Neste trabalho estudou-se o desenvolvimento de metodologia analitica para a determinação e quantificação de sete anti-inflamatórios não esteroides, amplamente consumidos para tratamento humano, além da cafeína, determinada como marcador antropogênico, em amostras aquosas ambientais. Os analitos estudados foram acetaminofeno (AC), ácido salicílico (AS), cafeína (CA), cetoprofeno (CE), diclofenaco (DC), dipirona (DP), ibuprofeno (IB) e naproxeno (NA) . Como padrão internos, foi utilizado o lindano (LI). A determinação destes analitos foi realizada utilizando-se cromatografia a gás acoplada à espectrometria de massas (GC-MS) utilizando MSTFA/Imidazol como derivatizante. As condições para a reação de derivatização foram otimizadas utilizando o planejamento Doehlert. O procedimento de pré-concentração utilizado foi a extração em fase sólida (SPE), tendo como sorvente um sistema de fase polimérica reversa. O procedimento de SPE foi baseado em trabalhos publicados na literatura, com metanol e água (ajustada a pH 3,0) para o condicionamento e eluição com acetonitrila. Os parâmetros de desempenho do método, como recuperação, linearidade, limite de detecção, limite de quantificação, repetitividade e reprodutibilidade foram avaliados de acordo com as normas estabelecidas pela ANVISA e INMETRO. Os limites de detecção ficaram entre 1,09 e 1079,14 ng L-1 e os de quantificaçõ entre 3,63 e 3597,12 ng L-1. Após as definições em relação ao método, amostras de água do Arroio Dilúvio (em Porto Alegre – RS) e de uma Estação Piloto de tratamento de efluente pertencente ao Instituto de Pesquisas Hidráulicas (IPH/UFRGS) , foram analisadas para avaliar a presença destes analitos. As amostras da ETE-piloto do IPH, foram coletadas nos meses de janeiro e fevereiro e as amostras do Arroio Dilúvio também foram coletadas no mesmo período. Considerando as amostras reais analisadas em algumas foram detectados e em outras quantificados os antiinflamatórios estudados. Nas amostras que estes compostos foram quantificados, a faixa de concentração variou entre 0,09 e 23,16 μg L-1. / In this work the development of an analytic methodology was studied to determine and quantify seven non-steroidal anti-inflammatory drugs, widely used in human treatment, and caffeine considered an anthropogenic marker. The compounds studied were acetaminophen (AC), salicylic acid (AS), caffeine (CA), ketoprofen (CE), diclofenac (DC), dipyrone (DP), ibuprofen (IB), naproxen (NA) and lindane (LI) as internal standard. The determination of these compounds was performed using gas chromatography coupled to mass spectrometry (GC-MS) with derivatization of the target analytes using MSTFA/Imidazole. The derivatization conditions were optimized with Doehlert design. Solid phase extraction (SPE) with a polymeric reversed solid phase was used as a pre-concentration system. The SPE procedure conditions were based previously established data in the literature, using methanol and water (adjusted to pH 3.0) for the conditioning step and acetonitrile for the elution step The performance parameters, such recovery, linearity, detection limit, quantification limit, repeatability and reproducibility were evaluated according to ANVISA and INMETRO determinations. The detection limits was in the range of 1,09 and 1079,14 ng L -1 and the quantification limits 3,63 and 3597,12 gn L-1. After method establishment, samples from a piloto sewage treatment plant and river water, both in Porto Alegre-RS, were analysed. The samples were collected in January and February 2012, both in the pilot plant and in the river water. In some real samples the antiinflammatories were detected and in others was possible quantify. In the samples were the analytes were quantified, the concentration range was 0,09 to 23,16 μg L-1.

Neste trabalho estudou-se o desenvolvimento de metodologia analitica para a determinação e quantificação de sete anti-inflamatórios não esteroides, amplamente consumidos para tratamento humano, além da cafeína, determinada como marcador antropogênico, em amostras aquosas ambientais. Os analitos estudados foram acetaminofeno (AC), ácido salicílico (AS), cafeína (CA), cetoprofeno (CE), diclofenaco (DC), dipirona (DP), ibuprofeno (IB) e naproxeno (NA) . Como padrão internos, foi utilizado o lindano (LI). A determinação destes analitos foi realizada utilizando-se cromatografia a gás acoplada à espectrometria de massas (GC-MS) utilizando MSTFA/Imidazol como derivatizante. As condições para a reação de derivatização foram otimizadas utilizando o planejamento Doehlert. O procedimento de pré-concentração utilizado foi a extração em fase sólida (SPE), tendo como sorvente um sistema de fase polimérica reversa. O procedimento de SPE foi baseado em trabalhos publicados na literatura, com metanol e água (ajustada a pH 3,0) para o condicionamento e eluição com acetonitrila. Os parâmetros de desempenho do método, como recuperação, linearidade, limite de detecção, limite de quantificação, repetitividade e reprodutibilidade foram avaliados de acordo com as normas estabelecidas pela ANVISA e INMETRO. Os limites de detecção ficaram entre 1,09 e 1079,14 ng L-1 e os de quantificaçõ entre 3,63 e 3597,12 ng L-1. Após as definições em relação ao método, amostras de água do Arroio Dilúvio (em Porto Alegre – RS) e de uma Estação Piloto de tratamento de efluente pertencente ao Instituto de Pesquisas Hidráulicas (IPH/UFRGS) , foram analisadas para avaliar a presença destes analitos. As amostras da ETE-piloto do IPH, foram coletadas nos meses de janeiro e fevereiro e as amostras do Arroio Dilúvio também foram coletadas no mesmo período. Considerando as amostras reais analisadas em algumas foram detectados e em outras quantificados os antiinflamatórios estudados. Nas amostras que estes compostos foram quantificados, a faixa de concentração variou entre 0,09 e 23,16 μg L-1. / In this work the development of an analytic methodology was studied to determine and quantify seven non-steroidal anti-inflammatory drugs, widely used in human treatment, and caffeine considered an anthropogenic marker. The compounds studied were acetaminophen (AC), salicylic acid (AS), caffeine (CA), ketoprofen (CE), diclofenac (DC), dipyrone (DP), ibuprofen (IB), naproxen (NA) and lindane (LI) as internal standard. The determination of these compounds was performed using gas chromatography coupled to mass spectrometry (GC-MS) with derivatization of the target analytes using MSTFA/Imidazole. The derivatization conditions were optimized with Doehlert design. Solid phase extraction (SPE) with a polymeric reversed solid phase was used as a pre-concentration system. The SPE procedure conditions were based previously established data in the literature, using methanol and water (adjusted to pH 3.0) for the conditioning step and acetonitrile for the elution step The performance parameters, such recovery, linearity, detection limit, quantification limit, repeatability and reproducibility were evaluated according to ANVISA and INMETRO determinations. The detection limits was in the range of 1,09 and 1079,14 ng L -1 and the quantification limits 3,63 and 3597,12 gn L-1. After method establishment, samples from a piloto sewage treatment plant and river water, both in Porto Alegre-RS, were analysed. The samples were collected in January and February 2012, both in the pilot plant and in the river water. In some real samples the antiinflammatories were detected and in others was possible quantify. In the samples were the analytes were quantified, the concentration range was 0,09 to 23,16 μg L-1.

Neste trabalho estudou-se o desenvolvimento de metodologia analitica para a determinação e quantificação de sete anti-inflamatórios não esteroides, amplamente consumidos para tratamento humano, além da cafeína, determinada como marcador antropogênico, em amostras aquosas ambientais. Os analitos estudados foram acetaminofeno (AC), ácido salicílico (AS), cafeína (CA), cetoprofeno (CE), diclofenaco (DC), dipirona (DP), ibuprofeno (IB) e naproxeno (NA) . Como padrão internos, foi utilizado o lindano (LI). A determinação destes analitos foi realizada utilizando-se cromatografia a gás acoplada à espectrometria de massas (GC-MS) utilizando MSTFA/Imidazol como derivatizante. As condições para a reação de derivatização foram otimizadas utilizando o planejamento Doehlert. O procedimento de pré-concentração utilizado foi a extração em fase sólida (SPE), tendo como sorvente um sistema de fase polimérica reversa. O procedimento de SPE foi baseado em trabalhos publicados na literatura, com metanol e água (ajustada a pH 3,0) para o condicionamento e eluição com acetonitrila. Os parâmetros de desempenho do método, como recuperação, linearidade, limite de detecção, limite de quantificação, repetitividade e reprodutibilidade foram avaliados de acordo com as normas estabelecidas pela ANVISA e INMETRO. Os limites de detecção ficaram entre 1,09 e 1079,14 ng L-1 e os de quantificaçõ entre 3,63 e 3597,12 ng L-1. Após as definições em relação ao método, amostras de água do Arroio Dilúvio (em Porto Alegre – RS) e de uma Estação Piloto de tratamento de efluente pertencente ao Instituto de Pesquisas Hidráulicas (IPH/UFRGS) , foram analisadas para avaliar a presença destes analitos. As amostras da ETE-piloto do IPH, foram coletadas nos meses de janeiro e fevereiro e as amostras do Arroio Dilúvio também foram coletadas no mesmo período. Considerando as amostras reais analisadas em algumas foram detectados e em outras quantificados os antiinflamatórios estudados. Nas amostras que estes compostos foram quantificados, a faixa de concentração variou entre 0,09 e 23,16 μg L-1. / In this work the development of an analytic methodology was studied to determine and quantify seven non-steroidal anti-inflammatory drugs, widely used in human treatment, and caffeine considered an anthropogenic marker. The compounds studied were acetaminophen (AC), salicylic acid (AS), caffeine (CA), ketoprofen (CE), diclofenac (DC), dipyrone (DP), ibuprofen (IB), naproxen (NA) and lindane (LI) as internal standard. The determination of these compounds was performed using gas chromatography coupled to mass spectrometry (GC-MS) with derivatization of the target analytes using MSTFA/Imidazole. The derivatization conditions were optimized with Doehlert design. Solid phase extraction (SPE) with a polymeric reversed solid phase was used as a pre-concentration system. The SPE procedure conditions were based previously established data in the literature, using methanol and water (adjusted to pH 3.0) for the conditioning step and acetonitrile for the elution step The performance parameters, such recovery, linearity, detection limit, quantification limit, repeatability and reproducibility were evaluated according to ANVISA and INMETRO determinations. The detection limits was in the range of 1,09 and 1079,14 ng L -1 and the quantification limits 3,63 and 3597,12 gn L-1. After method establishment, samples from a piloto sewage treatment plant and river water, both in Porto Alegre-RS, were analysed. The samples were collected in January and February 2012, both in the pilot plant and in the river water. In some real samples the antiinflammatories were detected and in others was possible quantify. In the samples were the analytes were quantified, the concentration range was 0,09 to 23,16 μg L-1.

<p>Infrared absorption spectra can provide analytically useful information on a large variety of compounds, ranging from small ions to large biological molecules. In fact, all analytes that possess a dipole moment that changes during vibration are infrared-active. The infrared (IR) spectrum can be subdivided into far-, mid- and near- regions. The focus of attention in this thesis is the mid-IR region, in which the fundamental vibrations of most organic compounds are located, thus providing scope for positive structural identification. However, while such near-ubiquitous signals can be very useful for monitoring simple molecules in simple systems, they can be increasingly disadvantageous as the number of analytes and/or the complexity of the sample matrix increases. Thus, hyphenation to a separation system prior to detection is desirable. Paper I appended to this thesis presents (for the first time) the on-line hyphenation between Fourier transform infrared spectroscopy, FTIR, and capillary zone electrophoresis, CZE. CZE is a highly efficient separation technique that separates ionic analytes with respect to their charge-to-size ratio. It is most commonly performed in aqueous buffers in fused silica capillaries. Since these capillaries absorb virtually all infrared light an IR-transparent flow cell had to be developed. In further studies (Paper II) the applicability of CZE is expanded to include neutral analytes by the addition of micelles to the buffer, and micellar electrokinetic chromatography, MEKC, was successfully hyphenated to FTIR for the first time. Paper III describes an application of the on-line CZE-FTIR technique in which non-UV-absorbing analytes in a complex matrix were separated, identified and quantified in one run.</p><p>Measuring aqueous solutions in the mid-IR region is not straightforward since water absorbs intensely in this region, sometimes completely, leaving no transmitted, detectable light. For this reason, quantum cascade lasers are interesting. These lasers represent a new type of mid-IR semiconducting lasers with high output power due to their ingenious design. The laser action lies within one conduction band (intersubband) and can be tailored to emit light in the entire mid-IR region using the same semiconducting material. To investigate their potential to increase the optical path length in aqueous solutions, these lasers were used with an aqueous flow system (Paper IV), and the experience gained in these experiments enabled hyphenation of such lasers to a CZE system (Paper V).</p>

Infrared absorption spectra can provide analytically useful information on a large variety of compounds, ranging from small ions to large biological molecules. In fact, all analytes that possess a dipole moment that changes during vibration are infrared-active. The infrared (IR) spectrum can be subdivided into far-, mid- and near- regions. The focus of attention in this thesis is the mid-IR region, in which the fundamental vibrations of most organic compounds are located, thus providing scope for positive structural identification. However, while such near-ubiquitous signals can be very useful for monitoring simple molecules in simple systems, they can be increasingly disadvantageous as the number of analytes and/or the complexity of the sample matrix increases. Thus, hyphenation to a separation system prior to detection is desirable. Paper I appended to this thesis presents (for the first time) the on-line hyphenation between Fourier transform infrared spectroscopy, FTIR, and capillary zone electrophoresis, CZE. CZE is a highly efficient separation technique that separates ionic analytes with respect to their charge-to-size ratio. It is most commonly performed in aqueous buffers in fused silica capillaries. Since these capillaries absorb virtually all infrared light an IR-transparent flow cell had to be developed. In further studies (Paper II) the applicability of CZE is expanded to include neutral analytes by the addition of micelles to the buffer, and micellar electrokinetic chromatography, MEKC, was successfully hyphenated to FTIR for the first time. Paper III describes an application of the on-line CZE-FTIR technique in which non-UV-absorbing analytes in a complex matrix were separated, identified and quantified in one run. Measuring aqueous solutions in the mid-IR region is not straightforward since water absorbs intensely in this region, sometimes completely, leaving no transmitted, detectable light. For this reason, quantum cascade lasers are interesting. These lasers represent a new type of mid-IR semiconducting lasers with high output power due to their ingenious design. The laser action lies within one conduction band (intersubband) and can be tailored to emit light in the entire mid-IR region using the same semiconducting material. To investigate their potential to increase the optical path length in aqueous solutions, these lasers were used with an aqueous flow system (Paper IV), and the experience gained in these experiments enabled hyphenation of such lasers to a CZE system (Paper V).

Diese Arbeit leistet einen methodischen Beitrag zur Identifizierung von Umsetzungsprozessen der Stickstoffverbindungen Ammonium und Nitrat in belasteten Grundwasserleitern mittels der Analytik der Isotopenverhältnisse N-15 bzw. O-18. Es existieren bereits verschiedene Präparationsmethoden, jedoch sind diese teilweise arbeits- oder zeitaufwändig und damit mit erheblichen Kosten verbunden. Für eine breitere Anwendbarkeit in den Umweltwissenschaften wurden im Rahmen dieser Arbeit zwei vereinfachte Methoden für die N-15 bzw. O-18 Stabilisotopenanalytik von Ammonium und Nitrat in Wässern erarbeitet. Zum einen wurde eine Fällungsmethode mit Natriumtetraphenylborat für die Probenvorbereitung der N-15 Isotopenanalyse für Ammonium weiterentwickelt, getestet und validiert. Bisher existierten keine Studien zur Anwendbarkeit dieser Methode auf die Analyse ammoniumhaltiger Wasserproben. Daher wurde die Methode in dieser Arbeit für die Anwendbarkeit auf Wasserproben optimiert, insbesondere auf natürliche Grundwasserproben. Zum anderen wurde eine gängige Aufbereitungsmethode für gelöstes Nitrat weiterentwickelt. Dabei wurden die Vorbereitungs- und Arbeitszeit der Denitrifizierermethode verkürzt, ohne die Genauigkeit der Messung negativ zu beeinflussen. Zu diesem Zweck wurden zwei bestehende Varianten der Methode miteinander kombiniert und modifiziert. Als Eignungsprüfung der Methoden zur Prozessidentifikation erfolgte eine exemplarische Feldstudie. Als Modellstandort diente ein Untersuchungsgebiet im Südosten Berlins. Der Grundwasserleiter des Standortes ist u. a. durch eine massive Kontamination von Ammonium gekennzeichnet. Im Untersuchungsgebiet wurde das sogenannte BIOXWAND-Verfahren entwickelt und zur Sanierung auf den Grundwasserleiter angewandt. Dabei handelt es sich um ein in-situ-Verfahren, wobei eine direkte Injektion von Sauerstoff in den Grundwasserleiter erfolgt um Nitrifikation zu begünstigen. Für die isotopengestützte Prozessidentifikation wurden im Rahmen dieser Arbeit von 2016 bis 2019 zweimal jährlich Grundwasserproben aus dem BIOXWAND-Anstrom und dem BIOXWAND-Abstrom entnommen und mit den erarbeiteten Präparationsmethoden aufbereitet und analysiert. Zur Prozessidentifikation wurde ein analytisches Modell erstellt. Bei der vorliegenden kumulativen Dissertation handelt es sich um eine verkürzte Darstellung der Forschungsergebnisse. Die ausführlichen Ergebnisse wurden bereits in der Fachzeitschrift 'Rapid Communications in Mass Spectrometry' veröffentlicht.:VERZEICHNIS DER TABELLEN ................................................................................ 9 VERZEICHNIS DER ABBILDUNGEN ....................................................................... 10 VERZEICHNIS DER ANHÄNGE .............................................................................. 11 VERZEICHNIS DER SYMBOLE UND ABKÜRZUNGEN ............................................. 12 1 EINLEITUNG UND MOTIVATION ....................................................................... 14 2 ZIELSETZUNG UND KONZEPT ............................................................................ 16 3 THEORETISCHE EINFÜHRUNG .......................................................................... 18 3.1 Stickstoff in der Umwelt ........................................................................................ 18 3.2 Ammonium und Nitrat im Stickstoffkreislauf ........................................................... 18 3.3 Einflussfaktoren auf die Prozesse des Stickstoffkreislaufs ....................................... 21 3.4 Isotopenanalytik in den Umweltwissenschaften ...................................................... 22 3.4.1 Definition stabiler Isotope ................................................................................................... 22 3.4.2 Isotopieeffekte und Fraktionierung .................................................................................... 24 3.4.3 Delta-Notation ....................................................................................................................... 25 3.4.4 Fraktionierungs- und Anreicherungsfaktor ....................................................................... 28 3.5 Analyse stabiler Isotope mittels Isotopenverhältnis-Massenspektrometrie ................. 29 3.5.1 Allgemeine Informationen ................................................................................................... 29 3.5.2 Massenspektrometer ............................................................................................................ 29 3.5.3 Analyse stabiler Isotope mittels Elementaranalysator-Isotopenverhältnis-Massenspektrometrie-Kopplung (EA-IRMS) ...................................................................... 31 3.5.4 Analyse stabiler Isotope mittels GasBench II – IRMS ..................................................... 33 3.6 Ammonium und Nitrat im Kontext stabiler Isotope .................................................. 34 4 PROBENAUFBEREITUNGSMETHODEN ............................................................... 37 4.1 Bedeutung der Probenaufbereitung ....................................................................... 37 4.2 Probenaufbereitung für die δ15N-Isotopenanalyse von gelöstem NH4+ ....................... 37 4.2.1 Destillationsmethode ............................................................................................................ 37 4.2.2 Quecksilberfällung ................................................................................................................ 37 4.2.3 Diffusionsmethode ................................................................................................................ 38 4.2.4 Kationenaustausch................................................................................................................ 39 4.2.5 Fällung von Ammonium mittels Tetraphenylborat ........................................................... 39 4.2.6 Weitere Methoden ................................................................................................................ 40 4.3 Zusammenfassung der Probenaufbereitungsmethoden für die δ15N-Isotopenanalyse von gelöstem NH4+ ............................................................................................... 40 4.4 Probenaufbereitung für die δ15N- und δ18O-Isotopenanalyse von gelöstem NO3− ........ 41 4.4.1 Reduktionsmethoden ........................................................................................................... 41 4.4.2 Denitrifizierermethode ......................................................................................................... 41 4.4.3 Silbernitratfällung.................................................................................................................. 42 4.4.4 Bariumnitratfällung ............................................................................................................... 43 4.5 Zusammenfassung der Probenaufbereitungsmethoden für die δ15N- und δ18O-Isotopenanalyse von gelöstem NO3- ....................................................................... 43 5 ÜBERBLICK DER DURCHGEFÜHRTEN STUDIEN ................................................ 44 5.1 δ15N-Analyse von Ammonium in gefriergetrockneten, natürlichen Grundwasserproben durch Fällung mit Natriumtetraphenylborat ............................................................ 44 5.2 Weiterführende Optimierung der Denitrifizierermethode für die schnelle 15N und 18O-Analyse von Nitrat in natürlichen Wasserproben ..................................................... 44 5.3 Beispielhafte Identifizierung von Nitrifikation und Sorptionsprozessen von Ammonium als Feldstudie ...................................................................................................... 45 6 DISKUSSION UND AUSBLICK ............................................................................ 47 7 DANKSAGUNG ................................................................................................... 50 8 LITERATURVERZEICHNIS ................................................................................. 51 ANHANG ............................................................................................................... 61 / This thesis provides a method to identify the transformation of the nitrogen species ammonium and nitrate in polluted aquifers by analyzing the isotope ratios N-15 and O-18. Various preparation methods already exist, but are either labor intensive or time consuming and are therefore related with considerable costs. To achieve a broader applicability in environmental sciences, two simplified methods for the N-15 and O-18 stable isotope analysis of ammonium and nitrate in water were developed in this thesis. On the one hand, a precipitation method using sodium tetraphenylborate for the sample preparation of the N-15 isotope analysis for ammonium was modified, tested and validated. So far no studies could verify the applicability of this method for analysis of water samples containing ammonium. Therefore, the method was optimized for applicability to water samples, especially natural groundwater samples within this thesis. On the other hand, a common processing method for dissolved nitrate was optimized. The preparation and working time of the denitrification method was shortened without negatively affecting the accuracy of the measurement. For this purpose, two existing variants of the method were combined and modified. Furthermore, an exemplary field study was carried out to test the suitability of the preparation methods for process identification. A study area southeast of Berlin (Germany) containing an aquifer massively contaminated with ammonium served as a model location. Inside the area, the so-called BIOXWAND process, an in-situ process whereby oxygen is injected directly into the aquifer to promote nitrification, was developed and applied to the aquifer in terms of remediation. For isotope-based process identification, groundwater samples were taken twice a year from 2016 to 2019 from the BIOXWAND inflow and outflow and analyzed using the preparation methods developed. An analytical model was created for process identification.:VERZEICHNIS DER TABELLEN ................................................................................ 9 VERZEICHNIS DER ABBILDUNGEN ....................................................................... 10 VERZEICHNIS DER ANHÄNGE .............................................................................. 11 VERZEICHNIS DER SYMBOLE UND ABKÜRZUNGEN ............................................. 12 1 EINLEITUNG UND MOTIVATION ....................................................................... 14 2 ZIELSETZUNG UND KONZEPT ............................................................................ 16 3 THEORETISCHE EINFÜHRUNG .......................................................................... 18 3.1 Stickstoff in der Umwelt ........................................................................................ 18 3.2 Ammonium und Nitrat im Stickstoffkreislauf ........................................................... 18 3.3 Einflussfaktoren auf die Prozesse des Stickstoffkreislaufs ....................................... 21 3.4 Isotopenanalytik in den Umweltwissenschaften ...................................................... 22 3.4.1 Definition stabiler Isotope ................................................................................................... 22 3.4.2 Isotopieeffekte und Fraktionierung .................................................................................... 24 3.4.3 Delta-Notation ....................................................................................................................... 25 3.4.4 Fraktionierungs- und Anreicherungsfaktor ....................................................................... 28 3.5 Analyse stabiler Isotope mittels Isotopenverhältnis-Massenspektrometrie ................. 29 3.5.1 Allgemeine Informationen ................................................................................................... 29 3.5.2 Massenspektrometer ............................................................................................................ 29 3.5.3 Analyse stabiler Isotope mittels Elementaranalysator-Isotopenverhältnis-Massenspektrometrie-Kopplung (EA-IRMS) ...................................................................... 31 3.5.4 Analyse stabiler Isotope mittels GasBench II – IRMS ..................................................... 33 3.6 Ammonium und Nitrat im Kontext stabiler Isotope .................................................. 34 4 PROBENAUFBEREITUNGSMETHODEN ............................................................... 37 4.1 Bedeutung der Probenaufbereitung ....................................................................... 37 4.2 Probenaufbereitung für die δ15N-Isotopenanalyse von gelöstem NH4+ ....................... 37 4.2.1 Destillationsmethode ............................................................................................................ 37 4.2.2 Quecksilberfällung ................................................................................................................ 37 4.2.3 Diffusionsmethode ................................................................................................................ 38 4.2.4 Kationenaustausch................................................................................................................ 39 4.2.5 Fällung von Ammonium mittels Tetraphenylborat ........................................................... 39 4.2.6 Weitere Methoden ................................................................................................................ 40 4.3 Zusammenfassung der Probenaufbereitungsmethoden für die δ15N-Isotopenanalyse von gelöstem NH4+ ............................................................................................... 40 4.4 Probenaufbereitung für die δ15N- und δ18O-Isotopenanalyse von gelöstem NO3− ........ 41 4.4.1 Reduktionsmethoden ........................................................................................................... 41 4.4.2 Denitrifizierermethode ......................................................................................................... 41 4.4.3 Silbernitratfällung.................................................................................................................. 42 4.4.4 Bariumnitratfällung ............................................................................................................... 43 4.5 Zusammenfassung der Probenaufbereitungsmethoden für die δ15N- und δ18O-Isotopenanalyse von gelöstem NO3- ....................................................................... 43 5 ÜBERBLICK DER DURCHGEFÜHRTEN STUDIEN ................................................ 44 5.1 δ15N-Analyse von Ammonium in gefriergetrockneten, natürlichen Grundwasserproben durch Fällung mit Natriumtetraphenylborat ............................................................ 44 5.2 Weiterführende Optimierung der Denitrifizierermethode für die schnelle 15N und 18O-Analyse von Nitrat in natürlichen Wasserproben ..................................................... 44 5.3 Beispielhafte Identifizierung von Nitrifikation und Sorptionsprozessen von Ammonium als Feldstudie ...................................................................................................... 45 6 DISKUSSION UND AUSBLICK ............................................................................ 47 7 DANKSAGUNG ................................................................................................... 50 8 LITERATURVERZEICHNIS ................................................................................. 51 ANHANG ............................................................................................................... 61