rate parameter. The second model had the form , where BA(t) is the BA at time t, asymp is the asymptote of the model, b1 (year) is the time need to reach the inflection point, and b2 (year) is the time needed to reach approximately 3/4 of the asymptote after reaching the inflection point.
The results showed that only the asymptote (asymp) in both two models should be considered as a mixed-effect. For the first model, spacing had a significant effect on both asymptote and the scale parameter b, but not on the rate parameter, rc. For the second model, spacing had a significant effect on both asymp and b1, but not on b2. The asymptote estimates from the two models were consistent. After 55 years, the narrowest spacing had the highest average BA per unit area (7.29 m2 per 0.1 ha), whereas the widest spacing had the lowest value (4.32 m2 per 0.1 ha). Based on the results from the second logistic model, the inflection point for the four spacings was reached around 16, 19, 22, and 24 years after the establishment of the spacing trial. The closer the initial spacing, the earlier the inflection point was reached. Regardless of the initial spacing, the estimated rate parameter was 0.13, and the time needed to reach 3/4 of the estimated maximum BA growth was 8 years after reaching the respective inflection points. After 50 years, the annual BA growth was close to 0, regardless of the initial spacing. This study confirmed the current silvicultural and management practices prescribed for the species, that is, the optimal planting density should be between 2500 to 3000 trees ha-1, thinning should commence between age 15 and 20, and the rotation period of the species should be around 30 years. | en |
dc.description.provenance | Made available in DSpace on 2021-06-15T00:23:16Z (GMT). No. of bitstreams: 1 ntu-98-R93625023-1.pdf: 2793260 bytes, checksum: 4d115562639a3cb3082f492e12bca602 (MD5) Previous issue date: 2009 | en |
dc.description.tableofcontents | 目錄
中文摘要…………………………………………………………………i 英文摘要…………………………………………………………………ii 目錄………………………………………………………………………iv 表目錄……………………………………………………………………v 圖目錄……………………………………………………………………vi 附錄目錄………………………………………………………………vii 壹、前言…………………………………………………………………1 貳、前人研究……………………………………………………………3 參、研究材料與方法……………………………………………………15 第一節 研究材料……………………………………………………15 第二節資料處理與分析………………………………………………18 肆、結果…………………………………………………………………25 伍、討論…………………………………………………………………54 陸、結論…………………………………………………………………58 柒、參考文獻……………………………………………………………60 附錄………………………………………………………………………65 表目錄 表一:L ogistic Model Ⅰ之G及R矩陣參數95%信賴區間.........42 表二:Logistic Model Ⅰ胸高斷面積預測模式.................43 表三:Logistic Model Ⅰ模式參數之95%信賴區間..............44 表四:Logistic ModelⅡ之G及R矩陣參數95%信賴區間...........47 表五:Logistic Model Ⅱ胸高斷面積預測模式.................48 表六:Logistic Model Ⅱ模式參數之95%信賴區間..............49 表七:Logistic Model Ⅰ和Logistic Model Ⅱ的比較..........50 圖目錄 圖一:Olindan及Southeastern林分在不同栽植距離下林木株數樹高胸徑變化圖…..5 圖二:Olindan及Southeastern林分在不同栽植距離下林木胸高斷面積材積變化圖..7 圖三:Olindan及Southeastern林分在不同栽植距離下平均胸高斷面積材積變化圖..8 圖四:Olindan及Southeastern林分不同栽植距離下,林木的生長趨線........................9 圖五:使用混合效應模式及生長模式,四種處理下火炬松平均材積生長之差異圖.13 圖六:173號造林地內之栽植距離試驗林分樣區配置圖.............................................15 圖七:胸高斷面積示意圖...............................................................................................16 圖八:173號造林地內之栽植距離試驗林分總胸高斷面積圖.....................................19 圖九:Logistic ModelⅠ之示意圖...................................................................................20 圖十:Logistic Model Ⅱ之示意圖.................................................................................21 圖十一:Logistic ModelⅠ胸高斷面積觀測值及預測值的線性迴歸...........................30 圖十二:Logistic ModelⅠ常態分布分位數散布圖.......................................................31 圖十三:Logistic ModelⅠ標準機差和估計值的散布圖...............................................32 圖十四:Logistic ModelⅠ機差的自相關圖...................................................................33 圖十五:Logistic ModelⅠ模式的預測圖.......................................................................34 圖十六:Logistic Model Ⅱ胸高斷面積觀測值及預測值的線性迴歸.........................35 圖十七:Logistic Model Ⅱ常態分布分位數散布圖.....................................................36 圖十八:Logistic Model Ⅱ標準機差和估計值的散布圖.............................................37 圖十九:Logistic Model Ⅱ機差的自相關圖.................................................................38 圖二十:Logistic Model Ⅱ模式的預測圖.....................................................................39 圖二十一:Logistic ModelⅠasymp參數逢機效應的差異圖........................................41 圖二十二:Logistic Model Ⅱasymp參數逢機效應的差異圖......................................46 圖二十三A:173號造林地內之栽植距離試驗林分林木絕對生長速率圖.................52 圖二十三B:173號造林地內之栽植距離試驗林分之胸高斷面積預測圖...............53 | |
dc.language.iso | zh-TW | |
dc.title | 柳杉栽植距離試驗之林分斷面積生長與收穫 | zh_TW |
dc.title | Stand Basal Area Growth and Yield of Japanese Cedar in a Spacing Trail | en |
dc.type | Thesis | |
dc.date.schoolyear | 97-1 | |
dc.description.degree | 碩士 | |
dc.contributor.oralexamcommittee | 郭幸榮,林世宗,汪大雄,王兆桓 | |
dc.subject.keyword | 柳杉,種內競爭,栽植距離試驗,生長, | zh_TW |
dc.subject.keyword | Cryptomeria japonica,intraspecific competition,spacing trail,growth, | en |
dc.relation.page | 78 | |
dc.rights.note | 有償授權 | |
dc.date.accepted | 2009-02-02 | |
dc.contributor.author-college | 生物資源暨農學院 | zh_TW |
dc.contributor.author-dept | 森林環境暨資源學研究所 | zh_TW |
顯示於系所單位: | 森林環境暨資源學系 |
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