阿中 發問時間: 社會與文化語言 · 9 年前

拜託幫忙翻譯一下!有關 PCDD/F 別用GOOGLE翻譯

Although the reduction of PCDD/F emissionsfrom the MSWI after the new equipment was installed has been very notable(99.9%), the important exposure reduction during the period 1996–2000 (67.6%)has been especially due to the decrease in PCDD/F intake throughout the diet (Llobet et al., 2003). Recent emphasis in the riskanalysis field has been focused on uncertainty in the risk assessment process. Some weakness owing the uncertainties in the data and model parameters must be taken into account. Thesmall number of air stack emissions beforeinstallation of the new equipment, as well asthe lack of consideration of all possibleplume depletion mechanisms in the dispersion and depositionmodeling (atmospheric degradation), can be consideredas a weakness of the model. Congener-specific atmosphericdegradation rates, photolytic dechlorination and/orcongener-specific soil dissipation rates have not beenconsidered. The number of PCDD/F concentrations measuredin air was only one and two for 1996 and 2000, respectively(mean values are here presented). It made the comparisonof predicted and measured air concentrations a tenuousexercise. A similar problem was also found with theemissions from the stack: one and four samples, respectively,before and after installation of the new technicalequipment.

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大大 你是直接丟google翻譯的吧= =

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  • 9 年前
    最佳解答

    可能會被刪而做白工!

    Although the reduction of PCDD/F emissions from the MSWI after the new equipment was installed has been very notable (99.9%), the important exposure reduction during the period 1996–2000 (67.6%)has been especially due to the decrease in PCDD/F intake throughout the diet (Llobet et al., 2003).雖然在新設備組裝後來自於MSWI的PCDD/F 發射的降低是非常顯著的(99.9%),在1996年–2000年期間重大的曝露減少,是由於整個飲食在PCDD/F攝入的減少。 Recent emphasis in the risk analysis field has been focused on uncertainty in the risk assessment process. Some weakness owing the uncertainties in the data and model parameters must be taken into account. 最近在風險分析領域的重點,已經聚焦於風險評估過程中的不確定性。某些弱點歸因於必須考慮資料中和模型參數的不確定性。 The small number of air stack emissions before installation of the new equipment, as well as the lack of consideration of all possible plume depletion mechanisms in the dispersion and deposition modeling (atmospheric degradation), can be considered as a weakness of the model. Congener-specific atmospheric degradation rates, photolytic dechlorination and/or congener-specific soil dissipation rates have not been considered.在新設備設置之前,少量空氣的堆疊釋出以及在傳播和沉積建立模型時缺乏所有可能的卷流耗盡機制的思考(大氣降解), 可以被視為此模型的一個弱點。特定于同類的大氣降解速率、光脫氯和/或特定于同類的土壤耗散率並未被考慮。 The number of PCDD/F concentrations measured in air was only one and two for 1996 and 2000, respectively (mean values are here presented). 1996年和2000年各別在空氣中測得的PCDD/F濃度值只有1和2(平均值在此顯示)。It made the comparison of predicted and measured air concentrations a tenuous exercise. 它使預測的和量測的空氣濃度比較成為空洞無力的課題。(有預測不準的意思)A similar problem was also found with the emissions from the stack: one and four samples, respectively, before and after installation of the new technical equipment. 從此堆疊排的釋放也發現類似的問題: 在新技術設備組裝前和後各別有1個和4個樣品。

    參考資料: 電腦週邊急救團
  • 9 年前

    雖然二惡英/F emissionsfrom 垃圾焚燒後安裝新設備減少已經很 notable(99.9%),重要接觸減少過程期間的 1996–2000 (67.6%)has 特別是由於減少二惡英樓整年的飲食 (Llobet 等人,2003年)。

    Riskanalysis 欄位中的最近強調重點一直在風險評估流程中的不確定性。由於資料和模型參數不確定性的一些弱點必須考慮在內。空氣而數堆疊排放 beforeinstallation 的新設備,以及審議所有 possibleplume 消耗機制中的分散和 depositionmodeling (大氣退化),為缺乏可 consideredas 模型的一個弱點。特定于同類的 atmosphericdegradation 率、 光脫氯和/orcongener 特定的土壤耗散率已不是最後。樓二惡英濃度 measuredin 空氣的人數分別是只有一個,兩個 1996 年和 2000 年,(指此處顯示值)。它由 comparisonof a tenuousexercise 的預測和測量空氣濃度。Theemissions 從堆疊也發現了類似的問題: 1 至 4 個樣本,分別之前和之後的新的 technicalequipment 的安裝。

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