第二章 文獻探討
3.1 實驗材料與 設備
4.3.5 比表面積的測定
表 4.19 水泥的比表面積
BET(m2/g)比表面積 Pore volume(cm3/g)平均孔容
Pore size(Å )平均孔徑。
Sample Hegiht BET(m2/g) Pore size(Å ) Pore volume(cm3/g) 水泥 0.2044 3.7010 0.001045 11.2985
4.3.6 熱重分析與熱差微熱分析(TGA&DTA)的測定 1.9 % weight loss
圖 4.66 水泥 TGA&DTA 圖
顯示熱重和差熱分析(DTA)的水泥催化劑的熱譜。從這個數字可以看出,三個階段的分 解在不同的溫度區的區別。熱對溫度的影響粘貼水泥評估已有報導【86,87】。人們普遍 認為在 120°C 水會完全蒸發消除,110°C-170°C 石膏和鈣礬石開始分解和碳水合物水部分 發生分解。180-300° C 分解水合物的矽酸鈣水合物(csh)和含碳的鋁酸鹽
(carboaluminate)中。結合水的損失和 portlandite 脫羥基反應之間發生脫水反應氫氧 化鈣的脫羥基(氫氧化鈣),大約需要 450-550° C。然後 700° C。以上碳酸鈣開始分解 去碳酸根。
實驗操作變數...
4.3.7 油與甲醇莫耳數比之影響
80 90 100
1/6 1/9 1/15 1/21 1/24
油醇比 轉
酯 率 (
) %
圖 4.67 油與甲醇莫耳數比之影響
反應條件:觸媒鍛燒溫度: 650 °C, 觸媒含量 4 %, 反應時間: 3 h, 反應溫度: 65 °C.
反應油醇比由 1:6~1:24,發現隨油醇比的增加轉酯率也上升。以 1:24 效果最好並以此設 定為最佳參數。
4.3.8 觸媒鍛燒溫度的影響
反應條件:油醇莫耳比:1/24, 觸媒含量 4 %, 反應時間: 3 h, 反應溫度: 65 °C.
觸媒鍛燒溫度條件為 85℃~950℃,發現在 350℃以下時,隨溫度上升轉酯率逐漸提高,
450℃以後反應趨於穩定轉酯率變化不大。不再提高。故以 450℃為最佳反應條件。
0
4.3.10 催化劑回收再利用對轉酯率影響
0 20 40 60 80 100
1 2 3 4 5 6 7
回收次數 轉
酯 率(
)%
圖 4.70 催化劑回收再利用對轉酯率影響
反應條件: 觸媒鍛燒溫度: 650 °C, 油醇莫耳比:1/24,反應時間: 3 h, 反應溫度: 65 °C. 觸 媒含量 4 %。由數據顯示水泥回收次數可重複 4 次,第 5 次開始觸媒逐漸毒化產生失效。
4.3.11 水泥氣相層析圖
圖 4.71 以水泥為催化劑轉酯大豆油氣相層析圖
表 4.20 水泥為催化劑轉酯大豆油氣相層析數據
A:C14 至 C24.1 脂肪酸甲酯成分峰之間的所有成分波峰之積分總面積=651642566 AEI:內標物十七烷酸甲酯之波峰面積=119548873
CEI:所用十七烷酸甲酯之濃度(mg/ml)=配標準品的濃度=10.192mg/ml VEI:所用十七烷酸甲酯之體積(ml)=2ml
m:樣品製備中精秤之樣品量(mg) =111.8mg
帶入以上公式求出 c=81.15%
Apex RT Area %Area
C16:0 4.21 57376689.4 4.53
C17:0 4.61 119,548,873 9.44
C18:0 5.39 281,217,659 22.21
C18:1 5.69 34,666,162 2.74
C18:2 5.76 2,986,253 0.24
C18:3 7.34 1,516,151 0.12
A 651642566
A EI 119548873
CEI 10.192
VEI 2
m 111.8
c 81.15%
4.3.12 以微波合成加熱方式轉酯大豆油為生質柴油之轉酯率
200 400 600 800
微波功率(w)
表 4.22 以微波合成加熱方式-改變不同時間
4.3.13 以水泥為催化劑轉酯大豆油反應機構圖【63-64】
Calcinated waste concrete has high activity for transesterification reaction from soybean oil.
圖 4.74 以水泥為催化劑轉酯大豆油反應機構圖 precursory solid base
+H2O
Soybean oil FAME>96.5%
+ glycerine
calcium silicate hydrate fine aggregate
crush
∆ Ca(OH)2(s)
CaO (s) waste concrete block
∆>900°C cement, fine aggregate
and coarse aggregate coarse aggregate separateness
第五章 結論與建議
5.1 結論:以圖 4.75 表示
本研究先以正交法比較:Ca(NO3)2 、Ca(OH)2、CaO 三種催化劑轉酯反應條件發現以 CaO 效果最佳,進一步由天然物廢棄的蛋殼中經由鍛燒程序產生 CaO 用於生質柴油的轉 酯化反應催化劑提高轉酯反應效率。不但可減少廢棄物又兼具環保功效,所產生的生質 柴油可提供能量用於解決能源問題。在適當的條件下,甲醇/油莫耳比 12:1,催化劑用量 質量比為 2%,反應時間為 2h,蛋殼鍛燒溫度 900°C、鍛燒時間 2h。形成甲基酯轉酯率 可達 95%以上,可重複使用 10 次。水泥磨粉在煅燒後可得到高活性催化劑。煅燒水泥具 有很高的活性對大豆油酯交換生產生質柴油。甲醇/油摩爾比 24:1,水泥 4%的催化劑,
反應溫度 65℃得到了最好的結果,以及生質柴油轉酯超過 98%在 3 小時的反應下。該方 法的水泥塊,是利用廢棄物製備的催化劑,可以做廢物的回收,減少污染,降低催化劑 的成本,對環境友好的催化劑。
圖 4.75 以不同催化劑轉酯大豆油反應機構圖
5.2 未來方向與建議:
目前因為生質柴油的原料油價格關係,使生質柴油的產品製造成本仍然居高不下,價格 上無法與普遍使用的石化柴油競爭,因此要尋找便宜的原料和發展適合它的製程。以蛋 殼與水泥為觸媒轉酯生質柴油是可行的方法。
建議1.可建立廢棄蛋殼回收管道。一方面可達到廢棄物減量與降低生質柴油生產成本。
建議2.可從廢棄建築物混擬土中。將水泥成分分離出用於生產生質柴油。一方面可達到
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