TWI302198B - - Google Patents

Download PDF

Info

Publication number
TWI302198B
TWI302198B TW94118467A TW94118467A TWI302198B TW I302198 B TWI302198 B TW I302198B TW 94118467 A TW94118467 A TW 94118467A TW 94118467 A TW94118467 A TW 94118467A TW I302198 B TWI302198 B TW I302198B
Authority
TW
Taiwan
Prior art keywords
scope
concentration
biosensor
urea
enzyme
Prior art date
Application number
TW94118467A
Other languages
Chinese (zh)
Other versions
TW200643417A (en
Inventor
Hsiao Chung Tsai
Ruey An Doong
Original Assignee
Hsiao Chung Tsai
Ruey An Doong
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Hsiao Chung Tsai, Ruey An Doong filed Critical Hsiao Chung Tsai
Priority to TW094118467A priority Critical patent/TW200643417A/en
Publication of TW200643417A publication Critical patent/TW200643417A/en
Application granted granted Critical
Publication of TWI302198B publication Critical patent/TWI302198B/zh

Links

Landscapes

  • Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
  • Control Of Non-Electrical Variables (AREA)

Description

1302198 九、發明說明: 【發明所屬之技術領域】 本發明係關於-種簡化化學感測器系統研發過程中 最佳化程序(optimization)之方法,特別是有關一種簡化 生物感測器系統研發過程中最佳化程序之方法。 【先前技術】 以pH改變為偵測基準的感測器已成為感測器技術發 展中之4要-環,此贼測H侧職驗指稍來感測化 學或酵素反應中質子或氫氧根離子的濃度變化。在一些對 pH值敏感之染劑分子(如溴酚藍【br〇m〇phen〇lblue】、漠 甲盼紫【bromcresol pUrpie】、瑞香酚藍【thym〇1 Wue】、 9-(4-diethylamino-2-octadecyloxy -styryl).acridine 、 carboxy-seminaphtharhodafluor]、aminofluorescein 及螢光 黃【fluorescein】)中,因螢光黃於氬離子雷射波長為488nm 時具有高莫爾濃度吸收性、高螢光產量及廣為人知的光學 特性’是以成為一適用於上述感測器之螢光探針。此外, 由於螢光黃已被商業化地利用於具有不同分子量之葡萄 聚醣衍生物中,是以可將習知存於溶膠_凝膠或聚合物包埋 中之漏>4問題降至最低。 目刖’模式模擬(model simulation)已成為一有用工 具,用以描述實驗過程中之現象及預估不同情況下調查系 統可此之行為。可靠的數學模型不僅有助於確認觀察結果 1302198 的正確性,並可理出存在於系統中之可能反應機制。更有 甚者,在感測器的發展過程中,此類模型亦可用以簡化繁 几的最佳化過程。儘管上述感測器之設計與應用已被廣泛 地研究,然而可用以預測系統1)11值變化與結果訊號之數 學模型仍有待發展。 【發明内容】 本發明之目的在於提供一種簡化化學感測器系統研 發過程中最佳化程序之方法。 本發明之另一目的在於提供一種簡化生物感測器系統研 發過程中最佳化程序之方法。 本發明提供一種簡化生物感測器系統研發過程中最 佳化程序之方法,其中此生物感測器系統具有一緩衝溶 液、、一反應物與一酵素,此生物感測器並以pH變化為偵測 基準。首先,推估此生物感測器系統中對緩衝溶液之緩衝 強度具有f彡響能力之所有組成份,射部分組成物係來自 於反,物與酵素之相互反應。接著,雜緩衝強度模 式4算緩衝強度,並在不同反應物濃度與不同阳值之複數 種參數組合下,得知麟能力之分佈。在生械測器系統 到達平衡時,對緩衝能力進行積分,以得知生物感測器系 統之最終pH值。 【實施方式】 1302198 本發明揭露一種簡化生物感測器系統研發過程中最 佳化程序之方法。現依據本發明之一較佳實施例,詳述如 下。 1.原理 1.2 線性之緩衝強度模型 〇inear buffer capacity model) 滴定曲線之斜率與溶液中pH值的變化有關。請參照 下列反應式(1),溶液的緩衝能力⑽係反比於滴定曲線之斜 率:1302198 IX. DESCRIPTION OF THE INVENTION: TECHNICAL FIELD OF THE INVENTION The present invention relates to a method for simplifying optimization in the development of a chemical sensor system, and more particularly to a simplified biosensor system development process. The method of optimizing the program. [Prior Art] The sensor with pH change as the detection reference has become the 4th-ring in the development of sensor technology. This thief measures the H-side job index to sense the proton or hydrogen in the chemical or enzyme reaction. The concentration of root ions changes. In some dye-sensitive dye molecules (such as bromophenol blue [br〇m〇phen〇lblue], bromocresol pUrpie], thymol blue [thym〇1 Wue], 9-(4-diethylamino -2-octadecyloxy-styryl).acridine, carboxy-seminaphtharhodafluor], aminofluorescein and fluorescein], high fluorescence concentration and high fluorescence yield due to fluorescence yellow at argon ion laser wavelength of 488 nm The well-known optical property 'is a fluorescent probe suitable for the above-mentioned sensor. In addition, since fluorescent yellow has been commercially used in dextran derivatives having different molecular weights, it is possible to reduce the problem of leaks >4 which are conventionally stored in sol-gel or polymer embedding. lowest. The visual 'model simulation' has become a useful tool to describe the phenomena in the experiment and to estimate the behavior of the survey system in different situations. A reliable mathematical model not only helps to confirm the correctness of the observation 1302198, but also to clarify the possible reaction mechanisms that exist in the system. What's more, in the development of sensors, such models can also be used to simplify the optimization process. Although the design and application of the above sensors have been extensively studied, the mathematical model that can be used to predict system 1) 11 value changes and result signals remains to be developed. SUMMARY OF THE INVENTION It is an object of the present invention to provide a method for simplifying the optimization process in the development of a chemical sensor system. Another object of the present invention is to provide a method of simplifying the optimization process in the development of a biosensor system. The present invention provides a method for simplifying an optimization procedure in a development of a biosensor system, wherein the biosensor system has a buffer solution, a reactant and an enzyme, and the biosensor is changed in pH. Detection benchmark. First, it is estimated that all components of the biosensor system have a fucking ability to the buffering strength of the buffer solution, and the part of the composition is derived from the interaction of the substance and the enzyme. Next, the hetero-buffer strength mode 4 calculates the buffer strength, and the distribution of the lining ability is known under the combination of various reactant concentrations and different yang values. When the biosensor system reaches equilibrium, the buffering capacity is integrated to know the final pH of the biosensor system. [Embodiment] 1302198 The present invention discloses a method for simplifying the optimization procedure in the development of a biosensor system. DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENTS In accordance with a preferred embodiment of the present invention, the following is detailed. 1. Principle 1.2 Linear buffer strength model 〇inear buffer capacity model) The slope of the titration curve is related to the change in pH in the solution. Please refer to the following reaction formula (1). The buffer capacity of the solution (10) is inversely proportional to the slope of the titration curve:

dpH dpHdpH dpH

其中CA及CB為添加於系統中之強酸/強鹼濃度。實際 上’緩衝強度可藉由各種方法(如一般滴定曲線模型 【general titration curve model】、線性緩衝強度模型【linear buffer capacity model】、非線性象徵緩衝強度模型 【non_linear symbolic buffer capacity model】以及非線性 擬_法之緩衝強度模型【non_linear tableau_method based buffer capacity model】。若僅考慮酸鹼化學平衡,則由一 系列反應式所代表之線性緩衝強度模型已足以用來描述 觀察所得之緩衝能力相關數據。非線性係指將系統中其 他反應(如複合反應與沈澱反應)的結果,亦一併納入 考量,此時模型中與反應平衡相關之各個參數皆呈非線 性。相較之下,線性緩衝強度模式因具有計算快速、極 1302198 * 佳的驗證(imPiementati〇n)與容錯能力⑽她㈣,以及容 易應用於新模型等優點,是以在本發财,_用此模 型來計算溶液的緩衝強度。 7以含有/單質子(含水)、w雙質子,與”三質子 之弱酸為例,緩衝能力之計算如下列方程式所示··、 (2) ⑶ β = 2303χΙΗΊχίι + Σ^^^ 1 b erm x = C aK a --!_ i[H+]+ Ka)2Among them, CA and CB are strong acid/strong alkali concentrations added to the system. In fact, the buffer strength can be obtained by various methods (such as general titration curve model, linear buffer capacity model, non-linear symbolic buffer capacity model, and nonlinearity). The non-linear tableau_method based buffer capacity model. If only the acid-base chemical equilibrium is considered, the linear buffer strength model represented by a series of reaction formulas is sufficient to describe the observed buffer capacity related data. Nonlinearity refers to the results of other reactions in the system (such as complex reaction and precipitation reaction), which are also taken into consideration. At this time, the parameters related to the reaction equilibrium in the model are nonlinear. In contrast, the linear buffer strength The model has the advantages of fast calculation, extremely accurate 1302198* (impiementati〇n) and fault tolerance (10), and (4), and easy to apply to the new model. It is based on this model to calculate the buffer strength of the solution. 7 with / single proton (aqueous), w double proton, For example, the weak acid of the three protons is calculated as the following equation. · (2) (3) β = 2303χΙΗΊχίι + Σ^^^ 1 b erm x = C aK a --!_ i[H+]+ Ka )2

term 2 =CaKaXTerm 2 =CaKaX

(4) (5) 其中ca與Ka各為此弱酸之濃度及解離常數,切mi、 term2、與term3則分別代表單質子、雙質子及三質^等 組成。溶液的總緩衝強度等於此三組成貢獻之 的緩衝則以單質子酸視之。錢定曲線法相比,由於線 性缓衝強度模型並不考餘何與驗添加量有關之變異 因子,是以成為便於執行電腦程式之方法。 又’、 1.2生物感測器中之緩衝能力 1302198 由上述方程式(2)至(5)中可知,溶液之pH值與存在於 >谷液中之可能組成份’為構成緩衝能力的兩個主要參數。 在本實施例中,茲以尿素分解(urease)、肌酸酐去亞胺 (creatinine deiminase ; CD )與乙醯膽鹼醋 (acetylcholinesterase ; AChE)為例,說明線性緩衝強度 模型之適當性與適用性。請參照下列方程式,其分別為尿 素分解、肌酸酐去亞胺與乙醯膽鹼酯所催化之水解反應 (化學式中之英文專有名詞已轉譯於内文中): (A)(4) (5) where ca and Ka are each a weak acid concentration and dissociation constant, and cut mi, term2, and term3 represent a single proton, a double proton, and a triple mass, respectively. The buffer with a total buffer strength equal to the contribution of the three constituents is treated as a single protonic acid. Compared with the Qianding curve method, the linear buffer strength model does not take into account the variation factors related to the added amount, which is a method for facilitating the execution of computer programs. ', 1.2 Buffering capacity in biosensors 1302198 As can be seen from equations (2) to (5) above, the pH of the solution and the possible components present in the > trough are 'two buffering capacities. The main parameters. In this example, the urea lysis, creatinine deiminase (CD) and acetylcholinesterase (AChE) are taken as examples to illustrate the appropriateness and applicability of the linear buffer strength model. . Please refer to the following equation, which is the hydrolysis reaction catalyzed by urea decomposition, creatinine deimin and acetylcholine ester. (English nouns in the chemical formula have been translated in the text): (A)

II urease H2N-C-NH2 3H20 Urea 2ΝΗ:+ HCCV+ Ohf (B)II urease H2N-C-NH2 3H20 Urea 2ΝΗ: + HCCV+ Ohf (B)

o HNo HN

Creatinine deiminase HfsT CH3 Creatinine H20Creatinine deiminase HfsT CH3 Creatinine H20

NH4+ + 〇H- N-Methylhydantoin N _ Cf (C) ^ AChE H3C-c—〇-(ch2)j~n (Chya h2〇 H+NH4+ + 〇H- N-Methylhydantoin N _ Cf (C) ^ AChE H3C-c-〇-(ch2)j~n (Chya h2〇 H+

CholineCholine

Acetylcholine 在尿素分解之糸統中’胺鹽(ammonium)離子、碳 酸鹽(carbonate)離子與氫氧根離子會在水解反應後自 系統中釋放出來。相似地,在肌酐酸去亞胺所催化之 水解反應中,亦可觀察到胺鹽離子與氫氧根離子的存 在,唯一不同的是此水解系統會產生N-曱基乙内醯 1302198 (N-methylhydantoin)。相異於上述兩種反應,乙醯膽鹼 被乙醢膽驗分解後,會產生膽驗(choline)、乙酸(acetic acid)及氫質子。請參照圖一,顯示水、ι,3-二[三(氫氧 曱基)曱基氨基]丙烧【l,3_bis[tris(hydroxymethyl) methylamino]propane ; BTP】(以下簡稱 BTP )緩衝溶液, 以及上述三個式子中各反應物/產物之解離常數。由於這 些組成份皆會影響溶液之緩衝能力,是以需將其效用皆 納入考量。然而,值得注意的是,在本發明中,乙醯膽 鹼與尿素並未被囊括於模型中。此係導因於乙醯膽鹼沒 有解離中心,因此假設其不會產生解離反應。爰另,尿 素之解離常數為-2.54、(U、14.43與18.30 (利用購自加 拿大 Advance Chemistry Development 公司之 ACD/pKa ν7·02軟體計算而得),由於這些解離常數皆已超過正常 pH值範圍(ΡΗ 1 — 14),是以將其對溶液緩衝能力之貢 獻忽略。 在計算緩衝能力時,假定產物的莫爾數遵循著化學 計量關係。本發明即根據線性緩衝強度模型及產物的預 定量,發展出一程式(MATLAB),用以計算不同生物感 測器系統中之緩衝能力,並在不同反應物濃度與不同pH 值等情況下,得知緩衝強度之3D分佈。圖二A〜C顯示 濃度為1 mM之BTP緩衝溶液,其於不同pH值、不同 反應物(分別為尿素、肌酐酸與乙醯膽鹼)濃度下之缓 衝強度3D分佈圖。其中,pH值被設定在5至10間,以 滿足大部分的生物系統;反應物濃度則設為1 μΜ至 10 1302198 M。模擬結果顯示在尿素分解系統中,當pH值為6·4時, 緩衝強度為0.06 dM/dpH ;而在pH值為9.2時,缓衝強 度為0.14 dM/dpH。在肌酐酸去亞胺_肌酐酸系統中, 當pH值為5時,緩衝強度為〇·〇6 dM/dpH ;而當pH值 增加至9·3 ’援衝強度亦隨之上升至0.12 dM/dpH。迴異 於上述’在乙醯膽鹼分解系統中,當pH值大於6時,緩 衝強度幾乎維持不變,此可能導因於乙酸與膽驗之解離 常數(各為4.76與13·9)已脫離受測的pH範圍(pH 5 -10) 〇 在以pH為偵測基準之生物感測器中,質子或氫氧根 離子係產生自一酵素反應,且這些離子之生成量應與修 訂後之反應物濃度相關。由於這些的離子會與總緩衝能 力相抵抗,是以可改變溶膠-凝膠基質中之pH值。有鑑 於此,在系統達到平衡時,由pH值所得之緩衝能力的積 分,應等同於下列方程式(6)中質子或氫氧根離子的莫 爾濃度。一旦不同濃度之反應物被摻入含有不同濃度與 起始pH值之BTP緩衝溶液中,系統的最終pH值即可被 得知。Acetylcholine in the system of urea decomposition, 'ammonium ions, carbonate ions and hydroxide ions are released from the system after hydrolysis reaction. Similarly, in the hydrolysis reaction catalyzed by creatinine deimin, the presence of amine salt ions and hydroxide ions can also be observed, the only difference being that the hydrolysis system will produce N-mercaptoacetone 1302198 (N -methylhydantoin). Different from the above two reactions, acetylcholine is decomposed by acetaminophen, which produces choline, acetic acid and hydrogen protons. Referring to Figure 1, the water, i, 3-, [3, bis[hydroxymethyl]methylamino]propane; BTP] (hereinafter referred to as BTP) buffer solution is shown. And the dissociation constant of each reactant/product in the above three formulas. Since these components all affect the buffering capacity of the solution, it is necessary to take into account its utility. However, it is worth noting that in the present invention, acetylcholine and urea are not included in the model. This is due to the fact that acetylcholine does not have a dissociation center, so it is assumed that it does not produce a dissociation reaction. ,In addition, the dissociation constant of urea is -2.54, (U, 14.43 and 18.30 (calculated using ACD/pKa ν7·02 software purchased from Advance Chemistry Development, Canada), since these dissociation constants have exceeded the normal pH range. (ΡΗ 1-14) is to ignore its contribution to the buffering capacity of the solution. In calculating the buffering capacity, it is assumed that the moiré of the product follows a stoichiometric relationship. The present invention is based on a linear buffer strength model and a predetermined amount of product. A program (MATLAB) was developed to calculate the buffering capacity of different biosensor systems, and the 3D distribution of buffer strength was obtained under different reactant concentrations and different pH values. Figure 2A~C A 3D distribution of buffer strength at a concentration of 1 mM BTP buffer at different pH values and different reactants (urea, creatinine and acetylcholine, respectively), wherein the pH is set at 5 Up to 10 to meet most biological systems; the concentration of the reactants is set to 1 μΜ to 10 1302198 M. The simulation results show that in the urea decomposition system, when the pH is 6.4, the buffer strength 0.06 dM/dpH; at a pH of 9.2, the buffer strength is 0.14 dM/dpH. In the creatinine deiminol-creatinine system, when the pH is 5, the buffer strength is 〇·〇6 dM/ dpH; and when the pH is increased to 9·3', the intensity of the acuity also rises to 0.12 dM/dpH. It is different from the above. In the acetylcholine decomposition system, when the pH is greater than 6, the buffer strength is almost maintained. No change, this may be due to the dissociation constant of acetic acid and biliary test (4.76 and 13.9 each) has deviated from the measured pH range (pH 5 -10) 〇 in the pH-based biosensor The proton or hydroxide ion is generated from an enzyme reaction, and the amount of these ions should be related to the modified reactant concentration. Since these ions will resist the total buffer capacity, the sol-condensation can be changed. The pH value in the gel matrix. In view of this, when the system reaches equilibrium, the integral of the buffering capacity obtained from the pH value should be equal to the molar concentration of the proton or hydroxide ion in the following equation (6). The reactants are incorporated into a BTP buffer solution containing different concentrations and initial pH, systemic The final pH value can be known.

Ca or CB = j β dpH 1·3 FITC-葡萄聚醣的激發螢光(Emitted fluorescence of FITC-dextran ) 螢光黃主要係以陽離子(FH/)、中性(FH2)、一價 1302198 陰離子_或二價陰離子(F2·)等解離型態存在於溶 Γ二Γΐΐ得螢光黃之光學特性與pH值緊密相 子可用以當作上述生物感測器之 酸驗“劑。备給定_濃度後,藉由f量 與解離常數即可得知在不同pH值下,螢光黃各解離型I 之莫爾濃度比。方程式⑺與⑻__⑼錢質量平 衡方程式及解離方程式。Ca or CB = j β dpH 1·3 FITC-Emitted fluorescence of FITC-dextran Fluorescent yellow is mainly composed of cation (FH/), neutral (FH2), monovalent 1302198 anion _ Or a dissociated form such as a dianion (F2·) is present in the optical properties of the fluorescein and the pH is closely related to the acidity of the biosensor as described above. After the concentration, the molar concentration ratio of each of the dissociated I of the fluorescent yellow is obtained by the amount of f and the dissociation constant. Equations (7) and (8)__(9) The mass balance equation and the dissociation equation.

〜ΛρΗ) = cfh + (PH) + c+ c阳(pH>c㈣ FH;- )fh2+h+ PK' = 2.08 fh2 ^FH^H+ PKa2 = 4.31 fit - + F2- + H+ 队3: = 6.43 ⑺ ⑻ (9) (10)~ΛρΗ) = cfh + (PH) + c+ c-yang (pH>c(4) FH;-)fh2+h+ PK' = 2.08 fh2 ^FH^H+ PKa2 = 4.31 fit - + F2- + H+ Team 3: = 6.43 (7) (8) (9) (10)

圖三為不同pH值下,計算所得之莫爾濃度比。由於 螢光黃具有三個_常數,是以其分佈轉遵循典型三 質子弱酸之模式。對生物感·或生醫制而言,生物 活性在低pH值(pH < 5)與高pH值(PH > 9)之環境中皆會 有所損耗,是以其pH值的範圍通常座落於5_9之間。 在此pH細巾’螢光黃主要細—價陰離子與二價陰離 子之解離型態存在於溶液中;中性型態佔不到2〇%之比 例;至於陽離子,其在pH值大於5時之效果更可被忽略。Figure 3 shows the calculated Mohr concentration ratio at different pH values. Since fluorescein yellow has three _ constants, it is a mode in which the distribution follows a typical three-proton weak acid. For biological or biomedical systems, biological activity is depleted in low pH (pH < 5) and high pH (PH > 9) environments, depending on the pH range. Located between 5_9. In this pH fine towel 'fluorescent yellow main fine-valent anion and divalent anion dissociation form is present in the solution; neutral type accounts for less than 2%%; as for the cation, when the pH is greater than 5 The effect can be ignored.

Sjoback等人在1995年確認了螢光黃的解離平衡, 並確定各解離型態的吸收性與螢光特性,使得各離型態 於不同pH值(以〜(辦)表示)下之分佈經由計算即可得 12 l3〇2i9g 知。更有甚者,在得到上述分佈之後,螢光黃於不同激 發波長、不同激光波長與不同pH值(分別以/(H,〆/) 表示)時之螢光強度,可藉由下列之方程式(11) -(15)推 演而得。 , , pH )^K{[Term FH. + Term FH 2 + Term F//. ] x Φ ^ _ (Aex )I FH-{λ em)In 1995, Sjoback et al. confirmed the dissociation equilibrium of fluorescein yellow, and determined the absorption and fluorescence characteristics of each dissociation type, so that the distribution of each dissociation state at different pH values (indicated by ~ (office)) was Calculate to get 12 l3 〇 2i9g know. What is more, after obtaining the above distribution, the fluorescence intensity of the fluorescent yellow at different excitation wavelengths, different laser wavelengths and different pH values (represented by /(H, 〆/), respectively) can be obtained by the following equation (11) - (15) derived. , , pH )^K{[Term FH. + Term FH 2 + Term F//. ] x Φ ^ _ (Aex )I FH-{λ em)

+ r^F2_x〇/2.(^)V(^)} (11) (12) (13) (14) (15)+ r^F2_x〇/2.(^)V(^)} (11) (12) (13) (14) (15)

Term : c + {ρΗ)ε + {λ )φ^ FH3 瑪 FH、 ->FH2 FH2->FH-Term : c + {ρΗ)ε + {λ )φ^ FH3 玛 FH, ->FH2 FH2->FH-

Termfh2 ·· cfh2 (pH)εfh2 rew(帅所从) τ^ηηρ2_\ 〇ρ2.{ρΗ)ερ2.{λ6Χ) 其中&為儀器參數,為了簡化計算,此參數可設為j。Termfh2 ·· cfh2 (pH)εfh2 rew (handy from) τ^ηηρ2_\ 〇ρ2.{ρΗ)ερ2.{λ6Χ) where & is the instrument parameter, in order to simplify the calculation, this parameter can be set to j.

〜(奸〇為在不同pH值下,螢光黃某一特定解離型態(X species)之濃度;心(允)及〇>((夂)各為該特定解離型態之 莫爾濃度吸收性(M'm-i)與螢光產量。气%為螢^黃 由第一種特疋解離型態(X!)轉換成第二種特定解離型 您(¾)時,產生之螢光產量;G(;L)代表對該特定型態 進仃標準化後所得之激光;至於u為激發波長 (nm) 〇 圖四顯示螢光黃之光學性質與解離常數。在pH值大 13 1302198 於f時’由於陽離子解離魏與巾轉離贿具有相當低 的莫爾濃度吸收性與幾可被忽略的莫爾濃度比,是以:其 對螢光強度之嫌忽視,而健擬—聽 险離 子解離型態的狀況。 ㈣離 為了使習知存於溶膠-凝膠包埋中之漏洩效應降至最 低’螢光黃之-衍生物’ FITc___,觀來 列型生物感測[FITC_«萄《具魏似於螢光黃之 ,學性質,這些性質包括吸收性與激發光譜,此外螢光 κ與FITC-葡萄聚醣兩者間之解離常數亦相似。基於上述 種種原因,螢光黃之光學參數被用來呈現以FITC-葡萄聚 醣為包埋材料之生物感測器系統,及其伴隨而來之模擬 過程。圖五顯示利用FITC_葡萄聚醣當作PH值探針,所 發展出之生物感測器模型的發展流程圖。藉由圖中所述 步驟,可得知包埋在溶膠-凝膠中之尿素分解酶生物感測 器、乙醯膽鹼酶生物感測器的螢光表現。 2·實驗細項 2·1氣相色層質譜儀分析(GC/MS analysis) 利用配備有 Hewlett-Packard 5973 質譜儀(GC/MSD) 之Hewlett-Packard 6890氣相色層分析儀,測定分解自乙 醯膽鹼之有機化合物。至於,所使用之管柱為含有固定相 聚本乙烯-二乙醯苯(polystyrene-divinylbenzene; 0.316 mm LD·,J & w Scientific)之 30_m GS-Q。氮氣被用以當作一 攜▼氣體’且其流速為1·3毫升/分鐘。質譜儀的注射口溫 1302198 度設為230度,四極柱之溫度則設為150度。離子化現象 係發生於離子衝擊(electron impact; EI)模式(70 eV)中。 電子倍增管電壓與增幅則以儀器的内設值為準。質譜儀的 調校是以四氟三丁基胺的電子衝擊碎片為基準,其荷質比 為69、219與502。在全區掃瞄搁取模式(f^ii scan acquisition mode)中,質譜儀的掃瞄範圍為5至500原子 質量單位。管柱溫度的梯度變化設定為在42。(:中維持4 分鐘,之後以每分鐘增加8。(:之速度,直至溫度抵達240 。(:止。系統溫度每運作一次需時約28/75分鐘。 2.2液相層析質譜儀分析及核磁共振光譜學(LC/MS analysis and NMR Spectroscopy ) 茲利用一含有真空抽氣管、P4000四溶媒梯度幫浦 (quaternary pump)、UV6000LP二極體陣列紫外線偵測 器(diode-array UV detector),以及配備有電灑式離子源 (electrospray ionization source ; ESI,FinniganMAT)與 on XCALIBUR 1.2 軟體之 Finnigan LCQDU0 四極柱離子 捕捉質譜儀(quadrupole ion trap mass spectrometer )之 TSP LC系統進行液相層析質譜實驗。電灑式離子化是設定在 正離子模式,電灑電壓為4500伏,而取得的質譜範圍則 為荷質比80至1000。在此實驗中,甲醇係被用以當作一 攜帶溶液,濃度為0.5 mM之BTP (荷質比為283.3)溶液 則被用來當作定量之内標準品。1Η與13C的核磁共振光 譜則是由VarianUnity Inova500-MHz光譜儀所測定,並 15 ⑧ 利用四曱基石夕燒作為内標準。 3·結果與討論 3·1 pH測定 。。在沒有酵素存在之狀況下,包埋有_之生物感測 益可用以制pH值變化。而由於酵素並不存在於此類系 統中’是以這類系統為測定pH值變化之化學感測器。圖 六顯示得自感測器陣列之實驗輯(空心方塊)以及在 不同pH值下計算所得之螢光強度(曲線)。由圖中可知, 當PH值向上料時’魏紐辑著增加;當pH值抵 達8.5 ’螢光強度之增加幅度才趨於平緩。模型模擬的結 果相當符合於實際結果’齡藉由前述理論推演出之榮 光強度’相當適合用來描述感測H陣列的行為。模型模 擬其中的-個優點為可分辨出各解離型態對pH值之貢 獻度’以及發生於系射之可能機制。圖七顯示在不同 pH值下’螢光黃各解離型態對螢光強度之貢獻。結果顯 示於pH值細為3至6時’―價陰離子解義態為榮光 強度之主要貢獻者;而當pH值範圍為6至9時,榮光強 度主要係為二舰鮮解__掌控。這些結果亦證 明劎述「刼離子解離型態與中性解離型態對螢光龙磬 激發之貢獻度,微乎其微」〇 汽愛光 3.2敏感度分析 由於上述麵可被制在不财度之各式緩衝系統 1302198 中,是以可簡化-般在錄躺n研發饮長而繁項的 最佳化(optimization)程序。圖八顯示尿素分解酵素型 之生物感測為的模擬結果,其中尿素分解反應係於不同 pH值之BTP缓衝溶液(濃度為imM)中進行,結果顯 示系統的初始pH值對分析結果具有很大的影響,亦即當 初始pH值較低時,可得到較大的動態範圍(dynaiJc range)與較南的敏感度。圖九顯示尿素分解酵素型之生 物感測器的模擬結果,其中尿素分解反應係於不同濃度 之BTP緩衝溶液(選定的pH值為6 〇)中進行,結果顯 示所選用緩衝溶液的濃度並不會影響動態範圍,^而其 對系統敏感度卻具有明顯的影響。當所選用的緩衝溶液 濃度較低時,紐舰力也較低,而使得纟⑽測之敏 感度增加。Waicerz等人在1995年亦在電化學型生物感 測器上得到類似的結果,在利用pH膜電極尿素分解之 生物感測器(pH membrane electrode-based u_e biosensor)測定尿素時,系統中緩衝溶液pH值與濃度的 降低,會導致敏感度的增加。更有甚者,即使緩衝溶液 pH值的降低會增加系統的動態範圍,緩衝溶液的值 仍對尿素偵測之動態範圍具有絕大影響。 上述模型除了可應用於BTP緩衝溶液系統中,本發 明亦調查其於其他緩衝溶液系統中之適用性,這些緩衝 溶液系統包括三羥甲基氨基甲烷-氯化氫 【tris(hydromethyl)-aminomethane-HCl ;以下稱 •s HC1 】、2- ( N-嗎林)乙基硫酸【2-〇sj_morph〇lin〇) 17 1302198 ethanesulfonic acid ;以下稱 MES】、味唾【imidazole】、 N-(2-羥乙基)哌嗪-N’-(4_ 丁烧硫酸) 【 N-(2-hydroxyethyl)piperazine-N’-(4-butanesulfonic acid);以下稱HEPES】與麟酸鹽等缓衝系統,圖十中並 列舉這些緩衝溶液之解離常數與pH範圍。圖十一 A至E 顯示尿素分解酵素型之生物感測器的模擬結果,其中尿 素分解反應係於不同的緩衝溶液系統中進行。在進行模 擬時,緩衝溶液之濃度為1〇〇 mM,pH值為5至10,尿 素濃度則在0至100 mM之間。結果顯示MES、咪唑與 磷酸鹽緩衝溶液之3D分佈近似於BTP緩衝溶液之3D分 佈’ Tris-HCl與HEPES之分佈則與上述緩衝溶液相異。 3.3尿素測定 在尿素分解催化之尿素水解反應中,根據化學計 篁關係,可得知1莫爾的尿素可產生i莫爾的碳酸氫離 子、氫氧根離子,以及2莫爾的胺鹽離子,其中氫氧根 離子會使溶膠-凝膠的pH值增加。碳酸氫離子與胺鹽離 子則為構成溶液總緩衝能力之主要份子,並可抵抗pH值 的上升。當上述反應式到達化學平衡狀態,可藉由包埋 在溶膠-凝膠中之FITC_葡萄聚醣辨認系統的最終pH 值,並以螢光強度呈現之。至於,在溶膠—凝膠基質中可 ^存在一些未膠化的氫氧基㊈si_〇H,ξ代表與別相鍵 、、ϋ)此氣氧基可忐影響溶液的總缓衝能力,是以本發明 (surface deprotonation~ (Secret is the concentration of a specific dissociation type (X species) of fluorescein at different pH values; heart (allow) and 〇> ((夂) each is the Mohr concentration of the specific dissociation type Absorbance (M'm-i) and fluorescence yield. The gas percentage is the firefly produced by the first special dissociation type (X!) converted to the second specific dissociation type (3⁄4). Light yield; G(;L) represents the laser obtained after normalization of the specific pattern; as for u, the excitation wavelength (nm) 〇 Figure 4 shows the optical properties and dissociation constant of the fluorescent yellow. At a pH of 13 1302198 At f, 'there is a relatively low molar concentration absorption and a negligible Mohr concentration ratio due to the cation dissociation between Wei and the towel. It is: the neglect of the fluorescence intensity, and the health-listening The condition of the dissociative ion dissociation type. (4) To minimize the leakage effect of the conventional sol-gel embedding 'fluorescent yellow-derivative' FITc___, observation of the type of biological sensing [FITC_« "There is a similarity to the fluorescence of yellow, the nature of the study, these properties include absorption and excitation spectra, in addition to fluorescent κ and FITC-glucan The dissociation constants are similar. For these various reasons, the optical parameters of Fluorescent Yellow are used to present biosensor systems with FITC-Glucan as the embedding material, and the accompanying simulation process. A flow chart showing the development of a biosensor model developed using FITC_glucan as a pH probe. The decomposition of urea embedded in a sol-gel can be obtained by the steps described in the figure. Fluorescence performance of enzyme biosensor, acetylcholine biosensor. 2. Experimental details 2. 1 GC/MS analysis using a Hewlett-Packard 5973 mass spectrometer (GC/MSD) Hewlett-Packard 6890 Gas Chromatography Analyzer for the determination of organic compounds decomposed from acetylcholine. As a result, the column used contains a stationary phase of polystyrene-divinylbenzene. 0.316 mm LD·, J & w Scientific) 30_m GS-Q. Nitrogen is used as a gas with a flow rate of 13.3 ml/min. The injection port temperature of the mass spectrometer is set to 1302198 degrees. 230 degrees, the temperature of the quadrupole is set to 150 degrees. The phenomenon occurs in the ion impact (EI) mode (70 eV). The voltage and amplification of the electron multiplier tube are based on the built-in value of the instrument. The mass spectrometer is calibrated with electrons of tetrafluorotributylamine. The impact debris is the reference, and the charge-to-mass ratio is 69, 219, and 502. In the full scan scan mode (f^ii scan acquisition mode), the mass spectrometer scans from 5 to 500 atomic mass units. The gradient change of the column temperature is set at 42. (: Maintain for 4 minutes, then increase by 8 per minute. (: The speed until the temperature reaches 240. (: Stop. The system temperature takes about 28/75 minutes per operation. 2.2 Liquid Chromatography Mass Spectrometer Analysis and LC/MS analysis and NMR Spectroscopy uses a vacuum pumping tube, a P4000 quadruple grading pump, a UV6000LP diode-array UV detector, and Liquid chromatography mass spectrometry experiments were performed with a TSP LC system equipped with an electrospray ionization source (ESI, Finnigan MAT) and a Finnigan LCQDU0 quadrupole ion trap mass spectrometer on XCALIBUR 1.2 software. The sputter ionization is set in positive ion mode, the electrospray voltage is 4500 volts, and the mass spectrum obtained is the charge to mass ratio of 80 to 1000. In this experiment, methanol is used as a carrier solution at a concentration of A 0.5 mM BTP (loading ratio of 283.3) solution was used as a standard within the quantification. The 1 Η and 13 C NMR spectra were obtained from Varian Unity Inova 500-MHz. Spectrometer measured, and 15 8 using the four-base stone as the internal standard. 3. Results and discussion 3.1 pH determination. In the absence of enzymes, the biological sensory benefits embedded in the system can be used to make pH changes, and because enzymes are not present in such systems' are chemical sensors that measure pH changes in this type of system. Figure 6 shows the experimental series (open squares) from the sensor array and The calculated fluorescence intensity (curve) at different pH values. It can be seen from the figure that when the pH value is upward, the 'Wei New series increases; when the pH reaches 8.5', the increase of the fluorescence intensity tends to be gentle. The results of the simulation are quite consistent with the actual results 'the glory intensity derived from the aforementioned theory' is quite suitable for describing the behavior of the sensing H array. The advantage of the model simulation is that the dissociation patterns can be distinguished from the pH value. The contribution 'and the possible mechanism of the ray-forming. Figure 7 shows the contribution of the respective dissociation patterns of fluorescein to the fluorescence intensity at different pH values. The results show that the pH is between 3 and 6 Anion solution is proud The main contributor to the intensity; and when the pH range is 6 to 9, the glory intensity is mainly controlled by the second ship. The results also prove that the 刼 ion dissociation type and the neutral dissociation type The contribution of the light dragon 磬 磬 , 〇 〇 〇 〇 3.2 3.2 3.2 3.2 3.2 3.2 3.2 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感 敏感The optimization program of the item. Figure 8 shows the simulation results of the biosensing of the urea-decomposing enzyme type, in which the urea decomposition reaction is carried out in a BTP buffer solution (concentration of imM) of different pH values, and the results show that the initial pH value of the system has a very good analysis result. The large effect, that is, when the initial pH is low, a larger dynamic range (dynaiJc range) and a more southerly sensitivity are obtained. Figure 9 shows the simulation results of a urea-decomposing enzyme type biosensor, in which the urea decomposition reaction is carried out in different concentrations of BTP buffer solution (selected pH value of 6 〇), and the results show that the concentration of the selected buffer solution is not Will affect the dynamic range, and it has a significant impact on system sensitivity. When the concentration of the selected buffer solution is low, the force of the new ship is also low, and the sensitivity of the 纟(10) measurement is increased. Waicerz et al. also obtained similar results on electrochemical biosensors in 1995. Buffer solutions in the system when urea was measured using a pH membrane electrode-based u_e biosensor. A decrease in pH and concentration results in an increase in sensitivity. What's more, even if the pH of the buffer solution decreases, the dynamic range of the system increases, and the value of the buffer solution has a great influence on the dynamic range of urea detection. In addition to the above model applicable to BTP buffer solution systems, the present invention also investigates its suitability for use in other buffer solution systems including tris(hydromethyl)-aminomethane-HCl; Hereinafter, •s HC1], 2-(N-morphin)ethylsulfate [2-〇sj_morph〇lin〇) 17 1302198 ethanesulfonic acid; hereinafter referred to as MES], sputum [imidazole], N-(2-hydroxy-B Piperazine-N'-(4-butanesulfonic acid) [N-(2-hydroxyethyl)piperazine-N'-(4-butanesulfonic acid); hereinafter referred to as HEPES] and buffering system such as linoleic acid, Figure 10 The dissociation constants and pH ranges of these buffer solutions are also listed. Figure 11A to E show the simulation results of a urea-decomposing enzyme type biosensor in which the urea decomposition reaction is carried out in different buffer solution systems. At the time of the simulation, the concentration of the buffer solution was 1 mM, the pH was 5 to 10, and the urinary concentration was between 0 and 100 mM. The results show that the 3D distribution of MES, imidazole and phosphate buffer solution is similar to the 3D distribution of BTP buffer solution. The distribution of Tris-HCl and HEPES is different from the above buffer solution. 3.3 Urea determination In the urea hydrolysis reaction of urea decomposition catalysis, according to the stoichiometric relationship, it can be known that 1 mole of urea can produce iMo's bicarbonate ions, hydroxide ions, and 2 moir amine salt ions. Where the hydroxide ion increases the pH of the sol-gel. The hydrogen carbonate ion and the amine salt ion are the main components of the total buffering capacity of the solution and are resistant to an increase in pH. When the above reaction formula reaches a chemical equilibrium state, the final pH of the system can be recognized by the FITC_glucan embedded in the sol-gel and expressed as fluorescence intensity. As for the sol-gel matrix, there may be some ungelatinized hydroxyl group IX si_〇H, ξ represents a bond with the other phase, ϋ) This oxy group can affect the total buffering capacity of the solution, With the invention (surface deprotonation

18 1302198 constant of silica ; (pKas= 6·8)14)。 圖十二顯示利用模型運算而得之螢光強度結果(實 線),與利用生物感測器偵測而得之實驗結果(空心圓), 其中尿素濃度為1 μΜ至1Μ,反應時間則為1〇分鐘。由 圖可知,模擬結果與實驗結果相符,而只在低濃度區域 存有稍微之差異,顯示本發明所揭露之模型適用於預測 利用FITC-葡萄聚醣偵測ΡΗ值變化之生物感測器行為。 3.4肌酐酸測定 與上述反應系統相似,肌酐酸被肌酐酸去乙醯水 解之後,會產生胺鹽離子與氫氧根離子。然而,由於肌 酐酸具有與受測pH值範圍相近(PH 5 - 1〇)之的一解離 常數(值為4.83),是以亦應考慮其於緩衝能力上之影 響。圖十三顯示利用模型運算而得之螢光強度結果(實 線)’與利用生物感測器债測而得之實驗結果(空心圓), 其中尿素濃度為1 μΜ至1M,反應時間則為1〇分鐘。由 圖可知,模擬結果與實驗結果間具有相當大的差異,於 疋推測可能的原因有二,—是所使用之解離常數不正確 或是系統尚未到達平衡。由於肌酐酸與]^_甲基乙内酰脲 _methylhydant〇in)之解離常數係藉由前述軟體預測而 得,是以其正確性需進一步確認。在進入資料庫 (ACD/pKa DB v7.〇25 Advance Chemistry Development, Inc·,Canada)進行調查之後,發現肌酐酸與N_甲基乙内酰 脲之解離常數分顺楊(Failey,C F ; B_,E^舰 1302198 1933, 102, 767)與 9.09 (Campi,E ; 〇stac〇H,G;18 1302198 constant of silica ; (pKas= 6·8) 14). Figure 12 shows the results of the fluorescence intensity obtained by the model calculation (solid line) and the experimental results (open circles) detected by the biosensor, wherein the urea concentration is 1 μΜ to 1Μ, and the reaction time is 1 minute. As can be seen from the figure, the simulation results are in agreement with the experimental results, and there is only a slight difference in the low concentration region, indicating that the model disclosed in the present invention is suitable for predicting biosensor behaviors using FITC-glucan to detect valence changes. . 3.4 Determination of creatinine acid Similar to the above reaction system, creatinine acid is hydrolyzed by creatinine dehydroacetate to produce amine salt ions and hydroxide ions. However, since creatinine has a dissociation constant (value of 4.83) which is close to the measured pH range (pH 5 - 1 〇), it is also considered to have an effect on the buffering capacity. Figure 13 shows the results of the fluorescence intensity obtained by the model calculation (solid line) and the experimental results obtained by using the biosensor's debt (open circles), wherein the urea concentration is 1 μΜ to 1 M, and the reaction time is 1 minute. As can be seen from the figure, there is a considerable difference between the simulation results and the experimental results. There are two possible reasons for the speculation, that is, the dissociation constant used is not correct or the system has not reached equilibrium. Since the dissociation constant of creatinine and _methylhydantoin _methylhydant 〇in) is predicted by the aforementioned software, its correctness needs to be further confirmed. After investigation into the database (ACD/pKa DB v7.〇25 Advance Chemistry Development, Inc., Canada), it was found that the dissociation constant of creatinine and N-methylhydantoin was divided into shun Yang (Failey, CF; B_). , E^ ship 1302198 1933, 102, 767) and 9.09 (Campi, E; 〇stac〇H, G;

Vanni,A. Gazz· C7w.m.侃 1965, 95, 796)。由於上述這歧 解離常數與模型模擬時所使用之解離常數相近,是以^ 擬值與實際值之間的差異可能不是導因於解離常數不正 確。 上述包埋酵素的溶膠-凝膠技術,可能會延遲分析物 或產物於多孔結構中之擴散作用,且發生由溶劑(如甲 醇)釋放或丨谷膠政膠老化所引起之酵素活性降低,是以 在溶膠_凝膠系統中觀察到的酵素反應速率較水溶液中所 觀察到的要來的慢。和尿素分解與乙醯膽鹼酯的反 應速率(分別為3545 S·1與6807 S·1)相比,由於肌酐酸 去乙醯具有較低的反應速率(668 s·1),因此肌酐酸在 水解時,反應系統可能尚未達到平衡。為了證明這個推 測,將較高濃度之肌酐酸去乙醯(丨u/mL)配製於pH 為6.0、濃度為1 mM之Βτρ緩衝溶液中,以催化不同濃 度(0.02至20 mM)之肌酐酸的分解,其間並利用一 pH 電極監控pH值的變化。此方法係直接紀錄系統pH值的 變化’是以自pH值經由FITC-葡萄聚醣傳遞至螢光強度 之訊息誤差可減到最小。圖十四為肌酐酸水解系統中溶 液pH值的變化’結果顯示當肌酐酸被加入反應管中,溶 液pH值會逐漸上升。然而,在1〇分鐘的時候,有些反 應尚未到達平衡,尤其是在較高濃度的肌酐酸(1 and20 mM)系統中。由圖十三所示pH值與螢光強度的關係, 可知在利用肌酐酸去乙醯分解肌酐酸的系統中,於10 1302198 分鐘時所記錄到之pH值可轉化為螢光強度。請參照圖十 五,模擬結果(solidline)與實驗結果(實心方塊)具有 尚度一致性,意味著前述模擬結果與實驗結果間之差異 係導因於系統反應尚未達到平衡。有鑑於此,茲將肌酐 酸去乙酿型之生物感測器的反應時間校正為3〇分鐘, 並將結果繪製成圖十五中之空心圓。如圖所示,上述結 果與模擬值具有南度一致性,顯示肌酐酸系統達到平衡 所需的時間較長。 3.5乙醯膽驗測定 虱化乙醯膽驗為可快速吸收空氣中之水分,並需儲 存在-20°C環境中之一高度吸濕化合物,是以儲備溶液中 乙醯膽驗的濃度係為一近估值,且其通常比期望值略 低。這種本質上的限制,無法僅藉由校正曲線即表現出 來;爰且’當氯化乙醯膽鹼被應用於乙醯膽鹼測定時, 此種限制並不被考慮進生物感測器中。不同於上述,本 發明係將濃度的準確理論值輸入模型中進行模擬,是以 可用來闡明此限制。 如同尿素分解與肌酐酸去乙醯系統,可利用類 似的方法計算乙醯膽鹼酯型之生物感測器的強度,其 中乙醯膽鹼之濃度為1 μΜ至1 M。乙醯膽鹼被分解後會 產生質子,因此當乙醯膽鹼濃度增加時,FT值會下降, 而形成如圖十六所示之反S型曲線(inversed sigmoidal curve)。請參照圖十六,顯示利用生物感測器偵測之反應 21 1302198 曲線(空心圓),與利用模型運算而得而得之實驗結果(虛 線)。其中,在進行模型模擬時,初始pH值為8·5之乙 醯膽鹼係100%被應用於模型中。由圖可知,當乙醯膽鹼 之濃度為0.9 - 4 mM時,模擬值與實驗結果高度相符, 然而當乙醯膽驗濃度落在此範圍之外時,模擬值與實驗 結果間具有明顯差異。此種現象可能導因於勒夜阳值的 降低與乙醯膽驗的濃度。熟悉該行業者皆知,當1〇〇mM 的乙醯膽鹼被配製於濃度為10 mM、pH為8 〇的Tris-HC1 缓衝溶液中,10小時後pH值會下降一個單位。圖十七 顯示隨著時間增長,溶液中pH值的變化,其中5〇 mM 之乙醯膽驗係被配製於濃度為丨mM、pH為8·5的Βτρ 緩衝/谷液(此係為利用生物感測器測定乙醯膽鹼之儲備 溶液)中。如圖所示,1分鐘之内,pH值明顯地由8·5 下降至7·6,之後pH值並繼續緩慢地掉落至I] ( 1⑻分 鐘時)。這些結果表明生物感測器之初始ρΗ值與模型模 擬所使用之初始pH值相異。由於本發明中所使用之乙釀 膽鹼溶液係為新鮮配製,並在10至20分鐘内使用,是 以挑選初始pH值7·5為後續模型模擬之初始pH值。 實驗結果與模擬制之另—個差異處(發生於高濃 度之乙醯膽驗),可能導因於乙醯膽驗濃度的改變。如前 所述’氯化乙_驗為—具有高度吸雕的化合物,其 可在製備過程巾快速吸收空氣巾的水分。在此前提之 下,配製出之乙醯膽驗濃度實際上係低於膽值;,導 致差異處的另一個可能性為乙醯膽鹼的自動分解,值得 22 的是’由模擬結果知道此分解並不會對PH值造成改 變。由於乙醯膽鹼的自動分解過程仍為未知,是以藉由 將pH值為7.5時之模擬值與實驗結果相比,而得到乙醯 膽驗氣度之降低率。請參關十八,當乙醢膽驗實際濃 度為期望濃度之7G%時,模擬曲線(實線)與實驗結果 (:心圓)間呈尚度符合。這些結果顯示,本發明中所 揭路之模型不僅能釐清習知生物感測器系統中不加以考 慮之向度吸濕性化合物本質上的限制(如初始pH值變異 或重置改變),並為此種限制對生物感測器所造成之影響 提供一闡釋。 本發明雖以較佳實施例闡明如上,然其它未脫離本 發明所揭示精神下所完成之等效變換或修飾者,均應視 為本發明之保護範疇。本發明之專利保護範圍更當視後 附之申請專利範圍、圖式及其等同領域而定。 【圖式簡單說明】 藉由以下詳細之描述結合所附圖示,將可輕易的了解 上述内容及此項發明之諸多優點,其中: 圖一顯示水、BTP緩衝溶液,以及反應式(A)、(B) 及(C)中各反應物/產物之解離常數。 圖二A顯示濃度為1 mM之BTP緩衝溶液,其於不 1302198 同pH值、不同尿素濃度下之緩衝強度3d圖。 圖二B顯示濃度為1 mM之BTP緩衝溶液,其於不 同pH值、不同肌酐酸濃度下之緩衝強度3D圖。 圖一 C顯不濃度為1 mM之BTP緩衝溶液,其於不 同pH值、不同乙醯膽鹼濃度下之缓衝強度3D圖。 圖三顯示不同pH值下計算所得之莫爾濃度比。 圖四顯示螢光黃之光學性質與解離常數。 圖五顯示利用FITC-葡萄聚醣當作pH值探針,所發 展出之生物感測器模型的發展流程圖。 圖六顯示得自感測器陣列之實驗數據(空心方塊)以 及在不同pH值下計算所得之螢光強度(曲線)。 圖七顯示在不同pH值下,螢光黃各解離型態對螢光 強度之貢獻。 圖八顯示尿素分解酵素型之生物感測器的模擬結 果,其中尿素分解反應係於不同pH值之BTP缓衝溶液(濃 度為1 mM)中進行。 ®九顯示尿素分解酵素型之生物感測器的模擬結 果’其中尿素分解反應係於不同濃度之BTP緩衝溶液(選 定的pH值為6·〇)中進行。 圖十顯示Tris-HCl、MES、咪唑、HEPES、ΒΤΡ與磷 酸鹽等緩衝系統之解離常數與pH範圍。 圖十一 A顯示尿素分解酵素型之生物感測器的模擬 結果,其中尿素分解反應係於Tris-HCl缓衝溶液系統中進 行0 (s 1302198 圖十一 β顯示尿素分解酵素型之生物感測器的模擬 結果’其中尿素分解反應係於MES緩衝溶液系統中進行。 圖十一 C顯示尿素分解酵素型之生物感測器的模擬 、、、口果,其中尿素分解反應係於咪唑緩衝溶液系統中進行。 士圖十一 D顯示尿素分解酵素型之生物感測器的模擬 結果,其巾尿素分解反·於HEPES緩衝溶_統中進 行。 圖十一Ε顯示尿素分解酵素型之生物感測器的模擬結 果,其中尿素分解反應係於磷酸鹽緩衝溶液系統中進行。 圖十二顯示利用模型運算而得之勞光強度結果(實 線)’與利用生物感測器偵測而得之實驗結果(空心圓), 其中尿素濃度為ΙμΜ至1Μ,反應時間縣1G分鐘。 圖十三顯示利用模型運算而得之營光強度結果(實 線),與利用生物感測器偵測而得之實驗結果^心圓), 其中尿素濃度為1 μΜ至1M,反應時間則為1()分鐘。 圖十四為肌酐酸水解系統中溶液pH值的變化,顯示 當肌酐酸被加入反應管中,溶液^^值會逐漸上升。 圖十五顯示模擬結果(_ line)與實驗結果(實心 方塊)具有尚度_雜’意味著前频擬結果與實驗結果 間之差異係導因於系統反應尚未達到平衡。 圖十六顯示當乙醯膽驗濃度增加時FT值會下降之 S塑曲線。 曰 圖十七顯示隨著時間增長,溶液中pH值的變化,其 中50 mM之乙醯膽驗係被配製於濃度為1 _、阳為μ 25 1302198 的BTP緩衝溶液中。 圖十八顯示當乙醯膽鹼實際濃度為期望濃度之70% 時,模擬曲線(實線)與實驗結果(空心圓)間呈高度符 合0Vanni, A. Gazz·C7w.m.侃 1965, 95, 796). Since the above dissociation constant is similar to the dissociation constant used in the model simulation, the difference between the pseudo value and the actual value may not be due to the fact that the dissociation constant is not correct. The sol-gel technique of embedding the above enzyme may delay the diffusion of the analyte or product in the porous structure, and the activity of the enzyme caused by the release of the solvent (such as methanol) or the aging of the glutinous gum may be reduced. The rate of enzyme reaction observed in the sol-gel system is slower than that observed in aqueous solutions. Compared with the reaction rate of urea decomposition and acetylcholine ester (3545 S·1 and 6807 S·1, respectively), creatinine acid has a lower reaction rate (668 s·1) due to creatinine acid deacetylation. Upon hydrolysis, the reaction system may not have reached equilibrium. In order to prove this hypothesis, a higher concentration of creatinine deacetylate (丨u/mL) was prepared in a pH of 6.0, 1 mM Βτρ buffer solution to catalyze different concentrations (0.02 to 20 mM) of creatinine The decomposition, during which a pH electrode is used to monitor the change in pH. This method directly records the change in pH of the system'. The error in the signal delivered from the pH to the fluorescence intensity via FITC-glucomann is minimized. Figure 14 shows the change in pH of the solution in the creatinine acid hydrolysis system. The results show that when creatinine is added to the reaction tube, the pH of the solution gradually increases. However, at 1 minute, some reactions have not reached equilibrium, especially in the higher concentrations of creatinine (1 and 20 mM) systems. From the relationship between the pH value and the fluorescence intensity shown in Fig. 13, it can be seen that in the system for decomposing creatinine using creatinine to deacetylate, the pH recorded at 10 1302198 minutes can be converted into fluorescence intensity. Referring to Figure 15, the simulation results (solidline) and the experimental results (solid squares) are consistent, meaning that the difference between the above simulation results and the experimental results is due to the system reaction has not yet reached equilibrium. In view of this, the reaction time of the creatinine-depleted biosensor was corrected to 3 〇 minutes, and the result was plotted as a hollow circle in Fig. 15. As shown, the above results are consistent with the analog values, indicating that the creatinine system takes longer to reach equilibrium. 3.5 醯 醯 验 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱 虱It is a near-valued estimate and it is usually slightly lower than expected. This intrinsic limitation cannot be manifested only by the calibration curve; and 'when acetylcholine is used in the determination of acetylcholine, this limitation is not considered in biosensors. . Unlike the above, the present invention simulates the theoretical value of the concentration input into the model, which can be used to clarify this limitation. Like the urea decomposition and creatinine deacetylation system, a similar method can be used to calculate the strength of the acetylcholine type biosensor, where the concentration of acetylcholine is 1 μΜ to 1 M. When acetylcholine is decomposed, protons are generated. Therefore, when the concentration of acetylcholine increases, the FT value decreases, and an inverted sigmoidal curve as shown in Fig. 16 is formed. Please refer to Figure 16 for the reaction 21 21 2198 curve (open circle) detected by the biosensor and the experimental result (dummy line) obtained by using the model calculation. Among them, in the model simulation, 100% of the acetylcholine system with an initial pH of 8.5 was applied to the model. As can be seen from the figure, when the concentration of acetylcholine is 0.9 - 4 mM, the simulated value is highly consistent with the experimental results. However, when the concentration of acetaminophen falls outside this range, there is a significant difference between the simulated value and the experimental results. . This phenomenon may be caused by a decrease in the positive value of the night and the concentration of the test. It is well known in the art that when 1 mM of acetylcholine is formulated in a Tris-HC1 buffer solution having a concentration of 10 mM and a pH of 8 Torr, the pH will drop by one unit after 10 hours. Figure 17 shows the change in pH in the solution over time. The 5 mM acetaminophen system was prepared at 浓度τρ buffer/glutle solution at a concentration of 丨 mM and pH 8.5 (this is the use The biosensor measures the stock solution of acetylcholine. As shown, within 1 minute, the pH dropped significantly from 8.5 to 7.6, after which the pH value continued to drop slowly to I] (1 (8) minutes). These results indicate that the initial pH value of the biosensor is different from the initial pH used for model simulation. Since the choline solution used in the present invention is freshly prepared and used within 10 to 20 minutes, the initial pH value of 7.5 is selected as the initial pH value for subsequent model simulation. Another difference between the experimental results and the simulated system (which occurs at a high concentration of the sputum test) may be due to changes in the concentration of the acetaminophen. As previously described, 'chlorinated B' is a highly absorbing compound that rapidly absorbs the moisture of the air towel during the preparation of the process towel. Under this premise, the concentration of the prepared sputum test is actually lower than the biliary value; another possibility that causes the difference is the automatic decomposition of acetylcholine, which is worth 22's. Decomposition does not change the pH. Since the automatic decomposition process of acetylcholine is still unknown, the reduction rate of acetammetry is obtained by comparing the simulated value at pH 7.5 with the experimental results. Please refer to the 18th. When the actual concentration of B is the 7G% of the expected concentration, the simulated curve (solid line) and the experimental result (: heart circle) are in good agreement. These results show that the model disclosed in the present invention not only clarifies the inherent limitations of the directional hygroscopic compounds (such as initial pH variation or reset change) that are not considered in conventional biosensor systems, and This limitation provides an explanation of the effects of biosensors. The present invention has been described above with reference to the preferred embodiments thereof, and other equivalent modifications and modifications may be made without departing from the spirit and scope of the invention. The scope of patent protection of the present invention is to be determined by the scope of the claims, the drawings and the equivalents thereof. BRIEF DESCRIPTION OF THE DRAWINGS The above and other advantages of the invention will be readily understood by the following detailed description in conjunction with the accompanying drawings in which: Figure 1 shows water, BTP buffer solution, and reaction formula (A) The dissociation constants of the reactants/products in (B) and (C). Figure 2A shows the BTP buffer solution at a concentration of 1 mM, which is 3d in the buffer strength at 1302198 with the same pH and different urea concentrations. Figure 2B shows the BTP buffer solution at a concentration of 1 mM, which is a 3D plot of buffer strength at different pH values and different creatinine acid concentrations. Figure 1 shows the CTP buffer solution with a concentration of 1 mM, which is a 3D plot of buffer strength at different pH values and different concentrations of acetylcholine. Figure 3 shows the calculated Mohr concentration ratio at different pH values. Figure 4 shows the optical properties and dissociation constants of fluorescent yellow. Figure 5 shows a development flow chart of the biosensor model developed using FITC-glucan as a pH probe. Figure 6 shows the experimental data (open squares) from the sensor array and the calculated fluorescence intensity (curve) at different pH values. Figure 7 shows the contribution of the respective dissociation states of fluorescein to fluorescence intensity at different pH values. Figure 8 shows the results of a biosensor of a urea-decomposing enzyme type in which the urea decomposition reaction is carried out in a BTP buffer solution (concentration: 1 mM) of different pH values. ®9 shows the simulated results of a biosensor of a urea-decomposing enzyme type' wherein the urea decomposition reaction is carried out in different concentrations of BTP buffer solution (selected pH value of 〇). Figure 10 shows the dissociation constants and pH ranges of buffer systems such as Tris-HCl, MES, imidazole, HEPES, hydrazine and phosphate. Figure 11A shows the simulation results of a urea-decomposing enzyme type biosensor, in which the urea decomposition reaction is carried out in a Tris-HCl buffer solution system for 0 (s 1302198. Figure 11 shows the urea-decomposing enzyme type biosensing The simulation result of the device 'where the urea decomposition reaction is carried out in the MES buffer solution system. Fig. 11C shows the simulation, and the fruit of the urea decomposing enzyme type biosensor, wherein the urea decomposition reaction is in the imidazole buffer solution system. The simulation results of the biosensor of the urea-decomposing enzyme type are shown in Fig. 11D, and the urea decomposition of the towel is carried out in the HEPES buffer solution. Figure 11 shows the biosensor of the urea decomposition enzyme type. The simulation results of the reactor, in which the urea decomposition reaction is carried out in a phosphate buffer solution system. Figure 12 shows the results of the work intensity (solid line) obtained by using the model calculation and the experiment using the biosensor detection. Results (open circles), wherein the urea concentration is ΙμΜ to 1Μ, and the reaction time is 1G minutes. Figure 13 shows the results of the camp light intensity obtained by the model calculation ( Line), and using the detection results obtained by the biosensor ^ concentric circles), where the urea concentration of 1 μΜ to 1M, the reaction time was 1 () min. Figure 14 shows the change in pH of the solution in the creatinine acid hydrolysis system. It shows that when creatinine is added to the reaction tube, the solution value will gradually increase. Figure 15 shows that the simulation results (_ line) and the experimental results (solid squares) have a degree of _hetery, which means that the difference between the pre-frequency quasi-results and the experimental results is due to the fact that the system response has not yet reached equilibrium. Figure 16 shows the S-plastic curve at which the FT value decreases as the concentration of the acetaminophen increases.曰 Figure 17 shows the change in pH in the solution over time. The 50 mM acetaminophen system was prepared in a BTP buffer solution with a concentration of 1 _ and a cation of μ 25 1302198. Figure 18 shows that when the actual concentration of acetylcholine is 70% of the desired concentration, the simulation curve (solid line) and the experimental result (open circle) are highly consistent.

Claims (1)

1302198 h 、申請專利範圍 ^種簡化化學感測器系統研發過”最佳 中該化學感測器系統具有至少 有影響推物她斷_度具 物潭強度模式計算該緩衝強度,並在不同反岸 物展度與不同ρΗ值之複數 〜认應 之分佈;以及 致、、且σ下,侍知该緩衝能力 在該化學感測器系統到達平 分,以得知該化學感測器系統之最^ρΗ值歲衝此力進行積 2. 如申睛專利範圍第丨項之 包含-偵測探針。 ,去’其中該化學感測器系統更 3. 如申請專利範圍第2項之 染劑。 ,其中該偵測探針為一螢光 4. 如申請專利範圍第3項之 (fluorescein) 〇 ,,其中該螢光染劑為螢光黃 5‘如申請專利範圍第3項之 萄聚醣。 '’ /、中該螢光染劑為FITC-葡 6.如申請專利範圍第2項之方 偵測探針的分佈。 决,更包含計算不同型態之該 1302198 7. 如申請專繼圍第2奴方法,更包含計算軸測探針之 表現強度。 8. 如申請補關第2奴方法,更包含得出德不同反應 物濃度時,該彳貞測探針之該表現強度。 9. -種簡化生物感測m統研^過程中最佳化程序 (_miZatiGn)之方法,其中該生物感測器系統呈有至少一1302198 h, the scope of patent application ^ Simplified chemical sensor system developed "Best in the chemical sensor system has at least have an impact on the pusher her break _ degree with the intensity of the pool to calculate the buffer strength, and in different counter The distribution of the shore material and the complex value of the different values of ρ 〜 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 认 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍 侍^ρΗ值? This force is accumulated. 2. For example, the scope of the patent scope is included - the detection probe. Go to 'where the chemical sensor system is more 3. For example, the dye of the second paragraph of the patent application scope The detection probe is a fluorescent light. 4. According to the fluorescein 〇 of the third application, wherein the fluorescent dye is fluorescent yellow 5', as in the third application of the patent scope. Sugar. '' /, the fluorescent dye is FITC-Port 6. The distribution of the detection probe is as in the second paragraph of the patent application. The determination includes the calculation of the different types of the 1302198. Following the second slave method, it also includes calculating the performance of the axonometric probe. Intensity 8. If the method of applying for the second slave is applied, it also includes the intensity of the performance of the probe when the concentration of different reactants is obtained. 9. - Simplified biological sensing a method of optimizing a program (_miZatiGn), wherein the biosensor system has at least one 缓衝溶液、至少-反應物與至少—酵素㈤制題,、是否要限 用一種),且該生物感測器係以爾化為偵測基準,該方法 推估該生物感測器系統中對該緩衝溶液之緩衝強度呈 有影響能力之所有組成份,苴中 及 /、 應物與該酵素之相互反應;巾‘賴成物錄自於該反 =祕_齡料轉該_強度,並林同反應 ^辰度财同pH值之複數種參數缸, 之分佈 、口Buffer solution, at least - reactant and at least - enzyme (5), whether to limit one), and the biosensor is based on the detection benchmark, the method is estimated in the biosensor system All components which have an influencing ability to the buffering strength of the buffer solution, and the interaction between the sputum and/or the substance and the enzyme; the towel's product is recorded from the reverse _ age _ age material to the _ intensity, And the same kind of parameter cylinder, the distribution and mouth of the same reaction 得知該緩衝能力 以及 分,緩衝能力進行積 其中該pH值係設定在5至 其中該反應物濃度係設定 其中該反應物為尿素時, i〇·如申請專利範圍第9項之方法 11·如申請專利範圍第9項之方法 在 1 μΜ至0.1 Μ。 12·如申睛專利範圍第9項之方法 該酵素為尿素分解。 28 1302198 · 13·如申請專利範圍第9項之方法,其中該反應物為肌酐酸 時,該酵素為肌酐酸去亞胺 。 14.如申請專利範圍第9項之方法,其中該反應物為乙酿膽鹼 時,該酵素為乙醯膽鹼 。 15·如申請專利範圍第9項之方法,其中該緩衝溶液為丨,3_二 f [l?3-bis[tris(hydroxymethyl) methylamino]propane ; BTP】。 l6.如申請專利範圍第9項之方法,其中該生物感·系統更 包含一偵測探針。 =申請翻翻第9項之方法,其中該_探針為一勞光 其中該螢光染劑為ΠΤΟ ,更包含計算不同型態之該 ’更包含計算該偵測探針之 18·如申請專利範圍第17項之方法 ®甸聚酶。 19·如申請專利範圍第16項之方法 偵蜊探針的分佈。 2〇.如申請專利範圍第16項之方法 表現強度。 •如申请專利範圍第16項 物濃声日士 乃忐更包合侍出在該不同反應 X守,3亥谓測探針之該表現強度。Knowing the buffering capacity and the fractional capacity, the buffering capacity is set, wherein the pH is set to 5, wherein the reactant concentration is set to be the urea, and the method is the method of the ninth aspect of the patent application. The method of claim 9 is in the range of 1 μΜ to 0.1 Μ. 12. The method of claim 9 of the scope of the patent application is that the enzyme is decomposed by urea. The method of claim 9, wherein the reactant is creatinine, the enzyme is creatinine deimin. 14. The method of claim 9, wherein the enzyme is acetylcholine when the reactant is choline. 15. The method of claim 9, wherein the buffer solution is 丨, 3_2 f [l?3-bis[tris(hydroxymethyl) methylamino]propane; BTP]. The method of claim 9, wherein the biological sensor system further comprises a detection probe. = The method of applying to turn over Item 9, wherein the _probe is a light-emitting light, wherein the fluorescent dye is ΠΤΟ, and the calculation includes the calculation of the different types of the detection probe. Method 17 of the patent scope ® Polymerase. 19. The method of claim 16 of the scope of the patent application. 2〇. The method of applying for the scope of patents, item 16 performance intensity. • If you apply for the scope of the patent, the 16th item, the sound of the Japanese singer, the singer, the singer, the singer, the singer, the performance of the test probe.
TW094118467A 2005-06-03 2005-06-03 Method for simplifying optimization during research and development of detector system TW200643417A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
TW094118467A TW200643417A (en) 2005-06-03 2005-06-03 Method for simplifying optimization during research and development of detector system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
TW094118467A TW200643417A (en) 2005-06-03 2005-06-03 Method for simplifying optimization during research and development of detector system

Publications (2)

Publication Number Publication Date
TW200643417A TW200643417A (en) 2006-12-16
TWI302198B true TWI302198B (en) 2008-10-21

Family

ID=45070423

Family Applications (1)

Application Number Title Priority Date Filing Date
TW094118467A TW200643417A (en) 2005-06-03 2005-06-03 Method for simplifying optimization during research and development of detector system

Country Status (1)

Country Link
TW (1) TW200643417A (en)

Also Published As

Publication number Publication date
TW200643417A (en) 2006-12-16

Similar Documents

Publication Publication Date Title
Azmi et al. A simple and sensitive fluorescence based biosensor for the determination of uric acid using H2O2-sensitive quantum dots/dual enzymes
Yang et al. A TP-FRET-based two-photon fluorescent probe for ratiometric visualization of endogenous sulfur dioxide derivatives in mitochondria of living cells and tissues
Cheng et al. Reaction-based colorimetric cyanide chemosensors: rapid naked-eye detection and high selectivity
Xiang et al. An invasive DNA approach toward a general method for portable quantification of metal ions using a personal glucose meter
Yi et al. A Dual‐Response Fluorescent Probe Reveals the H2O2‐Induced H2S Biogenesis through a Cystathionine β‐Synthase Pathway
Kimble et al. Progress toward the development of a point-of-care photonic crystal ammonia sensor
Horn et al. Stabilities of Trityl‐Protected Substrates: The Wide Mechanistic Spectrum of Trityl Ester Hydrolyses
Young et al. Accurate and sensitive quantitation of glucose and glucose phosphates derived from storage carbohydrates by mass spectrometry
Liang et al. Determination of propofol UDP-glucuronosyltransferase (UGT) activities in hepatic microsomes from different species by UFLC–ESI-MS
Seto et al. A simple and selective fluorometric assay for dopamine using a calcein blue–Fe2+ complex fluorophore
Yu et al. Fold-change compression: an unexplored but correctable quantitative bias caused by nonlinear electrospray ionization responses in untargeted metabolomics
Burton et al. A novel enzymatic technique for determination of sarcosine in urine samples
Kirby et al. Activating Water: Important Effects of Non‐leaving Groups on the Hydrolysis of Phosphate Triesters
Gosmaro et al. Measurement of total antioxidant capacity of human plasma: Setting and validation of the CUPRAC–BCS method on routine apparatus ADVIA 2400
Baranov et al. Kinetic model for Ca2+-induced permeability transition in energized liver mitochondria discriminates between inhibitor mechanisms
Michalski et al. Oxidation of ethidium-based probes by biological radicals: Mechanism, kinetics and implications for the detection of superoxide
Shen et al. Employing an ICT-ESIPT strategy for ratiometric tracking of HClO based on sulfide oxidation reaction
JP2013541009A (en) Sample detection method
CN103472041A (en) Use method for creatinine content detection kit
TWI302198B (en)
CN100554939C (en) Serum sodium ion by enzymatic method is measured reagent and method
Caldwell et al. Characterization of HOCl using atmospheric pressure ionization mass spectrometry
Ganorkar et al. Validated stability indicating and assay method development of linagliptin in formulation by RP-HPLC using quality by design
Rahman et al. Quantitative analysis of irbesartan in commercial dosage forms by kinetic spectrophotometry
Jia et al. Rhodamine B Piperazinoacetohydrazine: A Water‐Soluble Spectroscopic Reagent for Pyruvic Acid Labeling

Legal Events

Date Code Title Description
MM4A Annulment or lapse of patent due to non-payment of fees