INFLUENCE OF ALGAL PRODUCTION ON ECOSYSTEM METABOLISM, MICROBIAL ACTIVITY AND NUTRIENT DYNAMICS IN A CENTRAL INDIANA STREAM A THESIS SUBMITTED TO THE GRADUATE SCHOOL IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE MASTER OF SCIENCE BY ANDREA S. FITZGIBBON ADVISORS: DR. MELODY J. BERNOT & DR. KEVIN H. WYATT BALL STATE UNIVERSITY MUNCIE, INDIANA JULY 2014 INFLUENCE OF ALGAL PRODUCTION ON ECOSYSTEM METABOLISM, MICROBIAL ACTIVITY AND NUTRIENT DYNAMICS IN A CENTRAL INDIANA STREAM A THESIS SUBMITTED TO THE GRADUATE SCHOOL IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE MASTER OF SCIENCE BY ANDREA S. FITZGIBBON ADVISORS: DR. MELODY J. BERNOT & DR. KEVIN H. WYATT Committee Approval: ___________________________________________________________ Committee Chairperson ____________ Date ___________________________________________________________ Committee Member ____________ Date ___________________________________________________________ Committee Member ____________ Date Departmental Approval: ___________________________________________________________ Departmental Chairperson ____________ Date ___________________________________________________________ Dean of Graduate School ____________ Date BALL STATE UNIVERSITY MUNCIE, INDIANA JULY 2014 TABLE OF CONTENTS TABLE OF CONTENTS…………………………………………………………………..…….iii LIST OF FIGURES CHAPTER 1………………………………………………………...….…..iv LIST OF TABLES CHAPTER 1………………………………………………………...….…...vi LIST OF FIGURES CHAPTER 2……………………………………………………………….vii LIST OF TABLES CHAPTER 2………………………………………………………………...ix ABSTRACT……………………………………………………………………………………….1 ACKNOWLEGEMENTS…………………………………………………………………………3 CHAPTER 1: Comparison of algal and ecosystem metabolism and nutrient dynamics in a central Indiana stream ABSTRACT………………………………………………………………………………….……4 INTRODUCTION………………………………………………………………………….……..6 METHODS……………………………………………………………………………….……….8 RESULTS…………………………………………………………………………….………….14 DISCUSSION…………………………………………………………………….……………...21 CONCLUSIONS………………………………………………………………….…………......26 REFERENCES…………………………………………………………………….………….....27 FIGURES AND TABLES…………………………………………………………….………....32 CHAPTER 2: Influence of algal exudates on microbial activity and ecosystem dynamics ABSTRACT………………………………………………………………………………….…..44 INTRODUCTION………………………………………………………………………….……46 METHODS……………………………………………………………………………….……...48 RESULTS…………………………………………………………………………….………….53 DISCUSSION…………………………………………………………………….……….……..56 CONCLUSIONS………………………………………………………………….…………......59 REFERENCES…………………………………………………………………….………….....61 FIGURES AND TABLES…………………………………………………………….………....66 APPENDIXES…………………………………………………………………………………...75 iii LIST OF FIGURES Figure Page CHAPTER 1: Comparison of algal and ecosystem metabolism and nutrient dynamics in a central Indiana stream 1. Conceptual model of hypothesized algal mediated diurnal patterns of nutrients, (top panels) dissolved organic carbon (DOC), dissolve inorganic nitrogen (DIN); physiochemistry, (middle panels) dissolved oxygen (O2) and pH; and metabolism, (bottom panels) primary production, respiration and decomposition. ……………….….32 2. Conceptual model of hypothesized seasonal water column and algae patterns of dissolved oxygen (top panel); nutrients (middle panel); and metabolism, (bottom panels) primary production and respiration. ……………………………………………………………..33 3. Water column and algae diurnal variation in dissolved oxygen (DO, mg O2 /L) concentration and pH over time in July and December 2013. ………………………….34 4. Mean seasonal water column and algae dissolved oxygen concentrations. (n= 9 days per season; Winter = Dec - Feb, Spring = Mar - May, Summer = Jun - Aug, Fall = Sep Nov). Error bars indicate SD. Dashed line indicates a 1:1 relationship. ………………..37 5. Mean seasonal water column and algae pH. (n= 9 days per season; Winter = Dec - Feb, Spring = Mar - May, Summer = Jun - Aug, Fall = Sep - Nov). Error bars indicate SD. Dashed line indicates a 1:1 relationship. …………………………………………...…...38 6. Mean seasonal water column and algae total organic carbon concentrations. (n = 9 days per season; Winter = Dec - Feb, Spring = Mar - May, Summer = Jun - Aug, Fall = Sep Nov). Error bars indicate SD. Dashed line indicates a 1:1 relationship. …………….…39 7. Mean seasonal water column and algae nitrate concentrations. (n= 9 days per season; Winter = Dec - Feb, Spring = Mar - May, Summer = Jun - Aug, Fall = Sep - Nov). Error bars indicate SD. Dashed line indicates a 1:1 relationship. ……………………………40 8. Mean seasonal water column and algae phosphate concentrations. (n= 9 days per season; Winter = Dec - Feb, Spring = Mar - May, Summer = Jun - Aug, Fall = Sep - Nov). Error bars indicate SD. Dashed line indicates a 1:1 relationship. ……………………………41 iv 9. Mean daily rates of (A) GPP, (B) ER and (C) NEP measured in White River, Yorktown, Indiana from January through December 2013 (n = 2-3 days per month). Error bars indicate SD. Shaded area (A) indicated mean dry algal biomass (n = 12). ……………42 v LIST OF TABLES Table Page CHAPTER 1: Comparison of algal and ecosystem metabolism and nutrient dynamics in a central Indiana stream 1. Physiochemical characteristics of the water column (Water) and algae in the White River, Yorktown, Indiana from January through December 2013. Dissolved oxygen (DO), pH, temperature and conductivity were measured continuously at 10 minute intervals over approximately 72 hours (n = 125-432). Width (n = 1), flow and depth (n = 5) were measured during the sampling event. Discharge (n = 1) was calculated from width, flow and depth. Parentheses indicate standard error. …………………………………………35 2. Cumulative mean water column (Water) and algae, total organic carbon (TOC), nitrate (NO3), phosphate (PO4) and ammonium (NH4) concentrations. Phosphate concentrations were the below detection limit (0.01 mg/L) September through December. Standard error in parentheses, N= 48-144. ……………………………………………………………...36 3. Multiple regression model covariates for water and algal gross primary production (GPP) and ecosystem respiration (ER). ……………………………………………....….……..43 vi . LIST OF FIGURES Figure Page CHAPTER 2: Influence of algal exudates and benthic substrata on microbial activity 1. Mean dissolved oxygen across mesocosm treatments (algae, exudate and control) over three sampling events (n = 126 for algae treatment, n = 63 for exudate and control treatments). Error bars indicate SE. Note y-axis begins at 7.00 mg O2/ L. Dissolved oxygen differs by treatment (p = 0.027) but not by substrate (p= 0.241) with no interaction between main effects (p = 0.723). Pairwise differences indicated by letters above bars. ………………………………………………………………………………66 2. Mean pH of mesocosm (A) treatment (algae, exudate and control) and (B) substrate (sediment, leaves, sponge and glass) over three sampling events (n = 126 for algae treatment, n = 63 for exudate and control treatments, n = 60 for each substrate). Error bars indicate SE. Note y-axis begins at 8.00. pH differs by treatment and substrate (p < 0.001) with no interaction between main effects (p = 0.397). Pairwise differences indicated by letters above bars. ………………………………………………………….68 3. Mean total organic carbon (TOC) of mesocosm (A) treatment (algae, exudate and control) and (B) substrate (sediment, leaves, sponge and glass) over two sampling events (n = 32 for algae treatment, n = 16 for exudate and control treatments, n = 16 for each substrate). Error bars indicate SE. TOC differs by treatment (p < 0.0001) and substrate (p < 0.0001) with an interaction between main effects (p = 0.0073). Pairwise differences indicated by letters above bars. ……………………………………………………….…69 4. Mean nitrate (NO3) concentration by mesocosm (A) treatment (algae, exudate and control) and (B) substrate (sediment, leaves, sponge and glass) over two sampling events (n = 64 for algae treatment, n = 32 for exudate and control treatments, n = 32 for each substrate). Error bars indicate SE. NO3 differs by treatment (p = 0.0002) and substrate (p < 0.0001) with an interaction between main effects (p = 0.0003). Pairwise differences indicated by letters above bars. …………………………………………………………70 5. Mean phosphate (PO4) concentration by mesocosm (A) treatment (algae, exudate and control) and (B) substrate (sediment, leaves, sponge and glass) over two sampling events (n = 64 for algae treatment, n = 32 for exudate and control treatments, n = 32 for each substrate). Error bars indicate SE. PO4 differs by treatment (p = 0.0003) and substrate (p vii 6. = 0.0003) with no interaction between main effects (p < 0.0001). Pairwise differences indicated by letters above bars. …………………………………………………………71 Nutrient ratios of total organic carbon (TOC) to nitrate (NO3) and phosphate (PO4) among treatments (algae, exudate and control). Error bars indicate SE. TOC: NO3 did not differ by treatment (p = 0.263) nor did TOC: PO4 (p = 0.126). Dashed lines indicate differences in nutrient availability; arrows indicate high or low amounts of nutrient available. ………………………………………………………………………………...72 7. Mean respiration by mesocosm substrate type (sediment, leaves, sponge and glass; n = 20). Error bars indicate SE. Respiration differs by substrate (p < 0.001) but not by treatment (p = 0.997) with no interaction between main effects (p = 0.803). Pairwise differences indicated by letter above bars. ……………………………………………....73 8. Relationship between total organic carbon (TOC) concentration and microbial respiration by treatment (algae, exudate and control) (p < 0.01). ………………………………..….74 viii LIST OF TABLES Table Page CHAPTER 2: Influence of algal exudates and benthic substrata on microbial activity 1. Mean mesocosm temperature (°C) across algal and substrate treatments over three sampling events (n = 126 for algae treatment, n = 63 for exudate and control treatments and n = 60 for substrate treatments). Numbers in parentheses are SE. Temperature differs by treatment (p = 0.010) but not by substrate (p = 0.573) with no interaction between main effects (p = 0.371). Pairwise difference denoted by letters. ………………………67 ix ABSTRACT THESIS: Influence of algal production on ecosystem metabolism, microbial activity and nutrient dynamics in a central Indiana stream STUDENT: Andrea S. Fitzgibbon DEGREE: Masters of Science COLLEGE: Sciences and Humanities DATE: July 2014 PAGES: 155 One primary function in most ecosystems is photosynthesis which provides energy for consumers. In mid-order streams, benthic algae are primary producers fulfilling this role and their influence on stream biogeochemistry changes with the diurnal patterns of production. During the day, photosynthesis increases stream oxygen concentrations facilitating shifts in pH and nutrient concentrations. However, little is known about diurnal patterns of nutrient concentrations. Algal production regulates nutrient cycling through assimilation of inorganic nutrients and release of nitrogen and carbon exudates. Though nutrient assimilation by algae in streams is well understood, understanding of algal nutrient release is limited. Nutrient release by algae is a significant gap in our knowledge of ecosystem dynamics, especially in nutrient saturated streams. To understand algal dynamics in a nutrient saturated stream, algal production in a mid-order stream was measured via monthly sampling for one year using microelectrodes to quantify algal biofilm chemical gradients of dissolved oxygen and pH. Ecosystem energetics as gross primary production (GPP) and ecosystem respiration (ER) were also calculated. Nutrients were analyzed from water column and algal pore water samples. Dissolved oxygen concentrations and pH between the algae and water column followed similar diurnal curves although the amplitude of these changes varied seasonally. Nutrient and total organic carbon 1 concentrations varied seasonally. Overall, algae contributed ~ 13 % of primary production to total ecosystem production. Additionally, we assessed the influence of algal production on microbial activity using an in vitro factorial experiment. The objective of the experiment was to understand how algae may stimulate microbial respiration in a eutrophic stream ecosystem. An algal effect on microbial respiration after 3 days, was not observed likely because the labile algal exudates were quickly assimilated before the assay was conducted. Leaf substrates yielded the highest rates of microbial respiration likely due to higher carbon availability associated with leachate. Continued study of microbial responses to algae and benthic substrates will help predict ecosystem responses with changing nutrient status as streams become eutrophic. 2 ACKNOWLEDGEMENTS I would first like to thank the funding sources for this study including Ball State Graduate Student Research Program, Ball State University ASPiRE Graduate Research Program and the Indiana Academy of Science Welch Botanical Award. Thanks to Adam Carpenter, Ron and Toni Fitzgibbon, Jessica Moak and Ethan Toombs for their field assistance as well as Susannah Dragash and James Justice for their laboratory assistance. Thanks to Dr. Allison Rober for her time spent serving as a valuable committee member for this project. Lastly, I thank my advisors, Dr. Melody Bernot and Dr. Kevin Wyatt for the opportunity to be co-advised which has developed my research skill and interests, for their time, expertise and for their valuable guidance and advice throughout this study. 3 CHAPTER 1: Comparison of algal and ecosystem metabolism and nutrient dynamics in a central Indiana stream Abstract Benthic algae are primary producers in streams and can regulate nutrient cycling through assimilation and release of nutrients which may influence ecosystem process rates. Algal biofilm and water column metabolism estimates were quantified monthly over 1 yr in a central Indiana 3rd order stream. Biofilm dissolved oxygen (DO) and pH were measured continuously using microelectrodes and contrasted with water column dynamics. Specifically, algal DO concentrations ranged from 2.41 - 16.95 mg L-1 while water column DO concentrations ranged from 5.07 - 18.07 mg L-1. Algal pH (7.75 - 8.65) was lower than water column pH (8.88 - 9.73). Algae and the water column DO concentrations and pH elicited similar diurnal patterns that varied seasonally. Overall, algal pore water had higher total organic carbon concentrations relative to the water column. Nitrate concentrations were comparable between the algal pore water and water column in the winter and fall but algal pore nitrate concentrations were lower in the spring and higher in the summer relative to the water column. Phosphate concentrations were comparable between the algal pore water and water column during all seasons and phosphate was below detection in the fall and winter. Algal gross primary production (GPP; 0.31 g O2 m-2 d-1) and ecosystem respiration (ER; 0.31 g O2 m-2 d-1) was ~10x lower than water column GPP (3.22 g O2 m-2 d-1) and ER (3.21 g O2/m-2 d-1). Algae and water column NEP varied seasonally and reflected the differential spatial scales as the microbial community was more closely associated with algae. Overall algal GPP contributed ~ 13 % of total ecosystem production, though multiple regressions did not show that algal GPP or ER contributed to water column GPP. Although algal production did not directly influence water column metabolism, algal 4 biomass and algal dissolved oxygen as well as total organic carbon concentrations did influence water column metabolism. These data provide insight on algal production influence on ecosystem process rates via physiochemical changes in the environment. Further, these findings show that even in nutrient saturated systems, algae influence the water column through changes in physiochemical changes. 5 Introduction Primary production and respiration are metrics used to quantify metabolism (Odum 1956) to indicate biotic activity which varies based on community structure (Cummins 1974). Biotic communities are also influenced by surrounding landscape which can contribute allochthonous or autochthonous substrates for metabolism which can affect downstream ecosystem processes (Vannote et al. 1980, Odum and Barrett 2005). Allochthonous inputs are associated with small order and larger order streams whereas autochthonous inputs are generally associated with middle order streams. Small order streams typically yield low primary production as riparian vegetation restricts solar radiation available for photosynthesis resulting in a net heterotrophic ecosystem (Hill et al. 2001). Leaf litter also provides a carbon substrate for bacteria and fungi to contribute to respiration in smaller order streams (Petersen and Cummins 1974, Hieber and Gessner 2002). In larger order streams, increased depth and allochthonous inputs of accumulated materials from upper reaches (i.e., sediments) reduce light penetration and benthic substrate which supports respiration rates that can exceed primary production (Vannote et al. 1980, Chapin et al. 2002). Metabolism shifts from a net heterotrophic ecosystem in small and larger order systems towards a net autotrophic ecosystem in middle order reaches. Less canopy cover allows for increased light and primary production providing autochthonous sources of carbon into the stream (Webster et al. 1995). Benthic algae are dominant primary producers in middle order streams (Stevenson et al. 1996) and their influence on stream biogeochemistry changes with the diurnal patterns of production (Odum 1956, Roberts et al. 2007). During the day, photosynthesis increases stream dissolved oxygen concentrations (Mulholland et al. 2005) as well as pH (Talling 1976, Revsbech et al. 1983) and nutrient concentrations (Fig. 1; Kaplan and Bott 1982, Johnson and Tank 2009) 6 which all decrease to baseline levels at night. Algal production regulates nutrient cycling through assimilation of inorganic nutrients (removal from the water column) and release of nitrogen and carbon exudates (loss to the water column). Though nutrient assimilation by algae in streams is well understood (Bertilsson and Grace 2003), understanding of the factors influencing algal nutrient release is limited. Algal nutrient release represents a significant gap in our understanding of ecosystem dynamics, especially in nutrient saturated streams (Harbott and Grace 2005, Wiegner et al. 2005). Streams are becoming increasingly eutrophic with anthropogenic contaminants from agriculture and urbanization (Carpenter et al. 1998, Lewis et al. 2011) which can increase algal production (Blum 1956, Francoeur 2001), biomass (Stevenson 1997) and subsequently alter ecosystem processes and trophic interactions (Power 1992). Therefore, understanding how algae influence biogeochemistry can provide insight in predicting future responses in terms of heterotrophic metabolism, nutrient cycling and food web dynamics with anticipated changes in the environment. The goal of this research was to understand how algal production influenced algal and ecosystem metabolism in a mid-order stream through diurnal and seasonal changes in the physiochemical environment. Research was guided by specific questions and related hypotheses including: 1) How does algal production influence diurnal and seasonal patterns of oxygen and pH within an algal biofilm relative to the water column?; and, 2) How does algal production influence nutrient concentrations within algal pore water relative to the water column? We hypothesized that diurnal dissolved oxygen (DO) and pH within the algal biofilm would increase (Fig.1) with algal production and algal biofilm patterns in DO and pH would be consistent with water column patterns. We hypothesized that seasonal algal and water column DO patterns 7 would not be similar (Fig. 2) as algal production increased during the summer and decreased during the winter. We further hypothesized that as algal production increased with sunlight, algal pore water nutrient concentrations would also increase (Fig. 1) due to exudate release and this would not be consistent with nutrient concentrations in the water column as labile exudates released during photosynthesis would be quickly assimilated. We hypothesized that algal and water column nutrient concentrations would differ in the spring and summer but be comparable in fall and winter (Fig. 2). Specifically, we hypothesized that algal pore water concentrations would decrease relative to the water column in the spring with increased assimilation and algal pore water would increase relative to the water column in the summer with algal senescence releasing exudates. Methods Study Site Sampling was conducted in the White River, a 3rd order stream in Yorktown, Indiana, part of the Upper White River Watershed. The White River at Yorktown was selected for the presence of filamentous green algae attached to cobbles on the benthos throughout the year. Agricultural and urban activities including combine sewer overflows (CSOs) have contributed to high nitrogen concentrations within this sub-watershed (UWRWA 2011). As of 2011, this subwatershed was composed of 51.8% agriculture, 25.4% herbaceous, 15.0% urban, 5.2% forest, 1.9% wetland and 0.8% open water (UWRWA 2011). Field Sampling The White River was sampled monthly over 72 h events for one year (n = 12 sampling events: January 2013 – December 2013). During each event, algae and water column 8 physiochemical characteristics were recorded at 10 minute intervals using microelectrodes inserted into a filamentous green algae mat and a Hydrolab minisonde placed in a well-mixed portion of the water column. Water column and algal pore water samples were also collected every 3 h (except between 0000 and 0600) for measurement of nutrient concentrations (n = 6 water column and pore water samples per 24 h event). Stream width (m), depth (m), velocity (m/s), and discharge (m3/s) were also measured monthly. The width (m) of the stream was measured using metric tape followed by measurement of velocity using a Marsh-McBirney flow meter at 5 equidistant points across the width to measure depth (m) and velocity (m/s). Discharge (m3/s) was estimated by multiplying the width (m), mean depth (m) and mean velocity (m/s). Benthic algal biomass was collected using a 5.08 cm diameter PVC cylinder to isolate a known area (0.002 m2) and the algae within that area was scraped off of the cobble and placed into an individual container with 50 mL of stream water. Five samples per month were collected from five separate cobbles covered with filamentous green algae mats. Samples were placed on ice in the dark for transport and then placed in a drying oven (60˚C) and subsequently weighed (Stevenson and Bahls 1999). For benthic substrate characterization, the stream reach was divided into a 10 x 10 transect scaled by the width of the stream so there were 10 equidistant transects along the width and length of the stream which yielded 100 quadrants to describe the substrate (leaf, cobble or algae) present on the benthos. The percent substrate cover was calculated as: Substrate Cover (%) 100 of adrants ith s 100 Algae Physiochemical Measurements 9 strate (leaf co adrants le or algae) Measurements of in situ algae pH and dissolved oxygen were conducted using Clark-type microelectrodes (OX –N and pH –N, Unisense, Aarhus N, Denmark) connected to an UnderWater Meter system with external battery pack for 72 h of continuous data collection at 10 minute intervals. Microelectrodes were calibrated 1-3 d prior to and following each field sampling event. Oxygen microelectrodes were calibrated using a 6-point calibration curve derived from microelectrode response (mV) paired with known oxygen concentrations (mg O2 L1 ) from a hand-held dissolved oxygen meter (YSI, DO200). Oxygen concentrations were manipulated with O2 and N2 bubbling in tap water ranging from approximately 3 - 16 mg O2 L-1. Buffer solutions (4.00, 7.00 and 10.00) were used to calibrate the pH microelectrode; the mV response was compared to a pH measured using a hand-held meter (Extech, pH200). Calibration curves were created using linear regressions to represent the relationship between the microelectrode response and the known concentration or unit. All linear regressions had an r2 of 0.85 or above. During each sampling event, microelectrodes were positioned in the stream over a filamentous green algae mat attached to cobble in the benthos. Two dissolved oxygen and one pH microelectrode were suspended at approximately the same level using a custom four-way microelectrode clamp attached to a Unisense micromanipulator stand which was placed downstream in relation to the algal mat. The microelectrodes were inserted approximately 5 mm into the interior of the algal mat and programmed to log every 10 minutes for 72 h. Microelectrodes were checked every ~3 h to remove any debris (e.g., leaves, sticks, macrophytes). Microelectrode data were collected in mV and subsequently converted to mg O2 L-1 and pH units using the combined pre- and post- calibration curves. 10 Water Column Physiochemical Measurements A Hydrolab minisonde was deployed in a well-mixed portion of the water column ~10 m upstream from the microelectrodes in a region with no visible algal mats. The Hydrolab minisonde was equipped with a Luminescent Dissolved Oxygen (LDO) sensor for measurement of water column dissolved oxygen (mg L-1) temperat re (˚C) specific cond ctivity (μS/cm) and pH every 10 minutes for the 72 h duration. Dissolved oxygen concentration was calibrated according to manufacturer instructions prior to each sampling event. Metabolism Calculations Algae and water column metabolism including gross primary production (GPP), ecosystem respiration (ER) and net ecosystem production (NEP) were calculated using the nighttime regression method (Owens 1974, Hornberger and Kelly 1975, Young and Huryn 1999). Diurnal oxygen curves (24 h) for the algae and water column were selected for each sample month (n = 1 - 3) for a total of 65 diurnal curves. Temperature data coupled with the selected dissolved oxygen diurnal period was used to determine dissolved oxygen saturation. Since temperature was only logged in the water column it was also used in calculating the dissolved oxygen saturation for the algae. Before quantifying metabolism in the water column and algae, a reaeration coefficient was calculated to adjust for oxygen diffusion. To quantify K, raw data were used to quantify changes from saturation and change in dissolved oxygen concentration over time as described below. Dissolved oxygen concentration at saturation ( ) was calculated based on temperature and barometric pressure. Change in the concentration of dissolved oxygen over 10 minutes was determined( ). Change in measured dissolved oxygen concentration from the calculated dissolved oxygen concentration at saturation was 11 calculated for each interval( ). To determine the rate of change in dissolved oxygen, the difference in concentration ( ) was divided by the 10 min interval ). This rate of change ( ) was plotted against the dissolved oxygen period( concentration change from saturation ( ) during nighttime hours only which were considered sunset to sunrise. A linear regression was used to represent the relationship between the rate of dissolved oxygen change and deviation from saturation. The slope of the linear regression equation served as the reaeration coefficient (K). The reaeration coefficient was then incorporated into equations to quantify NEP, GPP and ER for the algae and water column each month. NEP, mg O2 L-1 ( ( )) GPP, mg O2 L-1 [ ( )] [(( ) ( ))( )] ER, mg O2 L-1 Units for these calculations were adjusted so the metabolism estimates were expressed as g O2 m2 d-1. The change in units incorporated the depth of the algae or water column in meters. The depth of the algae was estimated when adjusting the microelectrode depth in the interior of the algal mat. The depth of the algal mat varied temporally (average depth = 0.02 m). Nutrient Concentrations Water samples for nutrient analyses from both the water column and algal pore water were collected every 3 h during the 72 h sampling event. All water samples collected were filtered on site using a syringe filter containing a 25 mm Whatman glass fiber filter (GF/F; 0.7 micron pore size) in 20 mL high density polyethylene (HDPE) scintillation vials. All samples for 12 total organic carbon analysis were immediately acidified with 2 drops of 1.0 N HCl to inhibit microbial activity and convert all inorganic forms of carbon to carbon dioxide gas. All samples were then placed on ice and frozen for subsequent analyses. Algae pore water samples were collected using individual 5 mL syringes. Each 5 mL sample was collected directly above the surface of the algae to collect the biofilm pore water and each sample came from a different algal mat. Three 5 mL syringes were then filtered into each scintillation vial for a composite sample totaling 15 mL and 8 vials total. Four composite scintillation vials were used for nutrient analyses and four composite scintillation vials were acidified for total organic carbon analysis. Water column samples were collected using four 60 mL syringes at equidistant points across the width of the stream. Each 60 mL syringe was divided among two scintillation vials resulting in eight 20 mL scintillation vials. Four scintillation vials were used for nutrient analyses and four scintillation vials were acidified for total organic carbon analysis. Nutrient Analysis Nitrate (NO3) and phosphate (PO4) concentrations were measured for all samples with analytical duplicates on a Dionex ion chromatograph (Dionex Corporation, Sunnyvale, California) using standard methods (Eaton et al. 2005). Detection limits were 0.01 mg L-1 NO3 and 0.01 mg L-1 PO4. Ion concentrations below detection were reported as zero. Total organic carbon concentrations were measured for all samples with a Shimadzu TOC-L analyzer (Shimadzu Scientific Instruments, Columbia Maryland) using standard methods (Eaton et al. 2005). Water column samples were analyzed using analytical duplicates. However, because of 13 the large volume (40 mL) needed for TOC analysis, algal pore water samples were analyzed as composite samples for each time point. Ammonium (NH4) concentrations were quantified using the phenylhypochlorite spectrophotometric technique on selected water column and algal pore water samples representative of each season (April, July, October and December; APHA 1995, Aminot et al. 1997). Samples were analyzed on a spectrophotometer (UV-1700 PharmaSpec, Shimadzu) at 650 nm. The a sor ance val es ere then converted to μg NH4 L-1 using a standard curve of ammonium chloride (NH4Cl) absorbance. The NH4 detection limit as 0.1 μg L-1 NH4. Statistics Independent variables for one-way analysis of variance (ANOVA) and paired t-tests were used for assessing differences in net ecosystem production (NEP), gross primary production (GPP), ecosystem respiration (ER), total organic carbon (TOC), nitrate (NO3), phosphate (PO4), ammonium (NH4), dissolved oxygen (DO) and pH among months and between the water column and algae. In addition to these independent variables, Pearson correlation statistics also incorporated temperature, conductivity, discharge, flow, width, water column depth, algae depth and algal biomass to identify related factors. Multiple regression analyses were also used to identify the independent variables that influenced variation of GPP and ER from the water column and algae individually. All statistical tests were performed with Minitab 16.2.4. Results Algae and water column diurnal variation 14 Dissolved oxygen and pH varied diurnally in both the algae and water column (Fig. 3) and the amplitude of the measurement varied seasonally. July DO concentrations in the algae (range = 3.54 – 15.88 mg L-1) and water column (range = 4.74 – 9.97 mg L-1) were comparable at night but algal primary production increased the DO concentration during the day to ~ 6 mg L1 higher than the water column DO concentration. In contrast, water column DO concentrations peaked during the day and were consistently 9 – 12 mg L-1 higher than the algal DO concentrations in December. July pH in the algae (range = 7.70 – 8.30) and water column (range = 8.89 – 9.25) as well as December pH in the algae (range = 7.87 – 8.71) and water column (range = 9.38 – 9.77) differed by ~ 1 pH unit and followed the diurnal variation of DO. Overall, pH was highest during the day and lowest during the night. Physical characteristics Temperature varied temporally (Table 1) with the lowest temperature in the winter months (Decem er mean = 1.37 ˚C) and the highest temperat re the s mmer months (J ne mean = 23.19 ˚C). Cond ctivity as lo est in the inter and early spring (March 448.20 μS cm-1) and highest in the fall (Octo er 1225.40 μS cm-1). Algal depth varied from 0.015 m to 0.03 m with a mean depth of 0.02 m. Algal biomass was highest in March (214.1 gdm m-2) and lowest in June (26.2 gdm m-2) following a flood event. The width of the stream was greatest (21 m) from January to April and decreased in the spring to ~17 m through the summer, decreasing into fall (~15 m). Flow was lowest in the late summer and fall (0.27 – 0.38 m s-1) and highest in in the late winter and spring (0.70 – 1.03 m s-1). Discharge was calculated from the depth, width and flow (range = 1,190 – 12,220 L s-1). 15 Flow correlated positively with depth (R = 0.76, p < 0.01). However, flow negatively correlated with algal depth (R = -0.74, p < 0.01). Temperature negatively correlated with stream depth (R = -0.62, p = 0.03). Algal biomass negatively correlated with temperature (R = -0.582, p = 0.05). Algal dynamics Algal dissolved oxygen (DO) concentration varied seasonally (p < 0.001; range = 4.73 – 9.57 mg L-1; Table 1). Dissolved oxygen concentrations in the algae decreased in the fall beginning in September (mean = 6.02 mg L-1) with the lowest concentration measured in December (min = 3.00 mg L-1). Dissolved oxygen concentrations also increased in the spring with a shift from February (mean = 6.26 mg L-1) to March (mean = 8.05 mg L-1). Algal pH (Table 1) ranged from 7.75 – 8.65 being lowest from May to September (mean = 7.99) and highest from October to April (mean = 8.49). Algal pore water TOC concentrations did not vary seasonally (p = 0.09; range = 4.26 – 7.33 mg L-1; Table 2). Algal pore water TOC concentrations was highest in March and April (mean = 7.26 – 7.33 mg L-1). In contrast, algal pore water NO3 concentrations did vary seasonally (p < 0.01; 5.02 – 75.95 mg L-1; Table 2). Specifically, algal pore water NO3 concentrations were highest in June (mean = 75.95 mg L-1) and July (mean = 73.19 mg L-1) relative to winter measurements (mean = 5.02 mg L-1). Algal pore water PO4 concentrations varied seasonally (p < 0.01; range= BDL – 29.30 mg L-1; Table 2) being higher in the summer (range = 7.87 – 29.30 mg L-1) relative to fall and winter measurements (range = BDL – 1.34 mg L-1). In contrast, algal pore water NH4 concentrations did not vary seasonally (p > 0.05; range = 4.20 – 5.22 μg L-1; Table 2). 16 Water column dynamics Water column DO concentrations varied seasonally (p < 0.001; range = 6.78 – 15.5 mg L1 ; Table 1) with the lowest concentrations in August and highest concentrations in December. Water column pH also varied seasonally (p < 0.001; range = 8.88 – 9.73; Table 1). Specifically, water column pH was lowest from May to November (mean = 9.09) and was highest from December to April (mean = 9.50 mg L-1). Water column TOC concentrations (p < 0.01; range = 2.89 – 8.38 mg L-1; Table 2) were highest in June following a storm event and lowest in January. Water column NO3 concentrations also varied seasonally (p < 0.01; range = 4.59 – 90.14 mg L-1; Table 2)being highest in March (mean = 90.14 mg L-1) and June (mean = 76.14 mg L-1) relative to December measurements (mean = 4.59 mg L-1). Water column PO4 concentrations were highest in the summer (range = 8.34 – 30.18 mg L-1) relative to fall and winter measurements (range = BDL – 1.79 L-1) (p < 0.01; range = BDL – 30.18 mg L-1; Table 2). In contrast, water column NH4 concentrations did not vary seasonally (p = 0.08; range = 2.44 – 5.03 μg L-1; Table 2). Relationships between the algae and water column Algae and water column DO concentrations were negatively correlated (R = -0.398, p = 0.20; Fig. 4) whereas algae and water column pH were positively correlated (R = 0.696, p = 0.01; Fig. 5). There was a seasonal shift in the relationship between water column and algal DO concentrations. Specifically, water column DO concentrations were highest in the winter when algal DO concentrations were low (p < 0.01). This relationship shifted in the spring as algal DO concentrations increased and water column DO concentrations decreased, likely associated with 17 primary production and increasing temperatures, respectively. Algal DO concentrations were significantly lower than water column DO concentrations from October – May (p = 0.09) while algal DO concentrations were comparable to water column DO concentrations for June – September (p = 0.61). In contrast, algal pH was significantly different from water column pH across all months (p < 0.01). As water column DO concentrations increased, temperature decreased (R = -0.90, p < 0.01). Water column DO concentrations increased with algal biomass (R= 0.667, p = 0.02). In contrast, there was not a relationship between algal DO concentrations and algal biomass (R = 0.200, p = 0.532). As water column pH (R = -0.863, p < 0.01) and algal mat pH (R = -0.758, p < 0.01) increased, temperature decreased. Water column DO increased with water column pH (R = 0.841. p < 0.01). Across sampling events, there was no difference between algal pore water and water column PO4 concentrations (p > 0.05; Fig. 8). However, algal pore water NO3 concentrations were 16 – 26 % higher in July and August relative to the water column (Fig. 7). Additionally, algal pore water TOC concentrations were 20 – 60 % higher than water column TOC concentrations (Fig. 6) from January through April (p = 0.003 – 0.059) and in October (p = 0.04). While algal pore water and water column NH4 concentrations were comparable in April, July and October (p > 0.05), in December algal pore water NH4 was 49 % higher than water column NH4 concentrations (p = 0.02). As water column TOC concentrations increased, temperature also increased (R = 0.570, p = 0.05).and water column DO concentrations decreased (R = -0.548, p = 0.07). Water column NO3 concentrations increased with water column NH4 (R = 0.951, p = 0.05). Additionally, algal pore water NO3 concentrations increased with water column NH4 concentrations (R = 0.946, p = 18 0.05) as well as water column NO3 concentrations (R = 0.870, p < 0.01). Water column PO4 concentrations increased with temperature (R = 0.671, p = 0.02) and decreased with stream depth (R = -0.678, p = 0.02), consistent with algal pore water PO4 concentrations. Algal and ecosystem metabolism Algal gross primary production (GPP) varied seasonally (p < 0.01; range = 0.005 – 2.16 g O2 m-2 d-1; Fig. 9a). Algal GPP was highest in August and lowest in January. Water column GPP also varied seasonally (p = 0.01; range = 1.27 – 6.15 g O2 m-2 d-1; Fig. 9a) being highest in June and lowest in January. Algal and water column GPP were similar in January, March, and June (p > 0.05) but differed in February, April, May, and July through December (p = 0.01 – 0.03). Water column GPP was consistently 101 – 198 % greater than algal GPP except in August when water column GPP was only 10 % greater than algal GPP. While water column GPP was consistently higher than algal GPP, the contribution by algae to the ecosystem production varied seasonally. Relative to water column GPP, algae contributed the lowest amount of GPP in the winter (< 1 %) and the highest amount in the summer (41 %). Overall, algal GPP contributed ~13 % of production to the water column GPP. Algal ecosystem respiration (ER) varied seasonally (p < 0.01; range = 0.02 – 2.17 g O2 m-2 d-1; Fig. 9b). Algal ER was highest in August and lowest in February. Water column ER also varied seasonally (p < 0.01; range = 1.09 – 5.71 g O2 m-2 d-1; Fig. 9b) being highest in April and lowest in January. Algal and water column ER were similar in March and June (p > 0.05) but differed in January, February, April, May and July through December (p > 0.01 – 0.05). Water column ER was consistently 108 – 196 % greater than algal ER except in August when water column ER was only 14 % greater than algal ER. While water column ER was consistently 19 higher than algal ER, the contribution by algae to the ecosystem varied seasonally. Relative to water column ER, algae contributed the smallest amount of ER in the winter (~ 1 %) and the highest amount in the summer (39 %). Algal NEP was highest in March and lowest in August (p < 0.01; range = -0.02 – 0.09 g O2 m-2 d-1; Fig. 9c). Water column NEP also varied seasonally (p < 0.01; range = -0.36 – 0.86 g O2 m-2 d-1; Fig. 9c) and was highest in June and lowest in October. Algal and water column NEP differed in March, July, October and November (p = 0.01 – 0.03). Algal GPP increased with algal ER (R = 0.999, p < 0.01). Algal mat GPP (R = 0.677, p = 0.02) and algal mat ER (R = 0.665, p = 0.02) both increased with algal DO concentrations. Algal GPP (R = 0.534, p = 0.07) and algal ER (R = 0.541, p = 0.07) increased with water column PO4. Water column GPP increased with water column (R = 0.988, p < 0.01). Water column GPP (R = 0.813, p < 0.01) and water column ER (R = 0.821, p < 0.01) increased with water column TOC. Water column GPP (R = 0.493, p = 0.10) and water column ER (R = 0.526, p = 0.08) also increased with algal TOC concentrations. Water column GPP (R = -0.987, p < 0.01) and water column ER (R = -0.970, p = 0.03) increased with decreased in water column NH4 concentrations. Water column GPP was influenced by water column ER, algal biomass, algal and water column DO concentrations and water column pH (R2 = 99.87, S = 0.0834). Several covariates were consistent with the correlation analysis including water column ER and water column DO concentrations. Water column pH did not correlate directly with water column GPP but it did with water column DO concentrations. Algal biomass also helped explain some of the variation which suggested that it had an indirect effect as it correlated with water column DO concentrations which also influenced water column GPP. Water column ER was influenced by water column GPP, algal and water column TOC concentrations (R2 = 99.12, S = 0.1690). These 20 covariates were consistent with correlation analyses. Algal GPP was influenced by algal ER and algal biomass (R2 = 99.88, S = 0.0258). Algal ER was influenced by algal GPP and algal biomass (R2 = 99.85, S = 0.0255). Algal biomass did not correlate directly with algal GPP or ER but suggested an indirect effect. Discussion These findings provide an account of the influence of algal production on stream physiochemical characteristics, nutrient concentrations, and metabolism at diurnal and seasonal scales in a eutrophic stream. The study site selected was representative of one of the most degraded watersheds in the United States (UWRWA 2011) and the results should be considered in the context of a high nutrient system. In this nutrient saturated system, algal production influenced water column physiochemical variation and contributed only a small portion (~ 13 %) of total ecosystem production with the highest contribution in the summer. This contrasted the idea that open-canopy systems have primary production contributions to total ecosystem production > 50 % (Minshall 1978) in undisturbed streams. Therefore nutrient saturated systems may limit the influence primary producers have on total ecosystem production but the autochthonous sources are detectable even with large contributions from allochthonous sources. Alternatively, other primary producers (e.g., macrophytes) may contribute a significant amount of production in some ecosystems. Factors influencing algae and water column metabolism Although algal metabolism (GPP and ER) did not directly influence water column metabolism components, algal biomass, DO and TOC concentrations (mediated by algal 21 metabolism) did influence water column metabolism estimates. Algal biomass and DO concentrations influenced water column GPP while algal TOC concentrations influenced water column ER. Algal biomass was also found to be an important driver of ecosystem GPP in a multi-regional study (Bernot et al. 2010) and in a forested headwater stream (Roberts et al. 2007). In contrast to our study, algal dissolved oxygen concentrations have not been related to ecosystem metabolism in the literature. Perhaps this is because diurnal dissolved oxygen concentrations from algal biofilms are not typically collected and therefore not incorporated into regression models. If algal DO concentrations were exempt from the model, in this study PO4 concentrations from both the algae and water column in addition to biomass and water column TOC concentrations would explain 96 % of the variation in water column GPP. This is consistent with a multi-regional study (Mulholland et al 2001) where PO4 concentrations influenced water column GPP. Water column ER was driven by algal and water column TOC which was consistent with another multi-regional study (Bernot et al 2010) where these covariates explained variation in water column ER. Estimates of water column GPP and ER in the current study (GPP: 1.27 – 6.15 g O2 m-2 d-1, mean = 3.22 g O2 m-2 d-1; ER: 1.09 – 5.17 g O2 m-2 d-1, mean = 3.21 g O2 m-2 d-1) and algal GPP and ER (GPP: 0.005 – 2.16 g O2 m-2 d-1, mean = 0.31 g O2 m-2 d-1; ER: 0.02 – 2.17 g O2 m-2 d-1, mean = 0.31 g O2 m-2 d-1) are comparable to values reported in a variety of studies with different land uses. Water column metabolism estimates were similar to values reported with catchments that included pastures (GPP: 1.26 -3.68 g O2 m-2 d-1; ER: 2.02 – 2.68 g O2 m-2 d-1, Young and Huryn 1999), agriculture (mean GPP: ~ 4 g O2 m-2 d-1; mean ER: ~6 g O2 m-2 d-1, Bernot et al. 2010) and urbanization (mean GPP: 3.5 g O2 m-2 d-1; mean ER: 4.2 g O2 m-2 d-1, Pennino et al. 2014). Water column and algal metabolism estimates also both fell within the 22 bounds of estimates from an agriculturally influenced stream (GPP: 0.1 – 6.2 g O2 m-2 d-1; ER: 0.05 – 6.8 g O2 m-2 d-1, Frankforter et al. 2010). Our water column metabolism estimates were different compared to a low nutrient, geothermally regulated stream in Iceland which had a wide range of estimates (GPP: 2 – 28 g O2 m-2 d-1; ER: 3 - 67 g O2 m-2 d-1, Demars et al. 2011) but the upper range for both GPP and ER were 5 to 10 times higher than our maximum estimates. This suggests that low nutrient systems may be more productive relative to high nutrient systems. Water column NEP showed that the stream in the winter was autotrophic likely due to the open canopy as well as the removal of leaf litter from the benthos allowing more production, consistent with previous assessments (Roberts et al. 2007). Algal biomass was higher in the colder months; therefore, winter production may have been influenced more by total biomass, skewing production estimates. The lower temperature in the winter also decreased microbial activity which may have contributed to the P: R > 1 which was similar to the decrease in metabolism observed at colder temperatures in Iceland streams (Demars 2011). In spring, production was equal to respiration however the ecosystem became slightly autotrophic in the summer (P: R > 1). This suggested that the autotrophs and heterotrophs were releasing and assimilating at similar rates (Søndergaard et al. 1995). In the fall, the ecosystem was heterotrophic likely due to leaf litter inputs which increased the microbial activity (Petersen and Cummins 1974). Algal NEP indicated net heterotrophy in the fall, winter, and spring. This was likely due to the close association between the microbial community and the algae (Søndergaard et al. 1995). In the fall, microbial activity likely increased due to litter fall and decreased primary production (Petersen and Cummins 1974). In the winter and spring the microbial community 23 could quickly assimilate the exudates released from the algal mat. In the summer, algal NEP was autotrophic, likely due to primary production as well as algal senescence which released exudates for metabolism (Fogg 1983). Overall, these variations in NEP between the water column and algae reflect the spatial scales at which these measurements were collected. The microbial community was not coupled as tightly with the water column as it was to the algae in the benthos. Factors influencing algae and water column physiochemical variation On a diurnal scale, algal production consistently increased DO and pH during the day and decreased during the night within the algal mat, consistent with hypotheses and likely attributable to photosynthesis similar to diurnal patterns in an algal mats previously observed (Revsbech et al. 1983,Talling 1976). Water column DO concentrations also increased during the day and decreased during the night with similar amplitude to measurements collected in a headwater stream before leaf out in March (Roberts et al. 2007) and April (Mulholland et al. 2001). Due to diffusion limits, temperature is negatively correlated with DO, consistent with observations in the water column but not the algae. Thus, algal DO concentrations may be more associated with biological processes, for example, metabolism decreases with cold temperatures. Therefore similar to Demars et al. (2011) where metabolism decreased with temperature, algal dissolved oxygen concentrations would also decrease with decreasing temperature as it fuels metabolism. Temperature correlated negatively with algal biomass which would suggest that although algal abundance increases with decreasing temperature, algae are more efficient in summer months. 24 Factors influencing algae and water column nutrient concentrations Water column dissolved nutrient concentrations reflected the seasonal variability of nitrogen and phosphorus and the influences of agriculture and urbanization and were comparable to concentrations observed in the same watershed (Veach and Bernot 2011). Changes in algal pore water nutrient concentrations were consistent with seasonal patterns of production with assimilation in the spring and release in the summer (Mulholland and Hill 1997, Roberts et al. 2007). Even in this high nutrient system the influence of algae on nutrient concentrations was detectable. Although NO3 concentrations were elevated due to a storm event, relative to the water column, algal pore water had lower NO3 concentrations in spring likely due to assimilation. This decrease in stream nutrient concentrations in the spring has also been observed in headwater streams (Roberts et al. 2007) but at a different magnitude. We also observed an increase in algal pore water NO3 concentrations in the summer which was also consistent with trends observed in Roberts et al. (2007). Similar patterns in assimilation and release of nutrients in the spring and summer were found by Lee et al. (2012) though the highest concentrations of NO3 were measured during winter months in the Upper Mississippi River Basin, contrary to our observations. Algal biomass estimates for Lee et al. (2012) reported no algae in the winter which may have allowed NO3 to accumulate. In our study, NO3 concentrations were lowest in the winter likely a function of algal biomass assimilating available nutrients and changes in inputs from the surrounding watershed. Anthropogenic influences may have also affected NO3 and TOC concentrations through runoff associated with storms. The March storm event did not rise above flood stage and increases in TOC concentrations did not occur; however, NO3 concentrations were significantly higher. Nitrate is introduced to streams during storm events via tiles and subsurface flow while 25 organic carbon is commonly introduced via overland inputs (Wagner et al. 2008). The algae pore water had higher NO3 and PO4 concentrations in the summer relative to the water column, likely due to nutrient release from senescent algae (Bratbak et al. 1994). June sampling took place following a storm event that rose above flood stage and likely introduced a large amount of NO3 and organic carbon into the stream from agricultural and urban sources. Increased nitrate was consistent with David et al. (1997) and increased organic carbon concentrations in streams were consistent with Dalzell et al. (2005 and 2007) where allochthonous inputs were contributed to from agricultural fields and tiles following flooding events. Conclusions This study showed the influence algae have on water column physiochemistry, nutrients and metabolism. While physiochemical patterns were consistent between the algae and the water column, the amplitude of the changes varied as well as the contribution of algal-mediated shifts to the water column. These data also suggested that the microbial community was closely associated with the algae but not closely associated with the water column based on seasonal NEP. Algae contributed ~ 13 % to total ecosystem production. Algal contributions were detectable but not consistent with previous studies (Minshall 1978) as they were conducted in undisturbed streams. 26 References Aminot, A., D. S. Kirkwood, and R. Kerouel. (1997). Determination of ammonium in seawater by the indophenol-blue method: Evaluation of the ICES NUTS I/C 5 questionnairre. Marine Chemistry. 56:59-75. APHA. (1995). Standard Methods for the Examination of Water and Wastewater. 19th edition. American Public Health Association, Washington, D.C. Bernot, M. J., Sobota, D. J., Hall, R. O., Mulholland, P. J., Dodds, W. K., Webster, J. R., Tank, J. L., Ashkenas, L. R., Cooper, L. W., Dahm, C. N., Gregory, S. V., Grimm, N. B., Hamilton, S. K., Johnson, S. L., McDowell, W. H., Meyer, J. L., Peterson, B., Poole, G. C., Valett, H. M., Arango, C., Beaulieu, J. J., Burgin, A. J., Crenshaw, C., Helton, A. M., Johnson L. Merriam J. Niederlehner B. R. O’Brien J. M. Potter J. D. Shei ley R. W., Thomas, S. M. and K. Wilson. (2010), Inter-regional comparison of land-use effects on stream metabolism. Freshwater Biology, 55: 1874–1890. Bertilsson, S., and J.B. Jones. (2003). Aquatic Ecosystems: Interactivity of Dissolved Organic Matter: Interactivity of Dissolved Organic Matter. pp. 3-19 in Findlay & Sinsabaugh (eds.) Supply of dissolved organic matter to aquatic ecosystems: autochthonous sources. Academic Press. 496p. Blum, J. L. (1956). The ecology of river algae. The Botanical Review, 22(5), 291-341. Bratbak, G., Thingstad, F., and M. Heldal. (1994). Viruses and the microbial loop. Microbial Ecology, 28(2), 209-221. Carpenter, S. R., Caraco, N. F., Correll, D. L., Howarth, R. W., Sharpley, A. N., and V. H. Smith. (1998). Nonpoint pollution of surface waters with phosphorus and nitrogen. Ecological applications, 8(3), 559-568. Chapin III, F.S. , Matson, P.A., and H.A. Mooney. (2002). Principles of Terrestrial Ecosystem Ecology. 2nd ed. New York: Springer-Verlag. 529p. Cummins, K. W. (1974). Structure and function of stream ecosystems. BioScience, 24(11), 631641. Dalzell, B. J., Filley, T. R., and J.M. Harbor. (2005). Flood pulse influences on terrestrial organic matter export from an agricultural watershed. Journal of Geophysical Research: Biogeosciences, (2005–2012), 110(G2). 27 Dalzell, B.J., T.R. Filley, and J.M. Harbor, (2007). The role of hydrology in annual organic carbon loads and terrestrial organic matter export from a midwestern agricultural watershed. Geochimica et Cosmochimica Acta, 71:1448-1462. David, M. B., Gentry, L. E., Kovacic, D.A. and K. M. Smith. (1997). Nitrogen balance in and export from an agricultural watershed. Journal of Environmental Quality, 26: 1038–1048 Demars, B. O., Russell Manson, J., Olafsson, J. S., Gislason, G. M., Gudmundsdottír, R., Woodward, G., Reiss, J., Pichler, D.E., Rasmussen, J.J. and N. Friberg. (2011). Temperature and the metabolic balance of streams. Freshwater Biology, 56(6), 11061121. Eaton, A. D., M. a. H. Franson, A. P. H. Associati, A. W. W. Association, and W. E. Federation. 2005. Standard methods for examination of water & wastewater: centennial edition. American Public Health Association. Francoeur, S. N. (2001). Meta-analysis of lotic nutrient amendment experiments: detecting and quantifying subtle responses. Journal of the North American Benthological Society, 20(3), 358-368. Frankforter, J. D., Weyers, H. S., Bales, J. D., Moran, P. W., and D. L. Calhoun. (2010). The relative influence of nutrients and habitat on stream metabolism in agricultural streams. Environmental monitoring and assessment, 168(1-4), 461-479. Fogg, G. E. (1983). The ecological significance of extracellular products of phytoplankton photosynthesis. Botanica Marina, 26(1), 3-14. Griffiths, N. A., Tank, J. L., Royer, T. V., Roley, S. S., Rosi-Marshall, E. J., Whiles, M. R., Beaulieu, J.J. and L. T. Johnson. (2013). Agricultural land use alters the seasonality and magnitude of stream metabolism. Limnology and Oceanography, 58(4), 1513-1529. Harbott, E. L., and M. R. Grace. (2005). Extracellular enzyme response to bioavailability of dissolved organic C in streams of varying catchment urbanization. Journal of the North American Benthological Society, 24(3), 588-601. Hieber, M., and M. O. Gessner. (2002). Contribution of stream detrivores, fungi, and bacteria to leaf breakdown based on biomass estimates. Ecology, 83(4), 1026-1038. 28 Hill, W. R., Mulholland, P. J., and E. R. Marzolf. (2001). Stream ecosystem responses to forest leaf emergence in spring. Ecology, 82(8), 2306-2319. Hornberger, G. M., and M. G. Kelly. (1975). Atmospheric reaeration in a river using productivity analysis. Journal of the Environmental Engineering Division,101(5), 729-739. Johnson, L. T., and J. L. Tank. (2009). Diurnal variations in dissolved organic matter and ammonium uptake in six open-canopy streams. Journal of the North American Benthological Society, 28(3), 694-708. Kaplan, L. A. and T. L. Bott. (1982). Diel fluctuations of DOC generated by algae in a piedmont stream. Limnology and Oceanography, 27(6), 1091-1100. Lee, K. E., Lorenz, D. L., Petersen, J. C., and J. B. Greene. (2012). Seasonal Patterns in Nutrients, Carbon, and Algal Responses in Wadeable Streams within Three Geographically Distinct Areas of the United States, 2007–08. US Geological Survey. Lewis Jr, W. M., Wurtsbaugh, W. A., and H. W. Paerl. (2011). Rationale for control of anthropogenic nitrogen and phosphorus to reduce eutrophication of inland waters. Environmental Science & Technology, 45(24), 10300-10305. Minshall, G. W. (1978). Autotrophy in stream ecosystems. BioScience, 28(12), 767-771. Mulholland, P. J. and W. R. Hill. (1997). Seasonal patterns in streamwater nutrient and dissolved organic carbon concentrations: Separating catchment flow path and in‐stream effects. Water Resources Research, 33(6), 1297-1306. Mulholland, P. J., Houser, J. N. and K. O. Maloney. (2005). Stream diurnal dissolved oxygen profiles as indicators of in-stream metabolism and disturbance effects: Fort Benning as a case study. Ecological Indicators, 5(3), 243-252. Mulholland, P. J. , Fellows, C. S. , Tank, J. L. , Grimm, N. B. , Webster, J. R. , Hamilton, S. K. , Martí, E. , Ashkenas, L. , Bowden, W. B. , Dodds, W. K. , Mcdowell, W. H. , Paul, M. J. and B. J. Peterson. (2001). Inter-biome comparison of factors controlling stream metabolism. Freshwater Biology, 46: 1503–1517. Odum, H. T. (1956). Primary production in flowing waters. Limnology and Oceanography,1(2), 102-117. 29 Odum, E.P. and Barrett, G.W. (2005). Fundamentals of Ecology. 5th ed. Belmont, CA: Thomson Brooks/Cole. 624p. Owens, M. (1974). Measurements on non-isolated natural communities in running waters.In A manual on methods for measuring primary production in aquatic environments.Edited by R.A. Vollenweider. Blackwell Scientific Publications, Oxford. pp. 111–119. Pennino, M. J., Kaushal, S. S., Beaulieu, J. J., Mayer, P. M., and C. P. Arango. (2014). Effects of urban stream burial on nitrogen uptake and ecosystem metabolism: implications for watershed nitrogen and carbon fluxes. Biogeochemistry. Petersen, Robert C., and K. W. Cummins. (1974). Leaf processing in a woodland stream. Freshwater Biology, 4: 343-368. Power, M. E. (1992). Top-down and bottom-up forces in food webs: do plants have primacy. Ecology, 73(3), 733-746. Revsbech, N. P., Jorgensen, B. B., Blackburn, T. H. and Y. Cohen. (1983). Microelectrode studies of the photosynthesis and O2, H, S, and pH profiles of a microbial mat. Limnology and Oceanography, 28(6), 1062-1074. Roberts, B. J., Mulholland, P. J., and W. R. Hill. (2007). Multiple scales of temporal variability in ecosystem metabolism rates: results from 2 years of continuous monitoring in a forested headwater stream. Ecosystems, 10(4), 588-606. Søndergaard, M., Hansen, B., and S. Markager. (1995). Dynamics of dissolved organic carbon lability in a eutrophic lake. Limnology and Oceanography, 40:46–54. Stevenson, R. J. (1997). Resource thresholds and stream ecosystem sustainability. Journal of the North American Benthological Society, 410-424. Stevenson, R. J. and L. L. Bahls. 1999. Periphyton protocols. In: M. T. Barbour, J. Gerritsen, & B. D. Snyder, eds. Rapid Bioassessment Protocols for Use in Wadeable Streams and Rivers: Periphyton, Benthic Macroinvertebrates, and Fish. Second Edition. EPA 841-B99-002 United States Environmental Protection Agency, Washington. pp 6-1 to 6-22. Stevenson, R. J., Bothwell, M. L., Lowe, R. L., and J. H. Thorp. (1996). Algal ecology: Freshwater benthic ecosystem. Academic press. Talling, J.F. (1976). The depletion of carbon dioxide from lake water by phytoplankton. Journal of Ecology, 64(1), 79-121. 30 Upper White River Watershed Alliance (UWRWA). (2011). http://www.uwrwa.org/. Accessed 12 April 2014. Vannote, R. L., Minshall, G. W., Cummins, K. W., Sedell, J. R., and C. E. Cushing. (1980). The river continuum concept. Canadian Journal of Fisheries and Aquatic Sciences, 37(1), 130-137. Veach, A. M., and M. J. Bernot. (2011). Temporal variation of pharmaceuticals in an urban and agriculturally influenced stream. Science of the Total Environment, 409(21), 4553-4563. Wagner, L.E., P. Vidon, L.P. Tedesco, and M. Gray, 2008. Stream nitrate and DOC dynamics during three spring storms across land uses in glaciated landscapes of the Midwest. Journal of Hydrology, 362:177-190. Webster, J. R., Wallace, J. B., and E. F. Benfield. (1995). Organic processes in streams of the eastern United States. River and Stream Ecosystems–Ecosystems of the World, 22, 117187. Wiegner, T. N., Kaplan, L. A., Newbold, J. D., and P. H. Ostrom. (2005). Contribution of dissolved organic C to stream metabolism: a mesocosm study using 13C-enriched treetissue leachate. Journal of the North American Benthological Society, 24(1), 48-67. Young, R. G. and A. D. Huryn. (1999). Effects of land use on stream metabolism and organic matter turnover. Ecological Applications, 9(4), 1359-1376. 31 Fig. 1 32 Fig. 2 33 Fig. 3 34 Table 1. 35 Table 2. 36 Fig. 4 37 Fig. 5 38 Fig. 6 Winter Spring Summer Fall 8 -1 Algae (mg TOC L ) 10 6 4 2 0 0 2 4 6 Water column (mg TOC L-1) 39 8 10 Fig. 7 Winter Spring Summer Fall -1 Algae (mg NO3 L ) 80 60 40 20 0 0 20 40 60 Water Column (mg NO3 L-1) 40 80 Fig. 8 30 Winter Spring Summer Fall -1 Algae (mg PO4 L ) 25 20 15 10 5 0 0 5 10 15 20 Water Column (mg PO4 L-1) 41 25 30 Fig. 9 42 Table. 3 43 CHAPTER 2: Influence of algal exudates and benthic substrata on microbial activity Abstract Benthic algae are important for ecosystem processes because they regulate nutrient cycling through assimilation of inorganic nutrients and release of nitrogen and carbon exudates through photosynthesis. Algal-derived dissolved organic matter (DOM) may facilitate microbial respiration in streams and thereby influence ecosystem metabolism. The objective of this study was to isolate mechanisms by which algae may stimulate microbial respiration in a eutrophic stream ecosystem. We hypothesized that microbial activity would increase in the presence of algae due to the release of labile exudates into the surrounding water during photosynthesis. We used experimental mesocosms with a factorial design to study interactions between algal treatments (actively growing algae, algal exudate, and control) and benthic substrates (leaves, sediment, cellulose sponge and fritted glass disc) over a 3 d period. We measured physiochemical variables and nutrient concentrations every 24 h and quantified microbial respiration as an indicator of microbial activity using dehydrogenase assays (DHA) after 3 days. Following incubation of mesocosms, dissolved nutrient concentrations varied among both algal treatments and benthic substrates. Specifically, algal exudate and leaf treatments yielded the highest total organic carbon concentrations. The algal exudate and leaf treatments also had lower nitrate and higher phosphate concentrations relative to other treatments and substrates. Respiration differed among carbon substrates but not algal treatments. We did not detect an effect of algae or algal exudate abundance on microbial respiration after 3 days, potentially due to rapid assimilation of exudates prior to our measurements. Leaf substrates yielded the highest rates of microbial respiration likely due to higher carbon availability associated with leachate. 44 Regardless of algal treatment, when TOC concentrations were > 8 mg /L, microbial respiration increased suggesting that carbon concentration does influence respiration. These data show the influence of algae and benthic substrates on microbial respiration in eutrophic environments and offer insight into the challenges of studying these complex systems. Continued study of microbial responses to algae and benthic substrates will help predict ecosystem responses with changing nutrient status as streams become eutrophic. 45 Introduction Primary production and decomposition are processes that occur in both terrestrial (Tansley 1935) and aquatic ecosystems (Lindeman 1942, Odum 1956) and can be used as a measure of ecosystem function (Vannote et al. 1980).Though much research has quantified primary production and decomposition independently (Singh and Gupta 1977, Cole 1982), recent studies have highlighted relationships between these processes (Baines and Pace 1991, Findlay et al. 1993, Bertilsson and Jones 2003, Hagen et al. 2012 ) that enhance our understanding of ecosystem dynamics and nutrient cycling. Specifically, attention has focused on the potential for primary prod ction to facilitate decomposition thro gh the “priming effect” (Bingemann et al. 1953). In the context, the priming effect occurs when labile carbon and nitrogen exudates are released from primary producers into the environment and serve as a catalyst for microbial activity (Bingemann et al. 1953, Kuzyakov et al. 2000, Guenet et al. 2010, Bianchi 2011) facilitating increased mineralization of carbon and nitrogen. The mechanisms by which photosynthetic products increase decomposition of organic matter was first observed in terrestrial ecosystems where the addition of plant material to soil increased nitrogen mineralization (Lohnis 1926). Our understanding of the priming effect has continued to develop in the terrestrial literature (Bingemann et al. 1953, Kuzyakov et al. 2000, Fontaine et al, 2003) although the phenomenon has not been extensively studied in aquatic ecosystems (but see Guenet et al. 2010, Bianchi 2011, Danger et al. 2013). This represents a significant gap in our understanding of primary production and decomposition as well as the important role the microbial community serves in mediating these processes. In mid-order streams, algae regulate nutrient cycling through assimilation of inorganic nutrients (Howarth 1988, Mulholland 1996) and release of carbon and nitrogen exudates 46 (Bertilsson and Jones 2003, Harbott and Grace 2005, Wiegner et al. 2005). While algal nutrient assimilation is well studied, understanding of algal nutrient and dissolved organic matter (DOM; also referred to as exudate) release is limited. Nutrient and DOM release by algae may play an important role in decomposition and may increase assimilation and mineralization of organic matter by microbial communities. There are many pathways in which algae release DOM into the environment. Fogg (1983) suggested that healthy algae become supersaturated with labile organic matter and actively release DOM via the extracellular membrane to continue assimilation of available nutrients. Alternatively, DOM can be released passively through the extracellular membrane and not controlled by photosynthesis as light availability has been shown to be independent of DOM release (Bertilsson and Jones 2003). Senescent algae may also contribute labile organic matter for use by heterotrophic microorganisms (Bratbak et al. 1994, Wyatt et al. 2014a). Additionally, algal material can be released into the environment via cell lysis during “sloppy” cons mption y grazers (J mars et al. 1989 Wallace and Webster 1996). All of these pathways may influence the amount of labile organic matter available to heterotrophic microbes which influences microbial activity (Bertilsson and Jones 2003) and subsequently influences decomposition rates (Cole 1982, Jones and Cannon 1986, Baines and Pace 1991). The nutrient status of the environment can also influence algal DOM release (Fogg 1983, Obernosterer and Herndl 1995, Wyatt et al. 2014b). In eutrophic environments, the influence of active algal cell exudate on heterotrophic activity may be higher relative to oligotrophic environments because biomass can be greater (Obernosterer and Herndl 1995, Wyatt et al. 2010, Wyatt et al. 2012) due to nutrient saturated primary production (Rosemond et al. 1993, Mosisch et al. 2001). In oligotrophic environments, primary production is nutrient limited; thus, the amount of DOM released may be lower as algae retain DOM for continued photosynthesis. In 47 contrast, primary production in eutrophic environments is not nutrient limited; thus, the amount of DOM released may be due to maintenance of photosynthesis and continued assimilation of available nutrients (Fogg 1983, Obernosterer and Herndl 1995). In oligotrophic systems, algal DOM release may be important to ecosystem processes but the amount of DOM released may be lower relative to eutrophic systems. Understanding the influence algal DOM may have on heterotrophic respiration will help predict future ecosystem response to changes in the environment. For example, streams are becoming increasingly eutrophic which can increase algal production and subsequently microbial activity which may influence decomposition rates and alter ecosystem processing of nutrients and organic matter. The objective of this study was to isolate mechanisms by which algal DOM facilitates microbial activity in the context of available substrates. To do this we used experimental mesocosms with a factorial design to study interactions between algae and algal exudates with organic (leaves, sediment or cellulose sponge) and inorganic substrates (glass fritted disc) by measuring microbial respiration as an indicator of microbial activity. We hypothesized that microbial activity would increase with algal production or algal exudates due to increased availability of labile DOM. Since the organic substrates contributed additional carbon and nutrients, we expected that microbial respiration on organic substrates would be higher relative to the inorganic substrate and we anticipated that the inorganic substrate would isolate the relationship between algae and the stream microbial community to provide a respiration baseline. Methods Experimental design 48 Four algal treatments (actively growing algae, senesced algae, algal exudates only and a control without algae or exudates) were applied to four substrates (sediment, leaves, organic cellulose sponge and a control inorganic glass fritted disc) in experimental mesocosms. Each algal treatment and benthic substrate factorial combination (N = 16 combinations) had 5 replicates except the inorganic substrate which had 6 replicates yielding a total of 84 mesocosms. Each mesocosm was individually aerated using air stones. Mesocosms were 500 mL clear glass jars filled with 300 mL of stream water collected from the White River in central Indiana. Filamentous algae and sediment were also collected from the White River for use in the experiment. Physiochemical measurements (mean SE) of the stream water including temperature (22.0 0.06°C), dissolved oxygen (8.01 0.07 mg/L) and pH (8.86 0.01) were collected over a 3 d sampling event in May 2013 prior to experimental set-up. Initial total organic carbon (4.05 0.32 mg/L; n = 64), nitrate (15.71 1.06 mg/L; n = 80) and phosphate (14.41 1.14 mg/L; n = 80) concentrations were also measured via collection of filtered water samples. Algal treatments Filamentous green algae were carefully removed from cobbles to serve as both the actively growing and senesced algae treatments following incubation in the laboratory. The algal samples were placed in Whirl-Paks (Nasco, Fort Atkinson, WI) filled with stream water on site and transported to the laboratory on ice in the dark where they were processed within 1 h. Algae were divided for actively growing and senesced algal treatments into two 10 gallon (37.8 L) aquaria for incubation (5 d). Both aquaria were filled with stream water from the White River and were kept at room temperature (22 °C) under constant (24 h) light conditions. The aquarium 49 for the actively growing algae treatments were incubated with air stones to prevent uptake rates of nutrients from exceeding mixing and diffusion rates (Stevenson and Glover 1993) and to promote CO2 exchange. The second aquarium for the senesced algae treatments were incubated without air stones to facilitate degradation of the algal material. We observed stream algae degrade rapidly in stagnant conditions in the senesced treatment, changing from dark green to brown during the incubation and visually different from the algae in the actively growing aquarium which appeared dark green in color. Following initial algal incubations, algae were transferred to experimental mesocosms. Each mesocosm received approximately 1 g (wet weight) of algae. The senesced algae treatments recovered quickly (~1 d) when transferred to mesocosms (changing from brown back to dark green). Algal exudates were collected by leaching filamentous green algae and freeze-drying the dissolved organic matter into a powder form (Shapiro, 1957, Beck et al., 1974). Approximately 4 L of stream ater as collected and filtered thro gh a 0.2 μm Vac Cap filter (Pall Corporation Port Washington, NY) to remove heterotrophic organisms before any algal material was collected for DOM leaching. Benthic filamentous green algae were collected from cobbles in the stream as described above and sediment and macroinvertebrates were removed prior to placing in Whirl-Paks (Nasco, Fort Atkinson, WI) with stream water for transport to the laboratory on ice in the dark. In the la oratory eight 1 L eakers ere filled ith 500 mL of 0.2 μm filtered stream water. The algal tissue collected was distributed evenly among the eight beakers. The beakers were placed under constant light conditions at room temperature (21 °C) for 12 h. Following the incubation, the water was strained to remove algal material and then the remaining water was filtered through a Millipore nitrocellulose member filter (Millipore Corporation, Billerica MA; nominal pore size 0.45 μm). The filtrate as collected in Erlenmeyer flasks and a 50 sample was taken to quantify the total organic carbon in the sample for yield estimates. The filtrate was then immediately lyophilized converting the dissolved organic matter into a powder form using a Labconco Freeze Dryer (Labconco, Kansas City, MO). The resulting filtrate served as the inoculum for the algal DOM treatment. Each treatment received a concentration of 10 mg/L of DOM. Throughout the 3 d incubation period, as water evaporated from mesocosms, stream water was refilled to the initial 300 mL volume. Stream water was used to refill all mesocosms except for the algal exudate treatments which were refilled with stream water enriched with 10 mg/L of DOM. Substrate treatments Three leaf types, American Elm (Ulmus americana), Black Walnut (Juglans nigra), and Sugar Maple (Acer saccharum) were used for the coarse particulate organic matter (CPOM) substrate. Healthy leaves were removed from tree limbs in May 2013 and then dried at 70°C overnight. The dried leaves were then placed in stream water for 3 d to be conditioned by the microbial community before being distributed among mesocosms. Three leaves, one of each type, weighing approximately 5 g, were placed into each leaf treatment mesocosm. River sediment (top ~0 - 5 cm of the benthic surface) from the original collection site was used for the fine particulate organic matter substrate. The sediment was homogenized using a No. 3 sieve. Approximately 1 g of sediment (wet weight) was distributed to each sediment treatment mesocosm. Cellulose sponges (diameter of 2.54 cm; 3M Corporation, St. Paul, Minnesota) were used for the artificial organic carbon substrate. One sponge (mean weight of 0.38 g) was placed in each sponge treatment mesocosm. Glass fritted discs (diameter of 2.54 cm; Leco Corporation, 51 St. Joseph, MI) were used for the inorganic carbon substrate. One glass disc, with a mean weight of 4.9 g, was placed in each glass (inorganic carbon) treatment mesocosm. Physicochemical measurements Once every 24 h over the 3 d experiment, measurements of dissolved oxygen (mg O2/L), temperature (°C) (YSI, DO200) and pH (Extech, pH200) from each mesocosm were recorded. Composite duplicate water samples from each mesocosm were collected at 24 h and 48 h to quantify total organic carbon and nutrient concentrations. High-density polyethylene scintillation vials were filled with water filtered through Whatman GF/F (0.7 μm nominal pore size) efore freezing for subsequent analyses. Samples for measurement of total organic carbon (TOC) concentrations were acidified with 1.0 N HCl immediately after filtration. All samples were frozen within 1 h of filtration. Nitrate (NO3), phosphate (PO4) and ammonium (NH4) concentrations were measured using a Dionex ion chromatograph (Dionex Corporation, Sunnyvale, California). Detection limits were 0.01 mg NO3/L, 0.01 mg PO4/L and 0.005 mg NH4/L. Total organic carbon concentrations were measured using a Shimadzu TOC-L analyzer (Shimadzu Scientific Instruments, Columbia Maryland) using standard methods (Eaton et al. 2005). The detection limit for the TOC without blanking the instrument between samples was 2.0 mg TOC/L. Microbial respiration Microbial respiration of each mesocosm substrate (sediment, leaves, sponge or glass) was quantified using dehydrogenase activity (DHA) assays (Trevors 1984, Hill et al. 2002, Bunch and Bernot 2011) at the end of the 3 d incubation. Approximately 2 cm3 of each substrate was 52 removed from each mesocosm and placed into 50 mL falcon tubes with 2.5 mL of stream water and 1 mL of 0.75% iodonitrotetrazolium (INT) chloride. Samples were inverted until well mixed and incubated at room temperature for 3 h. Following incubation, 8 mL of methanol was added to each sample to stop the reaction and each sample was inverted until well mixed. All samples were centrifuged for 5 min and supernatant was analyzed on a spectrophotometer (UV-1700 PharmaSpec, Shimadzu) at 428 nm. Because methanol extracted chlorophyll from samples, absorbance values were corrected by averaging the absorbance of ten samples each of 1 g algae, 5 g leaves and 1 g sediment that were incubated with methanol only. Absorbance values were then converted to μg O2/h using a standard curve of INT formazan. Statistical analyses Difference in respiration and nutrient concentrations among algal and substrate treatments were analyzed using analysis of variance (ANOVA) and subsequent Tukey pairwise comparisons. Initial statistical tests indicated no differences between senesced and healthy algal treatments, potentially due to the senesced algae recovery in mesocosms. Thus, all analyses combined senesced and actively growing algae treatments. All ANOVA and pairwise comparisons were performed using SAS statistical software. Results Physicochemical measurements Dissolved oxygen concentrations were 1.4 % higher in the algal treatment (range = 7.40 8.00 mg O2/L) relative to the exudate treatment (7.34 - 7.61 mg O2/L) (p = 0.027; Fig. 1). In the 53 control treatment (no algae or exudate), dissolved oxygen concentration ranged from 7.43 to 7.70 mg O2/L and was not different from the algae and exudate treatments (p > 0.05). Water temperature in DOM treatments was 0.0 – 1.6 °C higher (range = 20.07- 21.67 °C) than the algae treatment (range = 18.47 - 21.77 °C) (p = 0.01; Table 1). Temperature in the control treatments ranged from 18.43 - 22.17 °C and was not different from the algae or exudate treatments (p > 0.05). Temperature did not differ among substrates (p > 0.05). Among algal treatments, pH was 0.61% higher in the exudate treatment (range = 8.56 8.74, p < 0.001; Fig. 2) relative to algae and control treatments (range = 8.47 - 8.70). Among substrates, pH was 0.50 % lower in the sponge treatments (range = 8.54 - 8.68) relative to other treatments (range = 8.47 - 8.74, p < 0.001; Fig. 2). Total organic carbon and dissolved nutrient concentrations Algal exudate treatments had 26.4% higher TOC concentrations (mean = 8.45 mg/L, p < 0.0001; Fig. 3) relative to the algae (mean = 6.42 mg/L) and control (mean = 6.54 mg/L) treatments. Substrate effects were measured with exposure to leaves yielding 33.7% higher TOC concentrations (mean = 8.87 mg/L, p < 0.0001; Fig. 3) relative to other substrate types (range = 5.91 – 7.04 mg/L). In contrast to the TOC concentrations, the exudate treatments had 17.5% lower NO3 concentrations (mean = 5.21 mg/L, p = 0.0002; Fig. 4) relative to the algae (mean = 6.25 mg/L) and control (mean = 6.16 mg/L) treatments (p > 0.05; Fig. 4). Treatments with leaves as the substrate had 42.2 % lower NO3 concentrations (mean = 5.48 mg/L, p < 0.0001; Fig. 4) relative to sediment (mean = 8.26 mg/L) and glass (mean = 8.55 mg/L) substrates (p > 0.05). Sponge substrates had 143.3% lower NO3 concentrations relative to other substrate types. 54 Similar to the TOC concentrations, the exudate treatment had 86.9% higher PO4 concentrations (mean = 0.013 mg/L, p < 0.01; Fig. 5) relative to the algae and control treatments (mean = 0.005 mg/L, p > 0.05). Leaves substrate yielded 110.1% higher PO4 concentrations (mean = 0.014 mg/L, p < 0.003; Fig. 5) relative to the sponge (mean = 0.003 mg/L) and glass (mean = 0.005 mg/L) treatments and 35.0% higher PO4 concentrations relative to the sediment treatment (mean = 0.010 mg/L) (p > 0.05). Ratios of TOC to NO3 were not different among treatments (range = 1.56 – 4.27, p = 0.263) but were among substrates (range = 0.73 – 7.29, p < 0.01) with the highest ratio associated with sponge substrate. Ratios of TOC to PO4 were not different among treatments (range = 1087.9 – 6894.8, p = 0.126) or substrates (range = 908.0 – 6898.9, p = 0.325). Relationships among nutrient ratios suggested differences in nutrient limitation among treatments (Fig. 6). Specifically, algae treatments were primarily phosphorus limited with the lowest TOC: NO3 and highest TOC: PO4 ratios of all treatments. The algae treatment had the highest NO3: PO4 ratio (7789.2). In contrast, exudate treatments were primarily nitrogen limited having the highest TOC: NO3 and lowest TOC: PO4 ratios relative to other treatments. The exudate treatment had the lowest NO3: PO4 ratio (427.5) which further suggested nitrogen limitation. The control treatments were likely carbon limited as the ratios of TOC: NO3, TOC: PO4 and NO3: PO4 were between the algae and exudate treatments. Respiration Leaf s strates had 157.4% higher respiration (mean = 2.72 μg O2/h, p < 0.001; Fig. 6) relative to other s strate types (mean = 0.33 μg O2/h). Total organic carbon influenced microbial respiration rates above a concentration threshold of ~8 mg/L (p < 0.01, Fig. 8; two- 55 dimensional Kolmogorov-Smirnov test, Garvey et al. 1998, Kemp and Dodds 2002). When TOC concentrations were above 8 mg/L, microbial respiration was higher, though variable as other factors were likely controlling rates (e.g., nitrogen, phosphorus, substrate). However, when TOC concentrations were < 8 mg/L respiration was always lower likely due to carbon limitation. Discussion Physiochemical dynamics in response to algae and benthic substrates Algae and substrate treatments influenced dissolved oxygen concentrations and temperature. Changes in dissolved oxygen may be attributed to biological processes. For example, heterotrophic metabolism of DOM decreased available oxygen. In contrast, algae increased dissolved oxygen concentrations which we would expect in conjunction with photosynthesis. Interestingly, the exudate treatment yielded the lowest dissolved oxygen concentration suggesting higher heterotrophic metabolism potentially associated with the readily available DOM. The exudate treatment also had the highest pH which may have been due to higher calcium concentrations, relative to the stream water, in the isolated algal exudate buffering pH shifts associated with production (Talling 1976). In the future, using anion and cation exchange resins would remove these anions and cations, resulting in a more pure algal exudate. Across the substrate treatments, pH was comparable except associated with the sponge treatment which had a significantly lower pH and may be an experimental artifact due to the possible neutralizing buffer agent present in the sponge. Temperature was also influenced by algae treatments and may also be an experimental artifact. The mesocosms were randomly distributed and mesocosms towards the middle of the arrangement may have been insulated by the surrounding mesocosms. 56 Nutrient dynamics in response to algae and substrates Algal treatments affected TOC, nitrate and phosphate concentrations. Specifically, TOC was lowest in the algae treatment, potentially due to assimilation during heterotrophic metabolism. The algae provide a carbon substrate for the microbial community to colonize and assimilate as quickly as it is released (Søndergaard et al. 1995, Wyatt et al. 2012). Even though the algae were healthy the cells co ld release organic car on via an “overflo ” mechanism (Fogg 1983). This overflow mechanism would be more prevalent in eutrophic streams since nitrogen and phosphorus are not limiting to algal productivity. Excess carbon is released so the photosynthetic structures are not clogged with excess carbohydrate and continued algal production can occur. As expected, TOC concentrations were highest in the exudate treatment. Initially, algal exudate treatments had a TOC concentration of 5.45 mg/L in addition to the baseline TOC concentration in the stream water (5.91 mg/L); thus, a cumulative initial concentration of 11.36 mg/L TOC. Over the experiment duration, algal exudate treatment TOC concentrations decreased to 8.56 mg/L. This change in TOC concentration during the experiment suggest that at least 2.80 mg/L TOC were assimilated by the microbial community as there was no influence by a benthic substrate. The algal exudate treatment was added during the experiment to replace the volume lost through evaporation and altered total organic carbon concentrations and assimilation. Using the change in organic carbon observed, the microbial community assimilated at least 24% of the organic carbon available, likely the most labile TOC constituents. The remaining 76% of TOC may have been recalcitrant and difficult to assimilate quickly. Labile organic carbon has been observed to be assimilated quickly (days, Wetzel and Manny 1972; 57 hours, Wyatt et al. 2012) with variation in the time scales based on the composition and origin of the labile organic carbon. For example, Wetzel and Manny (1972) studied leaf leachate while Wyatt and others (2012) studied algal exudates. The amount of labile organic carbon assimilated was comparable but slightly higher than the assimilation of labile organic carbon (0.6 – 1.1 mg/L) reported from a eutrophic lake (Søndergaard et al. 1995). Across substrates, NO3: PO4 was highest in the algal treatments. This may be due to nitrate release into the water column during algal production or that nitrification was stimulated in the presence of algae (Kemp and Dodds 2002). Alternatively, algae may have more efficiently assimilated phosphate resulting in higher ratios. Algal retention of phosphorus has been observed in stream ecosystems (Rier et al. 2007) as phosphorus can often be limiting to autotrophic metabolism. Algal exudate treatments increased availability of organic carbon which may have influenced the ability of the microbial community to assimilate nitrate and phosphate. The microbial community assimilated nitrate, as evidence by lower concentrations, although phosphate concentrations increased over the incubation suggesting that phosphate was being released back to the water column at an equal or greater rate. Phosphate may have been released back to the water column as microbial communities typically do not retain phosphate as efficiently as algae (Morris and Lewis 1992, Rier and Stevenson 2002). Further, the algal exudate ratio of nutrients suggests that the algae treatment mesocosms were primarily NO3 limited and secondarily PO4 limited. Algae and substrate effects on heterotrophic metabolism Contrary to our hypothesis, algal production and algal exudate did not affect microbial respiration. Microbial respiration rates were higher in the algae and exudate treatment relative to 58 the controls, though not statistically different. The lack of an effect of algae on microbial activity may have been due to limited replication. The labile organic carbon released during algal production was likely quickly assimilated and the associated increase in microbial respiration was not observed due to the sampling intervals. Additionally, Rier and Stevenson (2002) suggested that the link between algae and bacteria are more closely associated in oligotrophic environments when nutrients are limiting. Perhaps since the mesocosms were eutrophic, the microbial community was not dependent on algae for carbon and nutrients as they were available in the water column. Further, the algal exudate treatment limited heterotrophic response may be attributed to rapid assimilation of the DOM at experiment start followed by microbial respiration returning to baseline levels. In contrast to algal treatments, substrate affected microbial respiration with leaves resulting in higher respiration likely due to higher carbon availability. Leaf leachate increased the total organic carbon (TOC) concentration in mesocosms relative to other substrates but was comparable to the algal exudate treatment which did not increase respiration. Leaf leachate can be assimilated quickly by the microbial community (Strauss and Lamberti 2002) but higher respiration may also be associated with carbon substrate available for the microbial community (Farjalla et al. 2008, Yoshiura et al. 2008). Slow mineralization of recalcitrant leaf substrate may also explain higher microbial respiration relative to other substrates. Conclusion This experiment showed the influence algae and benthic substrates have on microbial respiration in eutrophic environments and offers insight into the challenges of studying these complex systems. Microbial activity was stimulated with TOC concentrations above 8 mg/L. 59 This response was primarily driven by the leaf substrate. While we did not observe an algal mediated microbial respiration response, this was likely because we did not capture the event, not because the response was absent. Organic carbon, especially labile forms, are quickly assimilated and shorter sampling intervals may help to quantify the influence of algae or algal exudates on the microbial community. Algae have been shown to provide important resources for heterotrophic bacteria (Fogg 1983, Obernosterer and Herndl 1995, Rier et al. 2007, Wyatt et al. 2010, Wyatt et al. 2012) and likely contribute to other processes in streams even in eutrophic ecosystems. Continued study of microbial responses to algae and benthic substrates will help to explain the mechanisms by which these communities interact and how these interactions may influence stream dynamics. 60 References APHA, 2005. Standard Methods for Examination of Water and Wastewater: Centennial Edition. Amer Public Health Assn. Baines, S. B., and M. L. Pace. (1991). The production of dissolved organic matter by phytoplankton and its importance to bacteria: patterns across marine and freshwater systems. Limnology and Oceanography, 36(6), 1078-1090. Beck K. C., Reuter J. H. and E. M. Perdue. (1974) Organic and inorganic geochemistry of some coastal plain rivers of the southeastern United States. Geochimica cosmochimca Acta 38: 341- 364. Bertilsson, S., and J.B. Jones. (2003). Aquatic Ecosystems: Interactivity of Dissolved Organic Matter: Interactivity of Dissolved Organic Matter. pp. 3-19 in Findlay and Sinsabaugh (eds.) Supply of dissolved organic matter to aquatic ecosystems: autochthonous sources. Academic Press. 496p. Bianchi, T. S. (2011). The role of terrestrially derived organic carbon in the coastal ocean: A changing paradigm and the priming effect. Proceedings of the National Academy of Sciences, 108(49), 19473-19481. Bingemann, C.W., Varner, J.E. and W. P. Martin. (1953). The effect of the addition of organic materials on the decomposition of an organic soil. Soil Science Society of America Proceedings. 17:34-38. Bratbak, G., Thingstad, F., and M. Heldal. (1994). Viruses and the microbial loop.Microbial Ecology, 28(2), 209-221. Bunch, A. R., and M.J. Bernot. (2011). Distribution of nonprescription pharmaceuticals in central Indiana streams and effects on sediment microbial activity. Ecotoxicology, 20(1), 97-109. Cole, J. J. (1982). Interactions between bacteria and algae in aquatic ecosystems. Annual Review of Ecology and Systematics, 291-314. Danger, M., Cornut, J., Chauvet, E., Chavez, P., Elger, A., and A. Lecerf. (2013). Benthic algae stimulate leaf litter decomposition in detritus-based headwater streams: a case of aquatic priming effect? Ecology, 94(7), 1604-1613. Eaton, A. D., M. a. H. Franson, A. P. H. Associati, A. W. W. Association, and W. E. Federation. 61 (2005). Standard methods for examination of water & wastewater: centennial edition. American Public Health Association. Farjalla, V. F., Marinho, C. C., Faria, B. M., Amado, A. M., Esteves, F. D. A., Bozelli, R. L., and D. Giroldo. (2009). Synergy of fresh and accumulated organic matter to bacterial growth. Microbial Ecology, 57(4), 657-666. Findlay, S., Howe, K., and D. Fontvielle. (1993). Bacterial-algal relationships in streams of the Hubbard Brook Experimental Forest. Ecology, 2326-2336. Fogg, G. E. (1983). The ecological significance of extracellular products of phytoplankton photosynthesis. Botanica Marina, 26(1), 3-14. Fontaine, S., Mariotti, A., and L. Abbadie. (2003). The priming effect of organic matter: a question of microbial competition?. Soil Biology and Biochemistry,35(6), 837-843. Garvey, J. E., Marschall, E. A., and R. A. Wright. (1998). From star charts to stoneflies: detecting relationships in continuous bivariate data. Ecology, 79(2), 442-447. Guenet, B., Danger, M., Abbadie, L., and G. Lacroix. (2010). Priming effect: bridging the gap between terrestrial and aquatic ecology. Ecology, 91(10), 2850-2861. Hagen, E. M., McCluney, K. E., Wyant, K. A., Soykan, C. U., Keller, A. C., Luttermoser, K. C., Holmes, E.J., Moore, J.C. and J. L. Sabo. (2012). A meta‐analysis of the effects of detritus on primary producers and consumers in marine, freshwater, and terrestrial ecosystems. Oikos, 121(10), 1507-1515. Harbott, E. L., and M. R. Grace. (2005). Extracellular enzyme response to bioavailability of dissolved organic C in streams of varying catchment urbanization. Journal of the North American Benthological Society, 24(3), 588-601. Hill, B. H., Herlihy, A. T., and P. R. Kaufmann. (2002). Benthic microbial respiration in Appalachian Mountain, Piedmont, and Coastal Plains streams of the eastern USA. Freshwater Biology, 47(2), 185-194. Howarth, R. W., Marino, R., and J.J. Cole. (1988). Nitrogen fixation in freshwater, estuarine, and marine ecosystems. 2. Biogeochemical controls. Limnology and Oceanography, 33(4), 688-701. 62 Jones, A. K., and R.C. Cannon. (1986). The release of micro-algal photosynthate and associated bacterial uptake and heterotrophic growth. British Phycological Journal, 21(4), 341-358. Jumars, P. A., Penry, D. L., Baross, J. A., Perry, M. J., and B. W. Frost. (1989). Closing the microbial loop: dissolved carbon pathway to heterotrophic bacteria from incomplete ingestion, digestion and absorption in animals. Deep Sea Research Part A. Oceanographic Research Papers, 36(4), 483-495. Kemp, M. J., and W.K. Dodds. (2002). Comparisons of nitrification and denitrification in prairie and agriculturally influenced streams. Ecological Applications, 12(4), 998-1009. Kuzyakov, Y., Friedel, J. K., and K. Stahr. (2000). Review of mechanisms and quantification of priming effects. Soil Biology and Biochemistry, 32(11), 1485-1498. Lindeman, R. L. (1942). The trophic-dynamic aspect of ecology. Ecology, 23(4), 399-417. Löhnis, F. (1926). Nitrogen availability of green manures. Soil Science, 22(4), 253-290. Morris, D. P., and W. M. Lewis. (1992). Nutrient limitation of bacterioplankton growth in Lake Dillon, Colorado. Limnology and Oceanography, 37(6), 1179-1192. Mosisch, T. D., Bunn, S. E., and P. M. Davies. 2001. The relative importance of shading and nutrients on algal production in subtropical streams. Freshwater Biology, 46:1269–1278. Mulholland, P. J. 1996. Role in nutrient cycling in streams. Pages 609–640 in R. J. Stevenson, M. Bothwell, and R. Lowe (editors). Algal ecology: freshwater benthic ecosystems. Academic Press, San Diego, California. Obernosterer, I., and G.J. Herndl. (1995). Phytoplankton extracellular release and bacterial growth: dependence on the inorganic N: P ratio. Marine ecology progress series, 116(1), 247-257. Odum, H. T. (1956). Primary production in flowing waters. Limnology and Oceanography,1(2), 102-117. Rier, S. T., and R. J. Stevenson. (2002). Effects of light, dissolved organic carbon, and inorganic nutrients on the relationship between algae and heterotrophic bacteria in stream periphyton. Hydrobiologia, 489(1-3), 179-184. 63 Rier, S. T., Kuehn, K. A., and S. N. Francoeur. (2007). Algal regulation of extracellular enzyme activity in stream microbial communities associated with inert substrata and detritus. Journal of the North American Benthological Society, 26(3), 439-449. Rosemond, A. D., Mulholland, P.J. and J. W. Elwood. (1993). Top-down and bottom-up control of stream periphyton: effects of nutrients and herbivores. Ecology 74:1264–1280. Shapiro, J. (1957) Chemical and biological studies on the yellow organic acids of lake water. Limnology and Oceanography. 2: 161-179. Singh, J. S., and S. R. Gupta. (1977). Plant decomposition and soil respiration in terrestrial ecosystems. The Botanical Review, 43(4), 449-528. Søndergaard, M., Hansen, B., and S. Markager. (1995) Dynamics of dissolved organic carbon lability in a eutrophic lake. Limnology and Oceanography, 40:46–54 Strauss, E. A., and G. A. Lamberti. (2002). Effect of dissolved organic carbon quality on microbial decomposition and nitrification rates in stream sediments.Freshwater Biology, 47(1), 65-74. Stevenson, R. J., and R. Glover. (1993). Effects of algal density and current on ion transport through periphyton communities. Limnology and Oceanography, 38(6), 1276-1281. Talling, J.F. (1976). The depletion of carbon dioxide from lake water by phytoplankton. Journal of Ecology, 64(1), 79-121. Tansley, A. G. (1935). The use and abuse of vegetational concepts and terms. Ecology, 16(3), 284-307. Trevors, J. T. (1984). The measurement of electron transport system (ETS) activity in freshwater sediment. Water Research 18: 581-584. Vannote, R. L., Minshall, G. W., Cummins, K. W., Sedell, J. R., and C. E. Cushing. (1980). The river continuum concept. Canadian Journal of Fisheries and Aquatic Sciences, 37(1), 130-137. Wallace, J. B., and J. R. Webster. (1996). The role of macroinvertebrates in stream ecosystem function. Annual Review of Entomology, 41(1), 115-139. 64 Wetzel, R. G., and B. A. Manny. (1972). Decomposition of dissolved organic carbon and nitrogen compounds from leaves in an experimental hardwater stream. (No. COO--159948). Michigan State Univ., Hickory Corners. WK Kellogg Biological Station. Wiegner, T. N., Kaplan, L. A., Newbold, J. D., and P. H. Ostrom. (2005). Contribution of dissolved organic C to stream metabolism: a mesocosm study using 13C-enriched treetissue leachate. Journal of the North American Benthological Society, 24(1), 48-67. Williams, C. J., Scott, A. B., Wilson, H. F., and M. A. Xenopoulos. (2012). Effects of land use on water column bacterial activity and enzyme stoichiometry in stream ecosystems. Aquatic Sciences, 74(3), 483-494. Wyatt, K.H., Rober, A.R., Schmidt, N., and I. R. Davison. (2014a). Effects of desiccation and rewetting on the release and decomposition of dissolved organic carbon from benthic macroalgae. Freshwater Biology, 59: 407-416. Wyatt, K.H., Tellez, E., Woodke, R.L., Bidner, R.J., and I.R. Davison. (2014b). Effects of nutrient limitation on the release and utilization of dissolved organic carbon from benthic algae in Lake Michigan. Freshwater Science, 33(2). Wyatt, K.H., Turetsky, M.R., Rober, A.R., Giroldo D., Kane, E.S., and R. J. Stevenson. (2012). Strong algal controls on carbon cycling during experimental and interannual variation in hydrology in an Alaskan fen. Oecologia 169: 821–832. Wyatt, K.H., Stevenson, R.J., and M.R. Turetsky. (2010). The importance of nutrient colimitation in regulating algal community composition, productivity, and algal-derived DOC in an oligotrophic marsh in interior Alaska. Freshwater Biology 55: 1845–1860. Yoshimura, C., Gessner, M. O., Tockner, K., and H. Furumai. (2008). Chemical properties, microbial respiration, and decomposition of coarse and fine particulate organic matter. Journal of the North American Benthological Society,27(3), 664-673. 65 Fig. 1 66 Table 1. 67 Fig. 2 68 Fig. 3 69 Fig 4. 70 Fig. 5 71 Fig. 6 72 Fig. 7 73 Fig. 8 Respiration ( g O2/L) 0.0020 Algae Exudate Control 0.0015 0.0010 0.0005 0.0000 5 6 7 8 mg TOC/L 74 9 10 Appendix 1. Water Column Physiochemical Measurements January 1/19/2013 9:10 1/19/2013 9:20 1/19/2013 9:30 1/19/2013 9:40 1/19/2013 9:50 1/19/2013 10:00 1/19/2013 10:10 1/19/2013 10:20 1/19/2013 10:30 1/19/2013 10:40 1/19/2013 10:50 1/19/2013 11:00 1/19/2013 11:10 1/19/2013 11:20 1/19/2013 11:30 1/19/2013 11:40 1/19/2013 11:50 1/19/2013 12:00 1/19/2013 12:10 1/19/2013 12:20 1/19/2013 12:30 1/19/2013 12:40 1/19/2013 12:50 1/19/2013 13:00 1/19/2013 13:10 1/19/2013 13:20 1/19/2013 13:30 1/19/2013 13:40 1/19/2013 13:50 1/19/2013 14:00 1/19/2013 14:10 Temp 2.71 2.72 2.72 2.72 2.73 2.75 2.76 2.76 2.75 2.76 2.81 2.88 2.94 2.98 3.01 3.05 3.08 3.12 3.16 3.20 3.25 3.30 3.36 3.41 3.46 3.51 3.56 3.61 3.65 3.69 3.74 DO 12.24 12.29 12.30 12.30 12.29 12.31 12.33 12.30 12.33 12.30 12.35 12.38 12.32 12.35 12.33 12.38 12.42 12.39 12.37 12.35 12.43 12.44 12.40 12.41 12.40 12.43 12.50 12.46 12.45 12.47 12.39 pH 9.75 9.76 9.76 9.77 9.78 9.78 9.78 9.77 9.76 9.75 9.74 9.73 9.59 9.57 9.57 9.56 9.56 9.55 9.55 9.55 9.55 9.55 9.54 9.54 9.54 9.53 9.53 9.53 9.52 9.52 9.52 February 2/7/2013 21:00 2/7/2013 21:10 2/7/2013 21:20 2/7/2013 21:30 2/7/2013 21:40 2/7/2013 21:50 2/7/2013 22:00 2/7/2013 22:10 2/7/2013 22:20 2/7/2013 22:30 2/7/2013 22:40 2/7/2013 22:50 2/7/2013 23:00 2/7/2013 23:10 2/7/2013 23:20 2/7/2013 23:30 2/7/2013 23:40 2/7/2013 23:50 2/8/2013 0:00 2/8/2013 0:10 2/8/2013 0:20 2/8/2013 0:30 2/8/2013 0:40 2/8/2013 0:50 2/8/2013 1:00 2/8/2013 1:10 2/8/2013 1:20 2/8/2013 1:30 2/8/2013 1:40 2/8/2013 1:50 2/8/2013 2:00 Temp 4.99 5.01 5.03 5.04 5.05 5.06 5.06 5.07 5.08 5.09 5.10 5.12 5.13 5.14 5.16 5.17 5.18 5.20 5.21 5.23 5.24 5.26 5.28 5.29 5.31 5.32 5.34 5.34 5.35 5.36 5.37 75 DO 12.04 12.03 11.98 11.86 11.90 11.88 11.89 11.88 11.79 11.83 11.81 11.76 11.83 11.76 11.78 11.76 11.72 11.71 11.66 11.65 11.70 11.65 11.62 11.62 11.61 11.59 11.58 11.53 11.54 11.52 11.53 pH 9.44 9.51 9.54 9.57 9.57 9.56 9.58 9.57 9.58 9.59 9.59 9.59 9.59 9.59 9.59 9.59 9.59 9.59 9.59 9.58 9.58 9.58 9.58 9.58 9.58 9.58 9.58 9.58 9.58 9.57 9.58 March 2/28/13 21:00 2/28/13 21:10 2/28/13 21:20 2/28/13 21:30 2/28/13 21:40 2/28/13 21:50 2/28/13 22:00 2/28/13 22:10 2/28/13 22:20 2/28/13 22:30 2/28/13 22:40 2/28/13 22:50 2/28/13 23:00 2/28/13 23:10 2/28/13 23:20 2/28/13 23:30 2/28/13 23:40 2/28/13 23:50 3/1/13 0:00 3/1/13 0:10 3/1/13 0:20 3/1/13 0:30 3/1/13 0:40 3/1/13 0:50 3/1/13 1:00 3/1/13 1:10 3/1/13 1:20 3/1/13 1:30 3/1/13 1:40 3/1/13 1:50 3/1/13 2:00 Temp 3.31 3.31 3.31 3.31 3.30 3.30 3.30 3.29 3.29 3.28 3.27 3.27 3.26 3.26 3.25 3.25 3.24 3.24 3.23 3.23 3.23 3.22 3.22 3.22 3.21 3.23 3.29 3.34 3.36 3.33 3.28 DO pH 12.96 12.97 12.97 12.91 12.94 12.98 12.91 12.97 12.89 12.94 12.93 12.98 12.94 12.91 12.97 12.91 12.95 12.93 12.95 12.94 12.93 12.91 12.98 12.95 12.92 12.94 12.83 12.73 12.70 12.74 12.79 1/19/2013 14:20 1/19/2013 14:30 1/19/2013 14:40 1/19/2013 14:50 1/19/2013 15:00 1/19/2013 15:10 1/19/2013 15:20 1/19/2013 15:30 1/19/2013 15:40 1/19/2013 15:50 1/19/2013 16:00 1/19/2013 16:10 1/19/2013 16:20 1/19/2013 16:30 1/19/2013 16:40 1/19/2013 16:50 1/19/2013 17:00 1/19/2013 17:10 1/19/2013 17:20 1/19/2013 17:30 1/19/2013 17:40 1/19/2013 17:50 1/19/2013 18:00 1/19/2013 18:10 1/19/2013 18:20 1/19/2013 18:30 1/19/2013 18:40 1/19/2013 18:50 1/19/2013 19:00 1/19/2013 19:10 1/19/2013 19:20 1/19/2013 19:30 1/19/2013 19:40 1/19/2013 19:50 3.78 3.82 3.85 3.90 3.94 3.96 3.98 4.01 4.02 4.04 4.06 4.07 4.09 4.09 4.10 4.11 4.13 4.14 4.15 4.16 4.18 4.19 4.20 4.22 4.23 4.25 4.26 4.27 4.28 4.30 4.30 4.31 4.33 4.34 12.40 12.46 12.40 12.42 12.46 12.40 12.41 12.34 12.38 12.36 12.34 12.35 12.30 12.35 12.31 12.29 12.27 12.25 12.21 12.17 12.24 12.12 12.13 12.13 12.09 12.05 12.04 12.01 11.98 11.96 11.94 11.98 11.95 11.90 9.52 9.52 9.51 9.51 9.50 9.50 9.50 9.49 9.49 9.50 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.48 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 9.49 2/8/2013 2:10 2/8/2013 2:20 2/8/2013 2:30 2/8/2013 2:40 2/8/2013 2:50 2/8/2013 3:00 2/8/2013 3:10 2/8/2013 3:20 2/8/2013 3:30 2/8/2013 3:40 2/8/2013 3:50 2/8/2013 4:00 2/8/2013 4:10 2/8/2013 4:20 2/8/2013 4:30 2/8/2013 4:40 2/8/2013 4:50 2/8/2013 5:00 2/8/2013 5:10 2/8/2013 5:20 2/8/2013 5:30 2/8/2013 5:40 2/8/2013 5:50 2/8/2013 6:00 2/8/2013 6:10 2/8/2013 6:20 2/8/2013 6:30 2/8/2013 6:40 2/8/2013 6:50 2/8/2013 7:00 2/8/2013 7:10 2/8/2013 7:20 2/8/2013 7:30 2/8/2013 7:40 5.37 5.37 5.38 5.38 5.38 5.39 5.39 5.40 5.40 5.40 5.39 5.38 5.37 5.36 5.34 5.32 5.32 5.32 5.34 5.36 5.39 5.40 5.42 5.44 5.44 5.44 5.43 5.42 5.41 5.39 5.38 5.36 5.34 5.33 76 11.50 11.52 11.50 11.49 11.46 11.49 11.48 11.46 11.43 11.44 11.43 11.43 11.42 11.43 11.46 11.47 11.43 11.40 11.43 11.40 11.34 11.28 11.28 11.23 11.17 11.15 11.14 11.14 11.10 11.06 11.11 11.10 11.10 11.15 9.58 9.57 9.58 9.59 9.59 9.59 9.59 9.59 9.59 9.58 9.59 9.59 9.58 9.60 9.59 9.59 9.59 9.58 9.56 9.56 9.56 9.54 9.53 9.53 9.52 9.51 9.50 9.49 9.49 9.48 9.48 9.48 9.48 9.49 3/1/13 2:10 3/1/13 2:20 3/1/13 2:30 3/1/13 2:40 3/1/13 2:50 3/1/13 3:00 3/1/13 3:10 3/1/13 3:20 3/1/13 3:30 3/1/13 3:40 3/1/13 3:50 3/1/13 4:00 3/1/13 4:10 3/1/13 4:20 3/1/13 4:30 3/1/13 4:40 3/1/13 4:50 3/1/13 5:00 3/1/13 5:10 3/1/13 5:20 3/1/13 5:30 3/1/13 5:40 3/1/13 5:50 3/1/13 6:00 3/1/13 6:10 3/1/13 6:20 3/1/13 6:30 3/1/13 6:40 3/1/13 6:50 3/1/13 7:00 3/1/13 7:10 3/1/13 7:20 3/1/13 7:30 3/1/13 7:40 3.25 3.25 3.27 3.28 3.28 3.28 3.26 3.24 3.23 3.21 3.20 3.19 3.18 3.17 3.16 3.15 3.15 3.15 3.15 3.15 3.15 3.14 3.14 3.14 3.15 3.15 3.15 3.16 3.15 3.15 3.15 3.16 3.15 3.16 12.79 12.87 12.83 12.82 12.85 12.86 12.86 12.89 12.84 12.90 12.94 12.95 12.94 12.88 12.90 12.90 12.92 12.95 12.98 12.95 12.92 12.89 12.96 12.95 12.89 12.90 12.96 12.93 12.90 12.95 12.88 12.91 12.91 12.91 1/19/2013 20:00 1/19/2013 20:10 1/19/2013 20:20 1/19/2013 20:30 1/19/2013 20:40 1/19/2013 20:50 1/19/2013 21:00 1/19/2013 21:10 1/19/2013 21:20 1/19/2013 21:30 1/19/2013 21:40 1/19/2013 21:50 1/19/2013 22:00 1/19/2013 22:10 1/19/2013 22:20 1/19/2013 22:30 1/19/2013 22:40 1/19/2013 22:50 1/19/2013 23:00 1/19/2013 23:10 1/19/2013 23:20 1/19/2013 23:30 1/19/2013 23:40 1/19/2013 23:50 1/20/2013 0:00 1/20/2013 0:10 1/20/2013 0:20 1/20/2013 0:30 1/20/2013 0:40 1/20/2013 0:50 1/20/2013 1:00 1/20/2013 1:10 1/20/2013 1:20 1/20/2013 1:30 4.34 4.31 4.29 4.30 4.35 4.39 4.43 4.46 4.47 4.48 4.48 4.47 4.47 4.46 4.45 4.45 4.44 4.44 4.44 4.43 4.42 4.42 4.41 4.40 4.38 4.38 4.37 4.36 4.35 4.34 4.32 4.31 4.31 4.30 11.93 11.92 11.90 11.92 11.88 11.86 11.82 11.79 11.78 11.77 11.80 11.78 11.78 11.74 11.77 11.75 11.74 11.74 11.70 11.70 11.74 11.67 11.67 11.70 11.75 11.69 11.68 11.66 11.69 11.69 11.67 11.67 11.65 11.66 9.49 9.50 9.50 9.50 9.49 9.49 9.49 9.48 9.48 9.48 9.48 9.49 9.49 9.49 9.49 9.49 9.49 9.50 9.50 9.50 9.50 9.51 9.51 9.51 9.51 9.51 9.51 9.51 9.51 9.52 9.52 9.52 9.53 9.53 2/8/2013 7:50 2/8/2013 8:00 2/8/2013 8:10 2/8/2013 8:20 2/8/2013 8:30 2/8/2013 8:40 2/8/2013 8:50 2/8/2013 9:00 2/8/2013 9:10 2/8/2013 9:20 2/8/2013 9:30 2/8/2013 9:40 2/8/2013 9:50 2/8/2013 10:00 2/8/2013 10:10 2/8/2013 10:20 2/8/2013 10:30 2/8/2013 10:40 2/8/2013 10:50 2/8/2013 11:00 2/8/2013 11:10 2/8/2013 11:20 2/8/2013 11:30 2/8/2013 11:40 2/8/2013 11:50 2/8/2013 12:00 2/8/2013 12:10 2/8/2013 12:20 2/8/2013 12:30 2/8/2013 12:40 2/8/2013 12:50 2/8/2013 13:00 2/8/2013 13:10 2/8/2013 13:20 5.31 5.29 5.26 5.25 5.22 5.21 5.19 5.18 5.18 5.17 5.15 5.14 5.12 5.11 5.10 5.09 5.08 5.08 5.07 5.07 5.06 5.04 5.01 5.01 5.01 5.01 5.01 5.01 5.01 4.99 4.98 4.96 4.95 4.95 77 11.14 11.11 11.10 11.19 11.18 11.27 11.23 11.26 11.27 11.31 11.30 11.32 11.31 11.36 11.38 11.41 11.45 11.51 11.49 11.52 11.61 11.61 11.71 11.74 11.80 11.80 11.88 11.84 11.89 11.90 12.01 12.00 12.04 12.12 9.49 9.50 9.51 9.51 9.51 9.52 9.52 9.53 9.53 9.53 9.53 9.54 9.55 9.55 9.55 9.56 9.56 9.57 9.58 9.59 9.59 9.61 9.63 9.63 9.63 9.63 9.64 9.64 9.65 9.65 9.66 9.66 9.67 9.67 3/1/13 7:50 3/1/13 8:00 3/1/13 8:10 3/1/13 8:20 3/1/13 8:30 3/1/13 8:40 3/1/13 8:50 3/1/13 9:00 3/1/13 9:10 3/1/13 9:20 3/1/13 9:30 3/1/13 9:40 3/1/13 9:50 3/1/13 10:00 3/1/13 10:10 3/1/13 10:20 3/1/13 10:30 3/1/13 10:40 3/1/13 10:50 3/1/13 11:00 3/1/13 11:10 3/1/13 11:20 3/1/13 11:30 3/1/13 11:40 3/1/13 11:50 3/1/13 12:00 3/1/13 12:10 3/1/13 12:20 3/1/13 12:30 3/1/13 12:40 3/1/13 12:50 3/1/13 13:00 3/1/13 13:10 3/1/13 13:20 3.15 3.16 3.16 3.16 3.17 3.17 3.17 3.17 3.17 3.17 3.17 3.17 3.18 3.18 3.18 3.16 3.17 3.20 3.23 3.27 3.29 3.31 3.33 3.33 3.32 3.33 3.33 3.34 3.35 3.35 3.36 3.37 3.39 3.41 12.90 12.94 12.93 12.92 12.97 12.91 12.92 12.92 12.94 12.96 12.93 12.94 12.96 13.00 12.99 13.06 13.06 13.03 13.02 13.05 13.01 13.04 13.01 12.96 13.05 13.08 13.07 13.05 13.07 13.11 13.04 13.04 13.08 13.17 1/20/2013 1:40 1/20/2013 1:50 1/20/2013 2:00 1/20/2013 2:10 1/20/2013 2:20 1/20/2013 2:30 1/20/2013 2:40 1/20/2013 2:50 1/20/2013 3:00 1/20/2013 3:10 1/20/2013 3:20 1/20/2013 3:30 1/20/2013 3:40 1/20/2013 3:50 1/20/2013 4:00 1/20/2013 4:10 1/20/2013 4:20 1/20/2013 4:30 1/20/2013 4:40 1/20/2013 4:50 1/20/2013 5:00 1/20/2013 5:10 1/20/2013 5:20 1/20/2013 5:30 1/20/2013 5:40 1/20/2013 5:50 1/20/2013 6:00 1/20/2013 6:10 1/20/2013 6:20 1/20/2013 6:30 1/20/2013 6:40 1/20/2013 6:50 1/20/2013 7:00 1/20/2013 7:10 4.30 4.29 4.29 4.26 4.25 4.22 4.20 4.18 4.15 4.13 4.10 4.07 4.03 3.98 3.91 3.88 3.86 3.87 3.88 3.86 3.83 3.79 3.75 3.70 3.66 3.61 3.55 3.51 3.47 3.44 3.40 3.35 3.31 3.27 11.66 11.66 11.69 11.65 11.70 11.64 11.71 11.69 11.65 11.68 11.67 11.69 11.67 11.70 11.72 11.69 11.68 11.67 11.72 11.71 11.70 11.66 11.72 11.75 11.77 11.78 11.75 11.80 11.77 11.82 11.79 11.85 11.79 11.85 9.53 9.53 9.53 9.54 9.54 9.54 9.54 9.54 9.55 9.55 9.55 9.55 9.56 9.57 9.57 9.57 9.57 9.56 9.56 9.56 9.56 9.56 9.56 9.57 9.57 9.57 9.58 9.59 9.59 9.59 9.59 9.60 9.60 9.60 2/8/2013 13:30 2/8/2013 13:40 2/8/2013 13:50 2/8/2013 14:00 2/8/2013 14:10 2/8/2013 14:20 2/8/2013 14:30 2/8/2013 14:40 2/8/2013 14:50 2/8/2013 15:00 2/8/2013 15:10 2/8/2013 15:20 2/8/2013 15:30 2/8/2013 15:40 2/8/2013 15:50 2/8/2013 16:00 2/8/2013 16:10 2/8/2013 16:20 2/8/2013 16:30 2/8/2013 16:40 2/8/2013 16:50 2/8/2013 17:00 2/8/2013 17:10 2/8/2013 17:20 2/8/2013 17:30 2/8/2013 17:40 2/8/2013 17:50 2/8/2013 18:00 2/8/2013 18:10 2/8/2013 18:20 2/8/2013 18:30 2/8/2013 18:40 2/8/2013 18:50 2/8/2013 19:00 4.97 4.98 4.98 4.99 5.01 5.02 5.03 5.04 5.04 5.03 5.03 5.04 5.04 5.04 5.03 5.02 5.00 4.98 4.96 4.94 4.91 4.89 4.87 4.85 4.82 4.80 4.77 4.73 4.70 4.66 4.62 4.58 4.54 4.50 78 12.09 12.13 12.18 12.18 12.20 12.24 12.25 12.25 12.23 12.31 12.34 12.41 12.33 12.37 12.40 12.37 12.37 12.34 12.37 12.33 12.33 12.31 12.25 12.32 12.28 12.28 12.24 12.27 12.22 12.19 12.15 12.14 12.16 12.13 9.68 9.68 9.67 9.69 9.69 9.70 9.69 9.70 9.69 9.70 9.70 9.70 9.71 9.71 9.71 9.72 9.73 9.73 9.73 9.73 9.73 9.72 9.73 9.74 9.73 9.74 9.74 9.74 9.74 9.74 9.74 9.74 9.74 9.74 3/1/13 13:30 3/1/13 13:40 3/1/13 13:50 3/1/13 14:00 3/1/13 14:10 3/1/13 14:20 3/1/13 14:30 3/1/13 14:40 3/1/13 14:50 3/1/13 15:00 3/1/13 15:10 3/1/13 15:20 3/1/13 15:30 3/1/13 15:40 3/1/13 15:50 3/1/13 16:00 3/1/13 16:10 3/1/13 16:20 3/1/13 16:30 3/1/13 16:40 3/1/13 16:50 3/1/13 17:00 3/1/13 17:10 3/1/13 17:20 3/1/13 17:30 3/1/13 17:40 3/1/13 17:50 3/1/13 18:00 3/1/13 18:10 3/1/13 18:20 3/1/13 18:30 3/1/13 18:40 3/1/13 18:50 3/1/13 19:00 3.44 3.47 3.48 3.50 3.52 3.54 3.55 3.57 3.58 3.58 3.60 3.59 3.60 3.60 3.60 3.60 3.60 3.60 3.61 3.60 3.61 3.61 3.61 3.61 3.61 3.61 3.60 3.60 3.60 3.59 3.56 3.54 3.55 3.57 13.12 13.15 13.15 13.15 13.17 13.16 13.15 13.14 13.19 13.17 13.21 13.10 13.19 13.17 13.16 13.15 13.18 13.18 13.13 13.17 13.19 13.13 13.13 13.13 13.14 13.12 13.10 13.08 13.12 13.07 13.05 13.03 13.08 13.00 1/20/2013 7:20 1/20/2013 7:30 1/20/2013 7:40 1/20/2013 7:50 1/20/2013 8:00 1/20/2013 8:10 1/24/2013 21:00 1/24/2013 21:10 1/24/2013 21:20 1/24/2013 21:30 1/24/2013 21:40 1/24/2013 21:50 1/24/2013 22:00 1/24/2013 22:10 1/24/2013 22:20 1/24/2013 22:30 1/24/2013 22:40 1/24/2013 22:50 1/24/2013 23:00 1/24/2013 23:10 1/24/2013 23:20 1/24/2013 23:30 1/24/2013 23:40 1/24/2013 23:50 1/25/2013 0:00 1/25/2013 0:10 1/25/2013 0:20 1/25/2013 0:30 1/25/2013 0:40 1/25/2013 0:50 1/25/2013 1:00 1/25/2013 1:10 1/25/2013 1:20 1/25/2013 1:30 3.24 3.19 3.16 3.11 3.07 3.03 0.69 0.67 0.66 0.64 0.65 0.63 0.61 0.61 0.58 0.55 0.54 0.55 0.58 0.61 0.63 0.65 0.68 0.69 0.69 0.69 0.68 0.68 0.67 0.67 0.66 0.66 0.67 0.66 11.83 11.89 11.85 11.88 11.90 11.92 12.98 13.04 12.96 13.00 12.96 12.92 12.97 12.88 13.01 12.99 12.94 12.93 12.94 12.94 12.87 12.90 12.84 12.85 12.90 12.81 12.89 12.82 12.84 12.86 12.85 12.82 12.83 12.82 9.60 9.61 9.61 9.62 9.62 9.62 9.62 9.65 9.66 9.66 9.64 9.64 9.64 9.64 9.64 9.64 9.64 9.64 9.65 9.65 9.65 9.66 9.66 9.66 9.65 9.66 9.66 9.66 9.60 9.66 9.67 9.67 9.68 9.68 2/8/2013 19:10 2/8/2013 19:20 2/8/2013 19:30 2/8/2013 19:40 2/8/2013 19:50 2/8/2013 20:00 2/8/2013 20:10 2/8/2013 20:20 2/8/2013 20:30 2/8/2013 20:40 2/8/2013 20:50 2/8/2013 21:00 2/8/2013 21:10 2/8/2013 21:20 2/8/2013 21:30 2/8/2013 21:40 2/8/2013 21:50 2/8/2013 22:00 2/8/2013 22:10 2/8/2013 22:20 2/8/2013 22:30 2/8/2013 22:40 2/8/2013 22:50 2/8/2013 23:00 2/8/2013 23:10 2/8/2013 23:20 2/8/2013 23:30 2/8/2013 23:40 2/8/2013 23:50 2/9/2013 0:00 2/9/2013 0:10 2/9/2013 0:20 2/9/2013 0:30 2/9/2013 0:40 4.47 4.43 4.41 4.38 4.37 4.32 4.26 4.23 4.22 4.23 4.23 4.23 4.21 4.18 4.16 4.12 4.09 4.06 4.04 4.01 4.00 3.97 3.95 3.93 3.90 3.88 3.85 3.83 3.81 3.78 3.76 3.73 3.71 3.68 79 12.14 12.11 12.07 12.09 12.05 12.06 12.10 12.07 11.99 12.00 12.03 12.00 12.03 12.02 12.00 12.01 11.98 12.00 11.97 12.02 12.03 12.05 12.06 12.02 12.04 12.06 12.04 12.05 12.03 12.08 12.03 12.08 12.05 12.10 9.74 9.74 9.74 9.74 9.74 9.75 9.74 9.75 9.74 9.73 9.74 9.74 9.74 9.74 9.75 9.75 9.76 9.76 9.75 9.76 9.75 9.76 9.75 9.76 9.76 9.77 9.77 9.77 9.77 9.78 9.77 9.78 9.78 9.78 3/1/13 19:10 3/1/13 19:20 3/1/13 19:30 3/1/13 19:40 3/1/13 19:50 3/1/13 20:00 3/1/13 20:10 3/1/13 20:20 3/1/13 20:30 3/1/13 20:40 3/1/13 20:50 3/1/13 21:00 3/1/13 21:10 3/1/13 21:20 3/1/13 21:30 3/1/13 21:40 3/1/13 21:50 3/1/13 22:00 3/1/13 22:10 3/1/13 22:20 3/1/13 22:30 3/1/13 22:40 3/1/13 22:50 3/1/13 23:00 3/1/13 23:10 3/1/13 23:20 3/1/13 23:30 3/1/13 23:40 3/1/13 23:50 3/2/13 0:00 3/2/13 0:10 3/2/13 0:20 3/2/13 0:30 3/2/13 0:40 3.59 3.61 3.62 3.62 3.62 3.60 3.58 3.56 3.55 3.54 3.52 3.51 3.49 3.48 3.47 3.46 3.46 3.45 3.44 3.43 3.42 3.41 3.40 3.38 3.37 3.37 3.36 3.35 3.34 3.32 3.32 3.31 3.31 3.30 13.02 12.97 13.00 12.98 12.97 12.94 12.95 12.92 12.94 12.97 12.92 12.92 12.95 12.91 12.93 12.94 12.94 12.94 12.89 12.94 12.96 12.97 12.94 12.91 12.89 12.94 12.88 12.92 12.92 12.88 12.89 12.90 12.88 12.91 1/25/2013 1:40 1/25/2013 1:50 1/25/2013 2:00 1/25/2013 2:10 1/25/2013 2:20 1/25/2013 2:30 1/25/2013 2:40 1/25/2013 2:50 1/25/2013 3:00 1/25/2013 3:10 1/25/2013 3:20 1/25/2013 3:30 1/25/2013 3:40 1/25/2013 3:50 1/25/2013 4:00 1/25/2013 4:10 1/25/2013 4:20 1/25/2013 4:30 1/25/2013 4:40 1/25/2013 4:50 1/25/2013 5:00 1/25/2013 5:10 1/25/2013 5:20 1/25/2013 5:30 1/25/2013 5:40 1/25/2013 5:50 1/25/2013 6:00 1/25/2013 6:10 1/25/2013 6:20 1/25/2013 6:30 1/25/2013 6:40 1/25/2013 6:50 0.66 0.68 0.68 0.68 0.69 0.69 0.69 0.70 0.71 0.70 0.71 0.71 0.71 0.71 0.72 0.72 0.71 0.69 0.65 0.65 0.66 0.67 0.69 0.72 0.73 0.76 0.76 0.77 0.74 0.70 0.68 0.70 12.84 12.81 12.80 12.85 12.79 12.81 12.84 12.77 12.79 12.78 12.80 12.80 12.78 12.75 12.81 12.82 12.77 12.82 12.82 12.77 12.76 12.77 12.76 12.76 12.73 12.73 12.69 12.71 12.73 12.70 12.74 12.68 9.68 9.69 9.71 9.70 9.69 9.69 9.69 9.69 9.69 9.68 9.68 9.71 9.70 9.69 9.69 9.69 9.72 9.69 9.69 9.71 9.72 9.70 9.72 9.73 9.71 9.70 9.70 9.71 9.73 9.71 9.71 9.73 2/9/2013 0:50 2/9/2013 1:00 2/9/2013 1:10 2/9/2013 1:20 2/9/2013 1:30 2/9/2013 1:40 2/9/2013 1:50 2/9/2013 2:00 2/9/2013 2:10 2/9/2013 2:20 2/9/2013 2:30 2/9/2013 2:40 2/9/2013 2:50 2/9/2013 3:00 2/9/2013 3:10 2/9/2013 3:20 2/9/2013 3:30 2/9/2013 3:40 2/9/2013 3:50 2/9/2013 4:00 2/9/2013 4:10 2/9/2013 4:20 2/9/2013 4:30 2/9/2013 4:40 2/9/2013 4:50 2/9/2013 5:00 2/9/2013 5:10 2/9/2013 5:20 2/9/2013 5:30 2/9/2013 5:40 2/9/2013 5:50 2/9/2013 6:00 3.66 3.64 3.62 3.60 3.57 3.55 3.52 3.50 3.47 3.45 3.42 3.39 3.34 3.29 3.28 3.29 3.30 3.31 3.30 3.28 3.25 3.23 3.20 3.17 3.15 3.12 3.09 3.07 3.05 3.02 3.00 2.98 80 12.08 12.05 12.07 12.06 12.07 12.08 12.10 12.10 12.07 12.09 12.08 12.13 12.15 12.12 12.11 12.16 12.13 12.08 12.19 12.12 12.11 12.13 12.16 12.14 12.16 12.19 12.14 12.16 12.21 12.23 12.20 12.18 9.78 9.78 9.78 9.78 9.78 9.78 9.78 9.78 9.78 9.78 9.78 9.78 9.79 9.78 9.77 9.77 9.76 9.76 9.75 9.76 9.77 9.77 9.78 9.78 9.79 9.78 9.79 9.79 9.79 9.79 9.80 9.80 3/2/13 0:50 3/2/13 1:00 3/2/13 1:10 3/2/13 1:20 3/2/13 1:30 3/2/13 1:40 3/2/13 1:50 3/2/13 2:00 3/2/13 2:10 3/2/13 2:20 3/2/13 2:30 3/2/13 2:40 3/2/13 2:50 3/2/13 3:00 3/2/13 3:10 3/2/13 3:20 3/2/13 3:30 3/2/13 3:40 3/2/13 3:50 3/2/13 4:00 3/2/13 4:10 3/2/13 4:20 3/2/13 4:30 3/2/13 4:40 3/2/13 4:50 3/2/13 5:00 3/2/13 5:10 3/2/13 5:20 3/2/13 5:30 3/2/13 5:40 3/2/13 5:50 3/2/13 6:00 3.29 3.29 3.27 3.26 3.25 3.23 3.22 3.20 3.17 3.12 3.12 3.14 3.15 3.16 3.16 3.15 3.14 3.12 3.10 3.08 3.06 3.05 3.03 3.02 3.00 2.99 2.97 2.96 2.96 2.95 2.94 2.93 12.93 12.90 12.90 12.90 12.92 12.87 12.92 12.91 12.89 12.95 12.96 12.99 12.91 12.92 12.91 12.93 12.94 12.90 12.93 12.94 12.98 12.94 12.93 12.96 12.95 12.97 12.97 12.98 12.96 12.98 12.97 12.95 Appendix 1. (continued) April 4/15/2013 0:00 4/15/2013 0:10 4/15/2013 0:20 4/15/2013 0:30 4/15/2013 0:40 4/15/2013 0:50 4/15/2013 1:00 4/15/2013 1:10 4/15/2013 1:20 4/15/2013 1:30 4/15/2013 1:40 4/15/2013 1:50 4/15/2013 2:00 4/15/2013 2:10 4/15/2013 2:20 4/15/2013 2:30 4/15/2013 2:40 4/15/2013 2:50 4/15/2013 3:00 4/15/2013 3:10 4/15/2013 3:20 4/15/2013 3:30 4/15/2013 3:40 4/15/2013 3:50 4/15/2013 4:00 4/15/2013 4:10 4/15/2013 4:20 4/15/2013 4:30 Temp 10.85 10.84 10.82 10.81 10.79 10.78 10.77 10.75 10.74 10.73 10.72 10.7 10.69 10.68 10.66 10.65 10.64 10.63 10.62 10.61 10.59 10.59 10.58 10.57 10.56 10.55 10.54 10.53 DO 9.62 9.64 9.58 9.58 9.58 9.57 9.58 9.56 9.58 9.55 9.53 9.49 9.52 9.51 9.54 9.53 9.52 9.49 9.46 9.45 9.51 9.47 9.49 9.43 9.46 9.46 9.43 9.39 pH 9.01 9.03 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 May Temp 5/29/2013 21:00 22.29 5/29/2013 21:10 22.25 5/29/2013 21:20 22.2 5/29/2013 21:30 22.15 5/29/2013 21:40 22.1 5/29/2013 21:50 22.05 5/29/2013 22:00 22 5/29/2013 22:10 21.95 5/29/2013 22:20 21.91 5/29/2013 22:30 21.87 5/29/2013 22:40 21.84 5/29/2013 22:50 21.8 5/29/2013 23:00 21.76 5/29/2013 23:10 21.73 5/29/2013 23:20 21.7 5/29/2013 23:30 21.66 5/29/2013 23:40 21.64 5/29/2013 23:50 21.61 5/30/2013 0:00 21.58 5/30/2013 0:10 21.55 5/30/2013 0:20 21.52 5/30/2013 0:30 21.49 5/30/2013 0:40 21.47 5/30/2013 0:50 21.44 5/30/2013 1:00 21.41 5/30/2013 1:10 21.39 5/30/2013 1:20 21.36 5/30/2013 1:30 21.34 81 DO 8.34 8.25 8.18 8.11 8.05 7.97 7.88 7.9 7.79 7.76 7.67 7.61 7.54 7.49 7.46 7.39 7.36 7.34 7.29 7.32 7.26 7.19 7.2 7.18 7.17 7.14 7.07 7.06 pH 8.78 8.8 8.8 8.8 8.8 8.79 8.78 8.78 8.78 8.77 8.77 8.77 8.76 8.77 8.76 8.76 8.75 8.76 8.75 8.75 8.75 8.75 8.74 8.75 8.74 8.74 8.74 8.74 June 6/17/2013 16:10 6/17/2013 16:20 6/17/2013 16:30 6/17/2013 16:40 6/17/2013 16:50 6/17/2013 17:00 6/17/2013 17:10 6/17/2013 17:20 6/17/2013 17:30 6/17/2013 17:40 6/17/2013 17:50 6/17/2013 18:00 6/17/2013 18:10 6/17/2013 18:20 6/17/2013 18:30 6/17/2013 18:40 6/17/2013 18:50 6/17/2013 19:00 6/17/2013 19:10 6/17/2013 19:20 6/17/2013 19:30 6/17/2013 19:40 6/17/2013 19:50 6/17/2013 20:00 6/17/2013 20:10 6/17/2013 20:20 6/17/2013 20:30 6/17/2013 20:40 Temp 23.56 23.59 23.6 23.61 23.59 23.56 23.55 23.55 23.54 23.54 23.53 23.53 23.52 23.52 23.53 23.53 23.54 23.57 23.6 23.62 23.62 23.6 23.58 23.56 23.54 23.53 23.51 23.51 DO 8.07 8.09 8.06 8.02 7.95 7.91 7.86 7.86 7.82 7.82 7.77 7.68 7.64 7.59 7.57 7.52 7.49 7.41 7.37 7.33 7.24 7.24 7.19 7.17 7.14 7.06 7.07 7.02 pH 9.1 9.06 9.07 9.07 9.07 9.07 9.06 9.07 9.06 9.06 9.06 9.06 9.06 9.05 9.05 9.05 9.05 9.05 9.05 9.05 9.04 9.04 9.03 9.03 9.02 9.02 9.02 9.01 4/15/2013 4:40 4/15/2013 4:50 4/15/2013 5:00 4/15/2013 5:10 4/15/2013 5:20 4/15/2013 5:30 4/15/2013 5:40 4/15/2013 5:50 4/15/2013 6:00 4/15/2013 6:10 4/15/2013 6:20 4/15/2013 6:30 4/15/2013 6:40 4/15/2013 6:50 4/15/2013 7:00 4/15/2013 7:10 4/15/2013 7:20 4/15/2013 7:30 4/15/2013 7:40 4/15/2013 7:50 4/15/2013 8:00 4/15/2013 8:10 4/15/2013 8:20 4/15/2013 8:30 4/15/2013 8:40 4/28/2013 21:00 4/28/2013 21:10 4/28/2013 21:20 4/28/2013 21:30 4/28/2013 21:40 4/28/2013 21:50 10.52 10.51 10.5 10.49 10.49 10.48 10.47 10.46 10.46 10.46 10.45 10.45 10.44 10.44 10.43 10.43 10.44 10.45 10.46 10.49 10.51 10.54 10.57 10.59 10.62 13.24 13.23 13.22 13.22 13.21 13.21 9.43 9.45 9.41 9.4 9.45 9.41 9.41 9.4 9.41 9.4 9.41 9.38 9.41 9.41 9.43 9.4 9.4 9.48 9.49 9.48 9.52 9.54 9.59 9.63 9.7 8.97 8.94 8.86 8.83 8.82 8.83 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.05 9.05 5/30/2013 1:40 5/30/2013 1:50 5/30/2013 2:00 5/30/2013 2:10 5/30/2013 2:20 5/30/2013 2:30 5/30/2013 2:40 5/30/2013 2:50 5/30/2013 3:00 5/30/2013 3:10 5/30/2013 3:20 5/30/2013 3:30 5/30/2013 3:40 5/30/2013 3:50 5/30/2013 4:00 5/30/2013 4:10 5/30/2013 4:20 5/30/2013 4:30 5/30/2013 4:40 5/30/2013 4:50 5/30/2013 5:00 5/30/2013 5:10 5/30/2013 5:20 5/30/2013 5:30 5/30/2013 5:40 5/30/2013 5:50 5/30/2013 6:00 5/30/2013 6:10 5/30/2013 6:20 5/30/2013 6:30 5/30/2013 6:40 21.31 21.28 21.25 21.23 21.2 21.17 21.13 21.11 21.07 21.04 21.02 20.99 20.96 20.93 20.9 20.88 20.85 20.82 20.8 20.77 20.75 20.74 20.71 20.69 20.67 20.66 20.64 20.63 20.62 20.61 20.62 82 7.08 7.07 7.04 7.01 6.99 7 6.97 7 6.95 6.95 6.91 6.95 6.92 6.9 6.9 6.91 6.87 6.91 6.87 6.87 6.85 6.85 6.82 6.86 6.84 6.85 6.87 6.86 6.89 6.89 6.91 8.74 8.73 8.73 8.73 8.73 8.73 8.73 8.73 8.72 8.73 8.73 8.73 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.72 8.73 8.73 8.73 6/17/2013 20:50 6/17/2013 21:00 6/17/2013 21:10 6/17/2013 21:20 6/17/2013 21:30 6/17/2013 21:40 6/17/2013 21:50 6/17/2013 22:00 6/17/2013 22:10 6/17/2013 22:20 6/17/2013 22:30 6/17/2013 22:40 6/17/2013 22:50 6/17/2013 23:00 6/17/2013 23:10 6/17/2013 23:20 6/17/2013 23:30 6/17/2013 23:40 6/17/2013 23:50 6/18/2013 0:00 6/18/2013 0:10 6/18/2013 0:20 6/18/2013 0:30 6/18/2013 0:40 6/18/2013 0:50 6/18/2013 1:00 6/18/2013 1:10 6/18/2013 1:20 6/18/2013 1:30 6/18/2013 1:40 6/18/2013 1:50 23.51 23.51 23.5 23.5 23.5 23.5 23.5 23.49 23.48 23.47 23.45 23.43 23.4 23.38 23.35 23.32 23.28 23.25 23.2 23.17 23.12 23.08 23.04 23.01 22.97 22.93 22.89 22.85 22.81 22.77 22.73 6.97 6.96 6.91 6.84 6.85 6.81 6.78 6.75 6.71 6.69 6.65 6.65 6.63 6.61 6.61 6.57 6.58 6.52 6.52 6.49 6.48 6.48 6.44 6.44 6.42 6.43 6.41 6.42 6.41 6.38 6.41 9.01 9.01 9.01 9.01 9.01 9.01 9.01 9 9 9 9 9 9 8.99 8.99 8.99 8.99 8.98 8.98 8.98 8.98 8.98 8.98 8.98 8.98 8.98 8.98 8.98 8.97 8.97 8.97 4/28/2013 22:00 4/28/2013 22:10 4/28/2013 22:20 4/28/2013 22:30 4/28/2013 22:40 4/28/2013 22:50 4/28/2013 23:00 4/28/2013 23:10 4/28/2013 23:20 4/28/2013 23:30 4/28/2013 23:40 4/28/2013 23:50 4/29/2013 0:00 4/29/2013 0:10 4/29/2013 0:20 4/29/2013 0:30 4/29/2013 0:40 4/29/2013 0:50 4/29/2013 1:00 4/29/2013 1:10 4/29/2013 1:20 4/29/2013 1:30 4/29/2013 1:40 4/29/2013 1:50 4/29/2013 2:00 4/29/2013 2:10 4/29/2013 2:20 4/29/2013 2:30 4/29/2013 2:40 4/29/2013 2:50 4/29/2013 3:00 13.2 13.2 13.19 13.18 13.18 13.18 13.18 13.17 13.17 13.16 13.16 13.15 13.14 13.14 13.13 13.12 13.11 13.1 13.09 13.08 13.08 13.07 13.06 13.05 13.04 13.04 13.02 13.02 13.01 13 12.99 8.79 8.72 8.7 8.66 8.68 8.65 8.59 8.59 8.58 8.55 8.56 8.52 8.52 8.5 8.47 8.48 8.43 8.44 8.42 8.42 8.42 8.39 8.38 8.38 8.39 8.36 8.35 8.37 8.39 8.37 8.36 9.04 9.04 9.03 9.04 9.04 9.04 9.04 9.05 9.05 9.05 9.05 9.05 9.06 9.06 9.06 9.06 9.07 9.07 9.08 9.09 9.09 9.08 9.08 9.08 9.08 9.09 9.09 9.1 9.1 9.1 9.11 5/30/2013 6:50 5/30/2013 7:00 5/30/2013 7:10 5/30/2013 7:20 5/30/2013 7:30 5/30/2013 7:40 5/30/2013 7:50 5/30/2013 8:00 5/30/2013 8:10 5/30/2013 8:20 5/30/2013 8:30 5/30/2013 8:40 5/30/2013 8:50 5/30/2013 9:00 5/30/2013 9:10 5/30/2013 9:20 5/30/2013 9:30 5/30/2013 9:40 5/30/2013 9:50 5/30/2013 10:00 5/30/2013 10:10 5/30/2013 10:20 5/30/2013 10:30 5/30/2013 10:40 5/30/2013 10:50 5/30/2013 11:00 5/30/2013 11:10 5/30/2013 11:20 5/30/2013 11:30 5/30/2013 11:40 5/30/2013 11:50 20.62 20.62 20.63 20.63 20.63 20.64 20.64 20.66 20.68 20.7 20.73 20.77 20.81 20.86 20.92 20.98 21.06 21.14 21.2 21.31 21.38 21.48 21.58 21.65 21.75 21.83 21.95 22.05 22.2 22.33 22.44 83 6.95 6.96 6.98 7.02 7.06 7.1 7.19 7.24 7.38 7.44 7.5 7.58 7.61 7.72 7.81 7.96 8.09 8.15 8.25 8.37 8.5 8.62 8.78 8.84 9 9.07 9.28 9.35 9.52 9.62 9.75 8.73 8.73 8.74 8.74 8.74 8.74 8.74 8.75 8.75 8.76 8.76 8.77 8.77 8.77 8.78 8.78 8.79 8.8 8.81 8.82 8.83 8.83 8.84 8.85 8.86 8.87 8.88 8.88 8.89 8.9 8.91 6/18/2013 2:00 6/18/2013 2:10 6/18/2013 2:20 6/18/2013 2:30 6/18/2013 2:40 6/18/2013 2:50 6/18/2013 3:00 6/18/2013 3:10 6/18/2013 3:20 6/18/2013 3:30 6/18/2013 3:40 6/18/2013 3:50 6/18/2013 4:00 6/18/2013 4:10 6/18/2013 4:20 6/18/2013 4:30 6/18/2013 4:40 6/18/2013 4:50 6/18/2013 5:00 6/18/2013 5:10 6/18/2013 5:20 6/18/2013 5:30 6/18/2013 5:40 6/18/2013 5:50 6/18/2013 6:00 6/18/2013 6:10 6/18/2013 6:20 6/18/2013 6:30 6/18/2013 6:40 6/18/2013 6:50 6/18/2013 7:00 22.69 22.66 22.63 22.6 22.57 22.54 22.51 22.48 22.46 22.45 22.44 22.44 22.42 22.38 22.33 22.28 22.23 22.19 22.16 22.12 22.09 22.06 22.04 22.02 21.99 21.97 21.94 21.92 21.89 21.87 21.85 6.41 6.42 6.4 6.39 6.41 6.39 6.4 6.39 6.37 6.39 6.38 6.4 6.37 6.37 6.39 6.39 6.39 6.4 6.39 6.41 6.41 6.4 6.42 6.44 6.39 6.41 6.43 6.41 6.41 6.43 6.46 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.98 8.98 8.98 8.98 8.98 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.97 8.98 8.98 8.98 8.98 4/29/2013 3:10 4/29/2013 3:20 4/29/2013 3:30 4/29/2013 3:40 4/29/2013 3:50 4/29/2013 4:00 4/29/2013 4:10 4/29/2013 4:20 4/29/2013 4:30 4/29/2013 4:40 4/29/2013 4:50 4/29/2013 5:00 4/29/2013 5:10 4/29/2013 5:20 4/29/2013 5:30 4/29/2013 5:40 4/29/2013 5:50 4/29/2013 6:00 4/29/2013 6:10 4/29/2013 6:20 4/29/2013 6:30 4/29/2013 6:40 4/29/2013 6:50 4/29/2013 7:00 4/29/2013 7:10 4/29/2013 7:20 4/29/2013 7:30 4/29/2013 7:40 4/29/2013 7:50 4/29/2013 8:00 4/29/2013 8:10 12.98 12.97 12.96 12.95 12.94 12.93 12.92 12.91 12.9 12.9 12.89 12.88 12.87 12.87 12.86 12.85 12.85 12.84 12.83 12.83 12.82 12.82 12.82 12.81 12.81 12.8 12.8 12.8 12.8 12.8 12.8 8.37 8.4 8.36 8.36 8.37 8.37 8.39 8.41 8.4 8.38 8.39 8.37 8.39 8.4 8.38 8.39 8.42 8.38 8.42 8.39 8.42 8.44 8.43 8.44 8.48 8.42 8.44 8.48 8.5 8.47 8.48 9.11 9.11 9.11 9.11 9.11 9.11 9.11 9.11 9.11 9.12 9.12 9.12 9.12 9.12 9.12 9.12 9.13 9.14 9.13 9.13 9.14 9.14 9.14 9.15 9.14 9.14 9.14 9.14 9.14 9.14 9.14 5/30/2013 12:00 5/30/2013 12:10 5/30/2013 12:20 5/30/2013 12:30 5/30/2013 12:40 5/30/2013 12:50 5/30/2013 13:00 5/30/2013 13:10 5/30/2013 13:20 5/30/2013 13:30 5/30/2013 13:40 5/30/2013 13:50 5/30/2013 14:00 5/30/2013 14:10 5/30/2013 14:20 5/30/2013 14:30 5/30/2013 14:40 5/30/2013 14:50 5/30/2013 15:00 5/30/2013 15:10 5/30/2013 15:20 5/30/2013 15:30 5/30/2013 15:40 5/30/2013 15:50 5/30/2013 16:00 5/30/2013 16:10 5/30/2013 16:20 5/30/2013 16:30 5/30/2013 16:40 5/30/2013 16:50 5/30/2013 17:00 22.53 22.62 22.77 22.87 23.02 23.15 23.21 23.28 23.27 23.41 23.55 23.6 23.67 23.72 23.73 23.82 23.91 23.99 24.05 24.05 24.1 24.12 24.1 24.1 24.12 24.15 24.18 24.16 24.14 24.13 24.12 84 9.79 9.93 10.07 10.14 10.34 10.42 10.44 10.48 10.33 10.55 10.72 10.76 10.79 10.78 10.68 10.75 10.91 10.99 11 10.82 10.76 10.71 10.64 10.49 10.47 10.49 10.48 10.45 10.33 10.23 10.13 8.92 8.93 8.93 8.94 8.95 8.96 8.96 8.97 8.97 8.98 9 9 9.01 9.01 9 9.01 9.02 9.02 9.02 9.02 9.03 9.02 9.01 9.01 9.01 9.01 9.02 9.02 9.02 9.01 9.01 6/18/2013 7:10 6/18/2013 7:20 6/18/2013 7:30 6/18/2013 7:40 6/18/2013 7:50 6/18/2013 8:00 6/18/2013 8:10 6/18/2013 8:20 6/18/2013 8:30 6/18/2013 8:40 6/18/2013 8:50 6/18/2013 9:00 6/18/2013 9:10 6/18/2013 9:20 6/18/2013 9:30 6/18/2013 9:40 6/18/2013 9:50 6/18/2013 10:00 6/18/2013 10:10 6/18/2013 10:20 6/18/2013 10:30 6/18/2013 10:40 6/18/2013 10:50 6/18/2013 11:00 6/18/2013 11:10 6/18/2013 11:20 6/18/2013 11:30 6/18/2013 11:40 6/18/2013 11:50 6/18/2013 12:00 6/18/2013 12:10 21.83 21.82 21.79 21.78 21.77 21.77 21.77 21.78 21.77 21.78 21.8 21.81 21.83 21.84 21.84 21.85 21.91 21.95 22.01 22.07 22.13 22.19 22.27 22.34 22.42 22.52 22.61 22.71 22.81 22.9 23 6.45 6.49 6.51 6.58 6.57 6.61 6.61 6.68 6.71 6.72 6.8 6.81 6.9 6.96 6.89 6.91 6.98 7.04 7.16 7.12 7.2 7.3 7.38 7.45 7.44 7.5 7.53 7.6 7.61 7.72 7.9 8.98 8.98 8.98 8.98 8.99 8.98 8.99 8.99 8.99 8.99 8.99 9 9 9 9.01 9.01 9.01 9.02 9.02 9.03 9.03 9.04 9.04 9.05 9.06 9.06 9.06 9.07 9.07 9.07 9.08 4/29/2013 8:20 4/29/2013 8:30 4/29/2013 8:40 4/29/2013 8:50 4/29/2013 9:00 4/29/2013 9:10 4/29/2013 9:20 4/29/2013 9:30 4/29/2013 9:40 4/29/2013 9:50 4/29/2013 10:00 4/29/2013 10:10 4/29/2013 10:20 4/29/2013 10:30 4/29/2013 10:40 4/29/2013 10:50 4/29/2013 11:00 4/29/2013 11:10 4/29/2013 11:20 4/29/2013 11:30 4/29/2013 11:40 4/29/2013 11:50 4/29/2013 12:00 4/29/2013 12:10 4/29/2013 12:20 4/29/2013 12:30 4/29/2013 12:40 4/29/2013 12:50 4/29/2013 13:00 4/29/2013 13:10 4/29/2013 13:20 12.8 12.8 12.81 12.81 12.82 12.84 12.85 12.86 12.88 12.9 12.91 12.93 12.95 12.97 12.99 13.02 13.06 13.09 13.12 13.17 13.21 13.25 13.3 13.34 13.39 13.43 13.45 13.47 13.49 13.51 13.54 8.52 8.54 8.55 8.57 8.58 8.61 8.68 8.69 8.72 8.78 8.81 8.83 8.85 8.86 8.92 9 9.04 9.08 9.14 9.16 9.21 9.27 9.28 9.32 9.35 9.34 9.34 9.33 9.34 9.34 9.37 9.14 9.14 9.14 9.14 9.14 9.15 9.15 9.14 9.13 9.12 9.12 9.11 9.11 9.11 9.11 9.11 9.11 9.11 9.1 9.1 9.1 9.09 9.09 9.09 9.09 9.08 9.08 9.08 9.08 9.08 9.08 5/30/2013 17:10 5/30/2013 17:20 5/30/2013 17:30 5/30/2013 17:40 5/30/2013 17:50 5/30/2013 18:00 5/30/2013 18:10 5/30/2013 18:20 5/30/2013 18:30 5/30/2013 18:40 5/30/2013 18:50 5/30/2013 19:00 5/30/2013 19:10 5/30/2013 19:20 5/30/2013 19:30 5/30/2013 19:40 5/30/2013 19:50 5/30/2013 20:00 5/30/2013 20:10 5/30/2013 20:20 5/30/2013 20:30 5/30/2013 20:40 5/30/2013 20:50 5/30/2013 21:00 5/30/2013 21:10 5/30/2013 21:20 5/30/2013 21:30 5/30/2013 21:40 5/30/2013 21:50 5/30/2013 22:00 5/30/2013 22:10 24.12 10.04 24.02 9.87 23.97 9.71 23.94 9.51 23.9 9.44 23.89 9.43 23.86 9.42 23.86 9.43 23.81 8.37 23.77 9.1 23.72 9.01 23.66 8.86 23.61 8.69 23.57 8.65 23.53 8.59 23.5 8.5 23.46 8.39 23.41 8.28 23.38 8.16 23.33 8.08 23.29 7.99 23.25 7.92 23.21 7.86 23.17 7.81 23.14 7.72 23.11 7.63 23.07 7.56 23.03 7.49 23.01 7.37 22.99 7.36 22.96 7.24 85 9.01 9 8.99 8.99 8.99 8.99 8.98 8.98 8.97 8.96 8.96 8.95 8.94 8.93 8.93 8.93 8.92 8.91 8.91 8.9 8.9 8.89 8.89 8.89 8.88 8.88 8.88 8.87 8.86 8.86 8.85 6/18/2013 12:20 6/18/2013 12:30 6/18/2013 12:40 6/18/2013 12:50 6/18/2013 13:00 6/18/2013 13:10 6/18/2013 13:20 6/18/2013 13:30 6/18/2013 13:40 6/18/2013 13:50 6/18/2013 14:00 6/18/2013 14:10 6/18/2013 14:20 6/18/2013 14:30 6/18/2013 14:40 6/18/2013 14:50 6/18/2013 15:00 6/18/2013 15:10 6/18/2013 15:20 6/18/2013 15:30 6/18/2013 15:40 6/18/2013 15:50 6/18/2013 16:00 6/18/2013 16:10 6/18/2013 16:20 6/18/2013 16:30 6/18/2013 16:40 6/18/2013 16:50 6/18/2013 17:00 6/18/2013 17:10 6/18/2013 17:20 23.09 23.18 23.26 23.36 23.45 23.54 23.65 23.73 23.82 23.88 23.91 24.05 24.11 24.2 24.26 24.3 24.4 24.49 24.59 24.68 24.75 24.8 24.84 24.83 24.84 24.82 24.8 24.78 24.74 24.7 24.68 7.91 7.94 7.88 8.03 9.08 9.08 9.08 9.08 9.09 9.09 9.09 9.1 9.1 9.1 9.11 9.11 9.12 9.12 9.12 9.12 9.13 9.13 9.13 9.13 9.14 9.14 9.14 9.14 9.14 9.14 9.14 9.14 9.13 9.13 9.13 4/29/2013 13:30 4/29/2013 13:40 4/29/2013 13:50 4/29/2013 14:00 4/29/2013 14:10 4/29/2013 14:20 4/29/2013 14:30 4/29/2013 14:40 4/29/2013 14:50 4/29/2013 15:00 4/29/2013 15:10 4/29/2013 15:20 4/29/2013 15:30 4/29/2013 15:40 4/29/2013 15:50 4/29/2013 16:00 4/29/2013 16:10 4/29/2013 16:20 4/29/2013 16:30 4/29/2013 16:40 4/29/2013 16:50 4/29/2013 17:00 4/29/2013 17:10 4/29/2013 17:20 4/29/2013 17:30 4/29/2013 17:40 4/29/2013 17:50 4/29/2013 18:00 4/29/2013 18:10 4/29/2013 18:20 4/29/2013 18:30 13.57 13.61 13.65 13.71 13.75 13.8 13.86 13.91 14 14.06 14.09 14.11 14.21 14.26 14.3 14.37 14.38 14.34 14.35 14.36 14.41 14.45 14.49 14.51 14.53 14.55 14.58 14.58 14.61 14.62 14.62 9.39 9.37 9.4 9.42 9.43 9.39 9.45 9.49 9.54 9.59 9.5 9.51 9.54 9.58 9.54 9.59 9.6 9.54 9.51 9.47 9.5 9.47 9.49 9.45 9.41 9.35 9.43 9.34 9.33 9.3 9.25 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.08 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.07 9.08 9.08 9.07 9.06 9.06 9.05 9.05 5/30/2013 22:20 5/30/2013 22:30 5/30/2013 22:40 5/30/2013 22:50 5/30/2013 23:00 5/30/2013 23:10 5/30/2013 23:20 5/30/2013 23:30 5/30/2013 23:40 5/30/2013 23:50 5/31/2013 0:00 5/31/2013 0:10 5/31/2013 0:20 5/31/2013 0:30 5/31/2013 0:40 5/31/2013 0:50 5/31/2013 1:00 5/31/2013 1:10 5/31/2013 1:20 5/31/2013 1:30 5/31/2013 1:40 5/31/2013 1:50 5/31/2013 2:00 5/31/2013 2:10 5/31/2013 2:20 5/31/2013 2:30 5/31/2013 2:40 5/31/2013 2:50 5/31/2013 3:00 5/31/2013 3:10 5/31/2013 3:20 22.93 22.9 22.88 22.84 22.81 22.78 22.75 22.74 22.71 22.7 22.68 22.66 22.62 22.59 22.55 22.52 22.48 22.44 22.41 22.38 22.34 22.31 22.28 22.24 22.21 22.17 22.14 22.11 22.08 22.04 22.01 86 7.19 7.14 7.12 7.06 7.03 6.99 6.98 6.96 6.9 6.87 6.89 6.87 6.82 6.8 6.78 6.76 6.78 6.73 6.75 6.71 6.72 6.7 6.69 6.7 6.7 6.68 6.64 6.63 6.64 6.63 6.64 8.85 8.85 8.84 8.84 8.84 8.84 8.84 8.84 8.84 8.84 8.84 8.84 8.84 8.83 8.83 8.83 8.83 8.83 8.83 8.83 8.83 8.83 8.83 8.83 8.82 8.83 8.82 8.82 8.82 8.82 8.82 6/18/2013 17:30 6/18/2013 17:40 6/18/2013 17:50 6/18/2013 18:00 6/18/2013 18:10 6/18/2013 18:20 6/18/2013 18:30 6/18/2013 18:40 6/18/2013 18:50 6/18/2013 19:00 6/18/2013 19:10 6/18/2013 19:20 6/18/2013 19:30 6/18/2013 19:40 6/18/2013 19:50 6/18/2013 20:00 6/18/2013 20:10 6/18/2013 20:20 6/18/2013 20:30 6/18/2013 20:40 6/18/2013 20:50 6/18/2013 21:00 6/18/2013 21:10 6/18/2013 21:20 6/18/2013 21:30 6/18/2013 21:40 6/18/2013 21:50 6/18/2013 22:00 6/18/2013 22:10 6/18/2013 22:20 6/18/2013 22:30 24.64 24.6 24.56 24.52 24.49 24.46 24.44 24.42 24.4 24.37 24.37 24.35 24.32 24.28 24.24 24.19 24.15 24.09 24.05 24.02 23.99 23.96 23.93 23.89 23.86 23.84 23.81 23.78 23.75 23.72 23.69 9.12 9.12 9.12 9.12 9.12 9.12 9.11 9.11 9.11 9.11 9.11 9.11 9.1 9.09 9.09 9.08 9.08 9.08 9.07 9.07 9.06 9.06 9.06 9.06 9.06 9.06 9.06 9.06 9.06 9.05 9.05 4/29/2013 18:40 4/29/2013 18:50 4/29/2013 19:00 4/29/2013 19:10 4/29/2013 19:20 4/29/2013 19:30 4/29/2013 19:40 4/29/2013 19:50 4/29/2013 20:00 4/29/2013 20:10 4/29/2013 20:20 4/29/2013 20:30 4/29/2013 20:40 4/29/2013 20:50 4/29/2013 21:00 4/29/2013 21:10 14.62 14.62 14.62 14.62 14.63 14.63 14.63 14.63 14.62 14.6 14.57 14.53 14.49 14.46 14.42 14.39 9.19 9.18 9.14 9.11 9.09 9.04 9.01 8.95 8.9 8.89 8.85 8.83 8.74 8.71 8.66 8.63 9.05 9.05 9.05 9.06 9.06 9.06 9.06 9.06 9.06 9.06 9.06 9.06 9.06 9.07 9.07 9.06 DO 8.24 8.22 8.16 8.2 8.1 8.07 7.98 7.91 7.88 7.84 7.78 pH 9.25 9.25 9.25 9.25 9.25 9.25 9.24 9.24 9.23 9.23 9.23 5/31/2013 3:30 5/31/2013 3:40 5/31/2013 3:50 5/31/2013 4:00 5/31/2013 4:10 5/31/2013 4:20 5/31/2013 4:30 5/31/2013 4:40 5/31/2013 4:50 5/31/2013 5:00 5/31/2013 5:10 5/31/2013 5:20 5/31/2013 5:30 5/31/2013 5:40 5/31/2013 5:50 5/31/2013 6:00 21.97 21.94 21.91 21.88 21.85 21.82 21.79 21.76 21.74 21.71 21.68 21.66 21.64 21.62 21.61 21.6 6.66 6.62 6.64 6.63 6.63 6.57 6.63 6.58 6.61 6.6 6.62 6.61 6.64 6.59 6.62 6.63 8.83 8.82 8.82 8.82 8.82 8.82 8.82 8.82 8.82 8.82 8.82 8.82 8.82 8.83 8.83 8.83 6/18/2013 22:40 6/18/2013 22:50 6/18/2013 23:00 6/18/2013 23:10 6/18/2013 23:20 6/18/2013 23:30 6/18/2013 23:40 6/18/2013 23:50 6/19/2013 0:00 6/19/2013 0:10 6/19/2013 0:20 6/19/2013 0:30 6/19/2013 0:40 6/19/2013 0:50 6/19/2013 1:00 6/19/2013 1:10 23.67 23.65 23.62 23.59 23.57 23.54 23.51 23.47 23.44 23.41 23.36 23.33 23.29 23.24 23.2 23.15 9.05 9.05 9.05 9.05 9.05 9.05 9.05 9.05 9.05 9.05 9.04 9.04 9.04 9.04 9.04 9.04 Appendix 1. (continued) July 7/26/2013 16:40 7/26/2013 16:50 7/26/2013 17:00 7/26/2013 17:10 7/26/2013 17:20 7/26/2013 17:30 7/26/2013 17:40 7/26/2013 17:50 7/26/2013 18:00 7/26/2013 18:10 7/26/2013 18:20 Temp 24.53 24.56 24.55 24.56 24.57 24.57 24.58 24.57 24.58 24.58 24.56 August Temp 8/6/2013 18:00 22.72 8/6/2013 18:10 22.72 8/6/2013 18:20 22.71 8/6/2013 18:30 22.71 8/6/2013 18:40 22.71 8/6/2013 18:50 22.71 8/6/2013 19:00 22.73 8/6/2013 19:10 22.74 8/6/2013 19:20 22.74 8/6/2013 19:30 22.74 8/6/2013 19:40 22.74 87 DO 9.8 9.69 9.68 9.58 9.52 9.5 9.47 9.46 9.43 9.3 9.26 pH 9.11 9.11 9.11 9.1 9.1 9.1 9.1 9.1 9.1 9.09 9.09 September 9/11/2013 21:00 9/11/2013 21:10 9/11/2013 21:20 9/11/2013 21:30 9/11/2013 21:40 9/11/2013 21:50 9/11/2013 22:00 9/11/2013 22:10 9/11/2013 22:20 9/11/2013 22:30 9/11/2013 22:40 Temp 25.83 25.79 25.75 25.7 25.66 25.61 25.56 25.51 25.46 25.43 25.38 DO 6.35 6.29 6.22 6.14 6.06 5.99 5.92 5.84 5.76 5.71 5.62 pH 9.05 9.04 9.04 9.03 9.02 9.01 9.01 9 8.99 8.99 8.98 7/26/2013 18:30 7/26/2013 18:40 7/26/2013 18:50 7/26/2013 19:00 7/26/2013 19:10 7/26/2013 19:20 7/26/2013 19:30 7/26/2013 19:40 7/26/2013 19:50 7/26/2013 20:00 7/26/2013 20:10 7/26/2013 20:20 7/26/2013 20:30 7/26/2013 20:40 7/26/2013 20:50 7/26/2013 21:00 7/26/2013 21:10 7/26/2013 21:20 7/26/2013 21:30 7/26/2013 21:40 7/26/2013 21:50 7/26/2013 22:00 7/26/2013 22:10 7/26/2013 22:20 7/26/2013 22:30 7/26/2013 22:40 7/26/2013 22:50 7/26/2013 23:00 7/26/2013 23:10 7/26/2013 23:20 7/26/2013 23:30 24.56 24.54 24.52 24.5 24.47 24.44 24.42 24.39 24.36 24.33 24.29 24.26 24.23 24.19 24.16 24.12 24.08 24.05 24.01 23.97 23.93 23.9 23.87 23.83 23.8 23.76 23.72 23.69 23.65 23.62 23.57 7.76 7.67 7.6 7.54 7.47 7.35 7.29 7.23 7.14 7.07 7 6.92 6.84 6.79 6.69 6.59 6.53 6.52 6.41 6.32 6.25 6.18 6.12 6.07 6.01 5.92 5.91 5.84 5.78 5.73 5.68 9.22 9.21 9.21 9.2 9.2 9.2 9.19 9.19 9.18 9.17 9.17 9.16 9.16 9.15 9.14 9.14 9.13 9.13 9.12 9.11 9.11 9.1 9.1 9.09 9.09 9.08 9.07 9.07 9.06 9.06 9.05 8/6/2013 19:50 8/6/2013 20:00 8/6/2013 20:10 8/6/2013 20:20 8/6/2013 20:30 8/6/2013 20:40 8/6/2013 20:50 8/6/2013 21:00 8/6/2013 21:10 8/6/2013 21:20 8/6/2013 21:30 8/6/2013 21:40 8/6/2013 21:50 8/6/2013 22:00 8/6/2013 22:10 8/6/2013 22:20 8/6/2013 22:30 8/6/2013 22:40 8/6/2013 22:50 8/6/2013 23:00 8/6/2013 23:10 8/6/2013 23:20 8/6/2013 23:30 8/6/2013 23:40 8/6/2013 23:50 8/7/2013 0:00 8/7/2013 0:10 8/7/2013 0:20 8/7/2013 0:30 8/7/2013 0:40 8/7/2013 0:50 22.72 22.7 22.68 22.65 22.63 22.6 22.58 22.55 22.53 22.5 22.48 22.46 22.43 22.41 22.38 22.36 22.34 22.32 22.3 22.27 22.24 22.22 22.2 22.18 22.16 22.14 22.12 22.1 22.08 22.06 22.04 88 9.22 9.12 9.06 8.98 8.87 8.75 8.72 8.62 8.55 8.43 8.39 8.34 8.23 8.18 8.09 8.03 7.99 7.89 7.86 7.76 7.73 7.66 7.61 7.56 7.48 7.46 7.41 7.33 7.32 7.26 7.22 9.09 9.08 9.08 9.07 9.07 9.06 9.05 9.05 9.04 9.03 9.03 9.03 9.02 9.01 9.01 9 9 8.99 8.99 8.99 8.98 8.98 8.97 8.96 8.96 8.95 8.95 8.95 8.95 8.94 8.93 9/11/2013 22:50 9/11/2013 23:00 9/11/2013 23:10 9/11/2013 23:20 9/11/2013 23:30 9/11/2013 23:40 9/11/2013 23:50 9/12/2013 0:00 9/12/2013 0:10 9/12/2013 0:20 9/12/2013 0:30 9/12/2013 0:40 9/12/2013 0:50 9/12/2013 1:00 9/12/2013 1:10 9/12/2013 1:20 9/12/2013 1:30 9/12/2013 1:40 9/12/2013 1:50 9/12/2013 2:00 9/12/2013 2:10 9/12/2013 2:20 9/12/2013 2:30 9/12/2013 2:40 9/12/2013 2:50 9/12/2013 3:00 9/12/2013 3:10 9/12/2013 3:20 9/12/2013 3:30 9/12/2013 3:40 9/12/2013 3:50 25.34 25.3 25.25 25.2 25.16 25.12 25.08 25.04 24.98 24.95 24.91 24.87 24.83 24.8 24.76 24.73 24.69 24.66 24.63 24.6 24.56 24.53 24.49 24.46 24.42 24.39 24.35 24.32 24.28 24.25 24.21 5.56 5.49 5.44 5.36 5.34 5.27 5.26 5.18 5.15 5.1 5.05 5.02 4.99 4.96 4.92 4.89 4.85 4.82 4.78 4.75 4.73 4.69 4.67 4.65 4.62 4.6 4.57 4.56 4.53 4.49 4.49 8.98 8.97 8.97 8.96 8.96 8.95 8.95 8.95 8.94 8.94 8.93 8.93 8.93 8.92 8.92 8.92 8.92 8.92 8.91 8.91 8.91 8.91 8.9 8.9 8.9 8.9 8.9 8.9 8.89 8.89 8.89 7/26/2013 23:40 7/26/2013 23:50 7/27/2013 0:00 7/27/2013 0:10 7/27/2013 0:20 7/27/2013 0:30 7/27/2013 0:40 7/27/2013 0:50 7/27/2013 1:00 7/27/2013 1:10 7/27/2013 1:20 7/27/2013 1:30 7/27/2013 1:40 7/27/2013 1:50 7/27/2013 2:00 7/27/2013 2:10 7/27/2013 2:20 7/27/2013 2:30 7/27/2013 2:40 7/27/2013 2:50 7/27/2013 3:00 7/27/2013 3:10 7/27/2013 3:20 7/27/2013 3:30 7/27/2013 3:40 7/27/2013 3:50 7/27/2013 4:00 7/27/2013 4:10 7/27/2013 4:20 7/27/2013 4:30 7/27/2013 4:40 23.54 23.5 23.46 23.41 23.38 23.33 23.29 23.26 23.22 23.17 23.13 23.08 23.04 23 22.95 22.91 22.87 22.84 22.81 22.77 22.73 22.71 22.67 22.64 22.6 22.57 22.53 22.5 22.47 22.43 22.39 5.62 5.59 5.54 5.5 5.46 5.41 5.38 5.35 5.31 5.29 5.26 5.22 5.2 5.17 5.13 5.11 5.1 5.07 5.05 5.04 5 4.99 4.97 4.98 4.93 4.93 4.92 4.87 4.87 4.86 4.85 9.05 9.05 9.04 9.03 9.03 9.03 9.02 9.02 9.01 9.01 9 9 9 9 8.99 8.99 8.99 8.99 8.98 8.98 8.97 8.97 8.97 8.96 8.96 8.96 8.96 8.95 8.95 8.95 8.95 8/7/2013 1:00 8/7/2013 1:10 8/7/2013 1:20 8/16/2013 15:30 8/16/2013 15:40 8/16/2013 15:50 8/16/2013 16:00 8/16/2013 16:10 8/16/2013 16:20 8/16/2013 16:30 8/16/2013 16:40 8/16/2013 16:50 8/16/2013 17:00 8/16/2013 17:10 8/16/2013 17:20 8/16/2013 17:30 8/16/2013 17:40 8/16/2013 17:50 8/16/2013 18:00 8/16/2013 18:10 8/16/2013 18:20 8/16/2013 18:30 8/16/2013 18:40 8/16/2013 18:50 8/16/2013 19:00 8/16/2013 19:10 8/16/2013 19:20 8/16/2013 19:30 8/16/2013 19:40 8/16/2013 19:50 8/16/2013 20:00 22.02 22 21.97 21.21 21.21 21.21 21.24 21.25 21.25 21.26 21.28 21.31 21.34 21.36 21.41 21.44 21.45 21.45 21.46 21.46 21.46 21.45 21.44 21.42 21.4 21.38 21.37 21.35 21.32 21.29 21.26 89 7.18 7.14 7.08 8.54 8.53 8.49 8.52 8.5 8.47 8.47 8.48 8.47 8.46 8.43 8.5 8.52 8.48 8.48 8.45 8.39 8.32 8.25 8.14 8.14 8.04 7.99 7.89 7.82 7.74 7.67 7.56 8.93 8.93 8.92 8.92 8.92 8.92 8.91 8.91 8.91 8.91 8.9 8.9 8.9 8.9 8.89 8.89 8.89 8.89 8.88 8.88 8.88 8.87 8.87 8.87 8.87 8.87 8.87 8.86 8.86 8.86 8.86 9/12/2013 4:00 9/12/2013 4:10 9/12/2013 4:20 9/12/2013 4:30 9/12/2013 4:40 9/12/2013 4:50 9/12/2013 5:00 9/12/2013 5:10 9/12/2013 5:20 9/12/2013 5:30 9/12/2013 5:40 9/12/2013 5:50 9/12/2013 6:00 9/12/2013 6:10 9/12/2013 6:20 9/12/2013 6:30 9/12/2013 6:40 9/12/2013 6:50 9/12/2013 7:00 9/12/2013 7:10 9/12/2013 7:20 9/12/2013 7:30 9/12/2013 7:40 9/12/2013 7:50 9/12/2013 8:00 9/12/2013 8:10 9/12/2013 8:20 9/12/2013 8:30 9/12/2013 8:40 9/12/2013 8:50 9/12/2013 9:00 24.18 24.15 24.12 24.08 24.06 24.03 23.99 23.96 23.94 23.91 23.88 23.85 23.71 23.66 23.56 23.52 23.5 23.47 23.45 23.43 23.41 23.37 23.33 23.3 23.27 23.24 23.2 23.16 23.11 23.05 23.01 4.44 4.43 4.41 4.41 4.36 4.34 4.34 4.32 4.31 4.28 4.28 4.27 4.49 4.54 4.68 4.67 4.65 4.63 4.57 4.53 4.47 4.49 4.5 4.52 4.52 4.54 4.59 4.62 4.66 4.73 4.81 8.89 8.89 8.88 8.88 8.88 8.88 8.88 8.87 8.87 8.87 8.87 8.87 8.87 8.87 8.87 8.87 8.86 8.86 8.86 8.86 8.86 8.86 8.87 8.87 8.87 8.88 8.88 8.88 8.89 8.89 8.89 7/27/2013 4:50 7/27/2013 5:00 7/27/2013 5:10 7/27/2013 5:20 7/27/2013 5:30 7/27/2013 5:40 7/27/2013 5:50 7/27/2013 6:00 7/27/2013 6:10 7/27/2013 6:20 7/27/2013 6:30 7/27/2013 6:40 7/27/2013 6:50 7/27/2013 7:00 7/27/2013 7:10 7/27/2013 7:20 7/27/2013 7:30 7/27/2013 7:40 7/27/2013 7:50 7/27/2013 8:00 7/27/2013 8:10 7/27/2013 8:20 7/27/2013 8:30 7/27/2013 8:40 7/27/2013 8:50 7/27/2013 9:00 7/27/2013 9:10 7/27/2013 9:20 7/27/2013 9:30 7/27/2013 9:40 7/27/2013 9:50 22.37 22.33 22.29 22.25 22.22 22.18 22.15 22.11 22.09 22.06 22.03 22 21.97 21.95 21.92 21.89 21.87 21.85 21.83 21.82 21.8 21.78 21.77 21.76 21.75 21.75 21.74 21.75 21.77 21.81 21.84 4.84 4.83 4.81 4.81 4.82 4.8 4.79 4.75 4.78 4.76 4.76 4.76 4.75 4.75 4.76 4.74 4.74 4.78 4.78 4.79 4.79 4.78 4.84 4.84 4.88 4.93 4.96 5.06 5.15 5.28 5.38 8.94 8.94 8.94 8.94 8.94 8.94 8.94 8.94 8.94 8.94 8.94 8.94 8.95 8.95 8.95 8.95 8.96 8.96 8.97 8.97 8.98 8.98 8.99 8.99 9 9.01 9.01 9.02 9.02 9.04 9.04 8/16/2013 20:10 8/16/2013 20:20 8/16/2013 20:30 8/16/2013 20:40 8/16/2013 20:50 8/16/2013 21:00 8/16/2013 21:10 8/16/2013 21:20 8/16/2013 21:30 8/16/2013 21:40 8/16/2013 21:50 8/16/2013 22:00 8/16/2013 22:10 8/16/2013 22:20 8/16/2013 22:30 8/16/2013 22:40 8/16/2013 22:50 8/16/2013 23:00 8/16/2013 23:10 8/16/2013 23:20 8/16/2013 23:30 8/16/2013 23:40 8/16/2013 23:50 8/17/2013 0:00 8/17/2013 0:10 8/17/2013 0:20 8/17/2013 0:30 8/17/2013 0:40 8/17/2013 0:50 8/17/2013 1:00 8/17/2013 1:10 21.23 21.2 21.17 21.14 21.1 21.08 21.05 21.01 20.98 20.96 20.93 20.9 20.86 20.82 20.79 20.76 20.73 20.7 20.66 20.63 20.6 20.57 20.54 20.51 20.48 20.45 20.42 20.39 20.36 20.33 20.31 90 7.47 7.42 7.32 7.26 7.17 7.12 7.08 7.02 6.97 6.87 6.82 6.76 6.68 6.61 6.58 6.55 6.47 6.43 6.36 6.33 6.25 6.22 6.15 6.1 6.05 6 5.97 5.9 5.88 5.83 5.8 8.86 8.86 8.86 9.24 9.25 9.25 9.25 9.25 9.25 9.26 9.26 9.26 9.26 9.26 9.27 9.27 9.28 9.28 9.28 9.28 9.28 9.27 9.27 9.27 9.27 9.26 9.26 9.25 9.25 9.24 9.23 9/12/2013 9:10 9/12/2013 9:20 9/12/2013 9:30 9/12/2013 9:40 9/12/2013 9:50 9/12/2013 10:00 9/12/2013 10:10 9/12/2013 10:20 9/12/2013 10:30 9/12/2013 10:40 9/12/2013 10:50 9/12/2013 11:00 9/12/2013 11:10 9/12/2013 11:20 9/12/2013 11:30 9/12/2013 11:40 9/12/2013 11:50 9/12/2013 12:00 9/12/2013 12:10 9/12/2013 12:20 9/12/2013 12:30 9/12/2013 12:40 9/12/2013 12:50 9/12/2013 13:00 9/12/2013 13:10 9/12/2013 13:20 9/12/2013 13:30 9/12/2013 13:40 9/12/2013 13:50 9/12/2013 14:00 9/12/2013 14:10 22.98 22.95 22.93 22.88 22.83 22.78 22.74 22.72 22.71 22.7 22.7 22.71 22.73 22.76 22.81 22.88 22.94 22.98 23.03 23.08 23.14 23.19 23.23 23.28 23.33 23.36 23.4 23.45 23.51 23.54 23.56 4.88 4.88 4.89 4.84 4.8 4.8 4.78 4.76 4.73 4.71 4.72 4.72 4.72 4.76 4.81 4.9 4.9 4.9 4.92 4.93 5.01 5.06 5.07 5.14 5.13 5.13 5.1 5.08 5.09 5.04 4.98 8.89 8.9 8.9 8.91 8.92 8.92 8.93 8.94 8.94 8.95 8.95 8.96 8.96 8.97 8.98 8.98 8.99 8.99 9 9.01 9.01 9.02 9.03 9.04 9.05 9.06 9.06 9.07 9.08 9.09 9.1 7/27/2013 10:00 7/27/2013 10:10 7/27/2013 10:20 7/27/2013 10:30 7/27/2013 10:40 7/27/2013 10:50 7/27/2013 11:00 7/27/2013 11:10 7/27/2013 11:20 7/27/2013 11:30 7/27/2013 11:40 7/27/2013 11:50 7/27/2013 12:00 7/27/2013 12:10 7/27/2013 12:20 7/27/2013 12:30 7/27/2013 12:40 7/27/2013 12:50 7/27/2013 13:00 7/27/2013 13:10 7/27/2013 13:20 7/27/2013 13:30 7/27/2013 13:40 7/27/2013 13:50 7/27/2013 14:00 7/27/2013 14:10 7/27/2013 14:20 7/27/2013 14:30 7/27/2013 14:40 7/27/2013 14:50 7/27/2013 15:00 21.85 21.88 21.95 22.03 22.08 22.13 22.17 22.21 22.29 22.44 22.55 22.65 22.79 22.94 23.04 23.12 23.22 23.34 23.37 23.44 23.54 23.65 23.79 23.91 24.03 24.19 24.29 24.45 24.43 24.46 24.49 5.41 5.46 5.56 5.68 5.73 5.8 5.79 5.78 5.86 6.03 6.06 6.15 6.26 6.36 6.49 6.49 6.64 6.7 6.72 6.8 6.9 7 7.13 7.25 7.32 7.43 7.51 7.59 7.57 7.54 7.6 9.05 9.05 9.06 9.06 9.07 9.07 9.08 9.08 9.09 9.09 9.09 9.11 9.11 9.11 9.11 9.12 9.13 9.13 9.13 9.13 9.14 9.14 9.15 9.15 9.16 9.16 9.17 9.17 9.17 9.17 9.17 8/17/2013 1:20 8/17/2013 1:30 8/17/2013 1:40 8/17/2013 1:50 8/17/2013 2:00 8/17/2013 2:10 8/17/2013 2:20 8/17/2013 2:30 8/17/2013 2:40 8/17/2013 2:50 8/17/2013 3:00 8/17/2013 3:10 8/17/2013 3:20 8/17/2013 3:30 8/17/2013 3:40 8/17/2013 3:50 8/17/2013 4:00 8/17/2013 4:10 8/17/2013 4:20 8/17/2013 4:30 8/17/2013 4:40 8/17/2013 4:50 8/17/2013 5:00 8/17/2013 5:10 8/17/2013 5:20 8/17/2013 5:30 8/17/2013 5:40 8/17/2013 5:50 8/17/2013 6:00 8/17/2013 6:10 8/17/2013 6:20 20.28 20.26 20.23 20.2 20.18 20.15 20.11 20.08 20.05 20.01 19.97 19.94 19.91 19.88 19.84 19.81 19.79 19.75 19.73 19.7 19.67 19.64 19.6 19.56 19.53 19.49 19.45 19.41 19.38 19.34 19.31 91 5.77 5.72 5.7 5.65 5.62 5.59 5.56 5.53 5.51 5.48 5.45 5.43 5.39 5.37 5.35 5.31 5.29 5.29 5.27 5.25 5.22 5.21 5.22 5.18 5.17 5.15 5.14 5.14 5.12 5.09 5.07 9.23 9.23 9.22 9.21 9.21 9.2 9.19 9.19 9.18 9.18 9.17 9.16 9.16 9.15 9.14 9.14 9.13 9.12 9.12 9.11 9.11 9.1 9.09 9.09 9.08 9.07 9.07 9.06 9.06 9.05 9.05 9/12/2013 14:20 9/12/2013 14:30 9/12/2013 14:40 9/12/2013 14:50 9/12/2013 15:00 9/12/2013 15:10 9/12/2013 15:20 9/12/2013 15:30 9/12/2013 15:40 9/12/2013 15:50 9/12/2013 16:00 9/12/2013 16:10 9/12/2013 16:20 9/12/2013 16:30 9/12/2013 16:40 9/12/2013 16:50 9/12/2013 17:00 9/12/2013 17:10 9/12/2013 17:20 9/12/2013 17:30 9/12/2013 17:40 9/12/2013 17:50 9/12/2013 18:00 9/12/2013 18:10 9/12/2013 18:20 9/12/2013 18:30 9/12/2013 18:40 9/12/2013 18:50 9/12/2013 19:00 9/12/2013 19:10 9/12/2013 19:20 23.6 23.67 23.73 23.81 23.87 23.9 23.96 23.98 24 24.02 24.04 24.06 24.04 24.04 24.02 24 23.99 23.99 23.98 23.97 23.96 23.94 23.92 23.91 23.9 23.89 23.86 23.82 23.78 23.74 23.69 4.94 4.94 4.9 4.89 4.89 4.87 4.85 4.83 4.81 4.81 4.78 4.79 4.74 4.74 4.72 4.71 4.68 4.69 4.69 4.69 4.7 4.71 4.71 4.73 4.73 4.73 4.73 4.7 4.7 4.64 4.61 9.1 9.11 9.12 9.12 9.14 9.15 9.15 9.16 9.17 9.17 9.17 9.17 9.18 9.17 9.18 9.18 9.19 9.19 9.19 9.19 9.19 9.19 9.19 9.19 9.19 9.18 9.18 9.18 9.17 9.17 9.16 7/27/2013 15:10 7/27/2013 15:20 7/27/2013 15:30 7/27/2013 15:40 7/27/2013 15:50 7/27/2013 16:00 7/27/2013 16:10 7/27/2013 16:20 7/27/2013 16:30 7/27/2013 16:40 7/27/2013 16:50 7/27/2013 17:00 7/27/2013 17:10 7/27/2013 17:20 7/27/2013 17:30 7/27/2013 17:40 7/29/2013 18:00 7/29/2013 18:10 7/29/2013 18:20 7/29/2013 18:30 7/29/2013 18:40 7/29/2013 18:50 7/29/2013 19:00 7/29/2013 19:10 7/29/2013 19:20 7/29/2013 19:30 7/29/2013 19:40 7/29/2013 19:50 7/29/2013 20:00 7/29/2013 20:10 7/29/2013 20:20 24.52 24.48 24.65 24.71 24.7 24.75 24.72 24.7 24.69 24.63 24.62 24.66 24.63 24.65 24.64 24.63 23.57 23.56 23.58 23.57 23.54 23.51 23.47 23.42 23.37 23.32 23.27 23.23 23.17 23.12 23.07 7.57 7.6 7.69 7.7 7.69 7.71 7.7 7.66 7.58 7.52 7.52 7.58 7.52 7.53 7.5 7.43 9.97 9.94 9.93 9.86 9.75 9.63 9.55 9.44 9.36 9.27 9.17 9.1 9 8.92 8.85 9.17 9.17 9.17 9.17 9.16 9.15 9.15 9.15 9.15 9.14 9.15 9.15 9.14 9.14 9.13 9.13 9.13 9.12 9.12 9.11 9.11 9.1 9.1 9.09 9.08 9.08 9.08 9.07 9.07 9.06 9.06 8/17/2013 6:30 8/17/2013 6:40 8/17/2013 6:50 8/17/2013 7:00 8/17/2013 7:10 8/17/2013 7:20 8/17/2013 7:30 8/17/2013 7:40 8/17/2013 7:50 8/17/2013 8:00 8/17/2013 8:10 8/17/2013 8:20 8/17/2013 8:30 8/17/2013 8:40 8/17/2013 8:50 8/17/2013 9:00 8/17/2013 9:10 8/17/2013 9:20 8/17/2013 9:30 8/17/2013 9:40 8/17/2013 9:50 8/17/2013 10:00 8/17/2013 10:10 8/17/2013 10:20 8/17/2013 10:30 8/17/2013 10:40 8/17/2013 10:50 8/17/2013 11:00 8/17/2013 11:10 8/17/2013 11:20 8/17/2013 11:30 19.28 19.25 19.22 19.19 19.18 19.16 19.14 19.13 19.12 19.11 19.11 19.12 19.12 19.14 19.15 19.17 19.2 19.23 19.26 19.29 19.32 19.36 19.4 19.45 19.51 19.59 19.67 19.75 19.85 19.95 20.06 92 5.09 5.09 5.12 5.14 5.17 5.18 5.24 5.27 5.28 5.33 5.38 5.45 5.48 5.56 5.59 5.68 5.67 5.76 5.8 5.85 5.87 5.98 6.02 6.12 6.2 6.31 6.44 6.57 6.69 6.84 6.97 9.04 9.03 9.03 9.02 9.02 9.02 9.01 9 9 9 8.99 8.99 8.98 8.98 8.97 8.97 8.96 8.96 8.96 8.96 8.95 8.95 8.95 8.95 8.94 8.94 8.94 8.94 8.93 8.93 8.93 9/12/2013 19:30 9/12/2013 19:40 9/12/2013 19:50 9/12/2013 20:00 9/12/2013 20:10 9/12/2013 20:20 9/12/2013 20:30 9/12/2013 20:40 9/12/2013 20:50 9/12/2013 21:00 9/12/2013 21:10 9/12/2013 21:20 9/12/2013 21:30 9/12/2013 21:40 9/12/2013 21:50 9/12/2013 22:00 9/12/2013 22:10 9/12/2013 22:20 9/12/2013 22:30 9/12/2013 22:40 9/12/2013 22:50 9/12/2013 23:00 9/12/2013 23:10 9/12/2013 23:20 9/12/2013 23:30 9/12/2013 23:40 9/12/2013 23:50 9/13/2013 0:00 9/13/2013 0:10 9/13/2013 0:20 9/13/2013 0:30 23.63 23.58 23.53 23.48 23.43 23.39 23.33 23.29 23.25 23.21 23.18 23.14 23.1 23.07 23.04 23 22.95 22.9 22.84 22.8 22.75 22.7 22.65 22.61 22.56 22.52 22.47 22.43 22.39 22.34 22.3 4.57 4.57 4.51 4.5 4.48 4.43 4.42 4.41 4.38 4.37 4.35 4.33 4.29 4.3 4.25 4.24 4.22 4.19 4.18 4.15 4.15 4.11 4.09 4.07 4.06 4.02 4.01 3.97 3.96 3.95 3.96 9.16 9.15 9.14 9.14 9.13 9.12 9.11 9.1 9.1 9.09 9.08 9.07 9.06 9.05 9.05 9.04 9.03 9.03 9.02 9.01 9.01 9 8.99 8.99 8.98 8.98 8.97 8.97 8.97 8.96 8.95 7/29/2013 20:30 7/29/2013 20:40 7/29/2013 20:50 7/29/2013 21:00 7/29/2013 21:10 7/29/2013 21:20 7/29/2013 21:30 7/29/2013 21:40 7/29/2013 21:50 7/29/2013 22:00 7/29/2013 22:10 7/29/2013 22:20 7/29/2013 22:30 7/29/2013 22:40 7/29/2013 22:50 7/29/2013 23:00 7/29/2013 23:10 7/29/2013 23:20 7/29/2013 23:30 7/29/2013 23:40 7/29/2013 23:50 7/30/2013 0:00 7/30/2013 0:10 7/30/2013 0:20 7/30/2013 0:30 7/30/2013 0:40 7/30/2013 0:50 7/30/2013 1:00 7/30/2013 1:10 7/30/2013 1:20 7/30/2013 1:30 23.03 22.98 22.92 22.87 22.82 22.77 22.71 22.67 22.62 22.58 22.53 22.49 22.44 22.39 22.35 22.3 22.26 22.21 22.16 22.12 22.07 22.01 21.97 21.92 21.87 21.82 21.77 21.72 21.67 21.61 21.57 8.7 8.65 8.56 8.53 8.41 8.33 8.23 8.16 8.07 7.97 7.92 7.85 7.79 7.69 7.64 7.58 7.55 7.46 7.41 7.34 7.29 7.23 7.2 7.13 7.08 7.05 7.02 6.98 6.94 6.9 6.86 9.05 9.05 9.04 9.04 9.03 9.03 9.02 9.02 9.01 9.01 9 9 9 8.99 8.99 8.98 8.98 8.98 8.97 8.97 8.96 8.96 8.96 8.95 8.95 8.94 8.94 8.94 8.94 8.93 8.93 8/17/2013 11:40 8/17/2013 11:50 8/17/2013 12:00 8/17/2013 12:10 8/17/2013 12:20 8/17/2013 12:30 8/17/2013 12:40 8/17/2013 12:50 8/17/2013 13:00 8/17/2013 13:10 8/17/2013 13:20 8/17/2013 13:30 8/17/2013 13:40 8/17/2013 13:50 8/17/2013 14:00 8/17/2013 14:10 8/17/2013 14:20 8/17/2013 14:30 8/17/2013 14:40 8/17/2013 14:50 8/17/2013 15:00 8/17/2013 15:10 8/17/2013 15:20 8/17/2013 15:30 8/17/2013 15:40 8/17/2013 15:50 8/17/2013 16:00 8/17/2013 16:10 8/17/2013 16:20 8/17/2013 16:30 8/17/2013 16:40 20.18 20.29 20.37 20.47 20.59 20.72 20.82 20.87 20.93 21.03 21.13 21.27 21.34 21.54 21.6 21.82 22.03 22.19 22.15 22.23 22.22 22.26 22.38 22.5 22.5 22.46 22.46 22.47 22.47 22.56 22.54 93 7.1 7.24 7.34 7.4 7.49 7.55 7.6 7.65 7.66 7.75 7.62 7.71 7.86 7.99 8.02 8.06 8.24 8.33 8.41 8.47 8.36 8.47 8.56 8.68 8.82 8.89 8.88 8.91 8.9 8.86 8.76 8.93 8.93 8.92 8.92 8.92 8.93 8.92 8.93 8.93 8.93 8.93 8.94 8.94 8.94 8.94 8.95 8.95 8.95 8.96 8.96 8.96 8.97 8.97 8.97 8.98 8.99 9 9.01 9.02 9.03 9.04 9/13/2013 0:40 9/13/2013 0:50 9/13/2013 1:00 9/13/2013 1:10 9/13/2013 1:20 9/13/2013 1:30 9/13/2013 1:40 9/13/2013 1:50 9/13/2013 2:00 9/13/2013 2:10 9/13/2013 2:20 9/13/2013 2:30 9/13/2013 2:40 9/13/2013 2:50 9/13/2013 3:00 9/13/2013 3:10 9/13/2013 3:20 9/13/2013 3:30 9/13/2013 3:40 9/13/2013 3:50 9/13/2013 4:00 9/13/2013 4:10 9/13/2013 4:20 9/13/2013 4:30 9/13/2013 4:40 9/13/2013 4:50 9/13/2013 5:00 9/13/2013 5:10 9/13/2013 5:20 9/13/2013 5:30 9/13/2013 5:40 22.25 22.21 22.16 22.11 22.06 22.02 21.97 21.92 21.87 21.83 21.78 21.73 21.68 21.63 21.58 21.54 21.5 21.45 21.41 21.36 21.31 21.26 21.22 21.16 21.11 21.06 21.01 20.95 20.9 20.85 20.8 3.92 3.91 3.91 3.87 3.88 3.88 3.86 3.86 3.83 3.81 3.8 3.78 3.77 3.75 3.75 3.74 3.75 3.74 3.73 3.72 3.71 3.71 3.72 3.75 3.73 3.74 3.73 3.72 3.72 3.73 3.73 8.95 8.95 8.94 8.94 8.94 8.93 8.93 8.93 8.92 8.92 8.92 8.91 8.91 8.91 8.91 8.9 8.9 8.9 8.89 8.89 8.89 8.89 8.89 8.89 8.88 8.88 8.88 8.88 8.88 8.88 8.88 7/30/2013 1:40 21.51 7/30/2013 1:50 21.47 6.85 8.93 6.81 8.92 8/17/2013 16:50 8/17/2013 17:00 22.52 22.51 8.65 9.05 8.57 9.06 9/13/2013 5:50 9/13/2013 6:00 20.75 3.74 20.69 3.75 8.88 8.87 Appendix 1. (continued) October 10/21/2013 21:00 10/21/2013 21:10 10/21/2013 21:20 10/21/2013 21:30 10/21/2013 21:40 10/21/2013 21:50 10/21/2013 22:00 10/21/2013 22:10 10/21/2013 22:20 10/21/2013 22:30 10/21/2013 22:40 10/21/2013 22:50 10/21/2013 23:00 10/21/2013 23:10 10/21/2013 23:20 10/21/2013 23:30 10/21/2013 23:40 10/21/2013 23:50 10/22/2013 0:00 10/22/2013 0:10 10/22/2013 0:20 10/22/2013 0:30 10/22/2013 0:40 10/22/2013 0:50 10/22/2013 1:00 10/22/2013 1:10 10/22/2013 1:20 Temp 13.15 13.14 13.12 13.11 13.09 13.07 13.04 13.02 12.99 12.96 12.92 12.90 12.87 12.84 12.80 12.77 12.74 12.70 12.66 12.63 12.59 12.55 12.51 12.47 12.43 12.38 12.34 DO 8.24 8.16 8.06 8.02 7.95 7.90 7.84 7.80 7.74 7.71 7.64 7.64 7.56 7.54 7.53 7.43 7.37 7.38 7.34 7.33 7.26 7.25 7.18 7.20 7.15 7.14 7.11 pH 9.08 9.11 9.12 9.12 9.12 9.11 9.11 9.10 9.10 9.09 9.09 9.08 9.08 9.07 9.06 9.06 9.05 9.05 9.05 9.04 9.04 9.03 9.03 9.03 9.02 9.02 9.01 November 11/8/2013 18:00 11/8/2013 18:10 11/8/2013 18:20 11/8/2013 18:30 11/8/2013 18:40 11/8/2013 18:50 11/8/2013 19:00 11/8/2013 19:10 11/8/2013 19:20 11/8/2013 19:30 11/8/2013 19:40 11/8/2013 19:50 11/8/2013 20:00 11/8/2013 20:10 11/8/2013 20:20 11/8/2013 20:30 11/8/2013 20:40 11/8/2013 20:50 11/8/2013 21:00 11/8/2013 21:10 11/8/2013 21:20 11/8/2013 21:30 11/8/2013 21:40 11/8/2013 21:50 11/8/2013 22:00 11/8/2013 22:10 11/8/2013 22:20 Temp 9.87 9.87 9.86 9.85 9.84 9.84 9.84 9.83 9.83 9.82 9.82 9.80 9.79 9.78 9.75 9.74 9.72 9.70 9.69 9.67 9.65 9.63 9.62 9.61 9.60 9.59 9.58 94 DO 11.47 11.45 11.35 11.29 11.24 11.13 11.03 11.00 10.90 10.86 10.74 10.68 10.59 10.54 10.46 10.37 10.28 10.23 10.18 10.12 10.06 10.01 9.94 9.87 9.82 9.77 9.79 pH 9.08 9.12 9.14 9.14 9.14 9.14 9.14 9.14 9.14 9.14 9.13 9.13 9.12 9.12 9.12 9.11 9.11 9.10 9.10 9.09 9.09 9.09 9.08 9.08 9.07 9.07 9.07 December 12/13/2013 20:00 12/13/2013 20:10 12/13/2013 20:20 12/13/2013 20:30 12/13/2013 20:40 12/13/2013 20:50 12/13/2013 21:00 12/13/2013 21:10 12/13/2013 21:20 12/13/2013 21:30 12/13/2013 21:40 12/13/2013 21:50 12/13/2013 22:00 12/13/2013 22:10 12/13/2013 22:20 12/13/2013 22:30 12/13/2013 22:40 12/13/2013 22:50 12/13/2013 23:00 12/13/2013 23:10 12/13/2013 23:20 12/13/2013 23:30 12/13/2013 23:40 12/13/2013 23:50 12/14/2013 0:00 12/14/2013 0:10 12/14/2013 0:20 Temp 2.65 2.61 2.56 2.52 2.47 2.45 2.43 2.42 2.39 2.36 2.33 2.28 2.22 2.18 2.13 2.09 2.04 1.99 1.95 1.90 1.85 1.79 1.76 1.71 1.68 1.69 1.69 DO 14.70 14.65 14.50 14.38 14.31 14.26 14.08 14.03 13.89 13.83 13.82 13.62 13.60 13.54 13.43 13.44 13.35 13.35 13.22 13.26 13.23 13.20 13.18 13.16 13.13 13.13 13.09 pH 9.70 9.69 9.69 9.68 9.67 9.66 9.65 9.64 9.63 9.63 9.62 9.61 9.60 9.60 9.59 9.58 9.58 9.57 9.57 9.57 9.56 9.56 9.55 9.55 9.54 9.54 9.53 10/22/2013 1:30 10/22/2013 1:40 10/22/2013 1:50 10/22/2013 2:00 10/22/2013 2:10 10/22/2013 2:20 10/22/2013 2:30 10/22/2013 2:40 10/22/2013 2:50 10/22/2013 3:00 10/22/2013 3:10 10/22/2013 3:20 10/22/2013 3:30 10/22/2013 3:40 10/22/2013 3:50 10/22/2013 4:00 10/22/2013 4:10 10/22/2013 4:20 10/22/2013 4:30 10/22/2013 4:40 10/22/2013 4:50 10/22/2013 5:00 10/22/2013 5:10 10/22/2013 5:20 10/22/2013 5:30 10/22/2013 5:40 10/22/2013 5:50 10/22/2013 6:00 10/22/2013 6:10 10/22/2013 6:20 10/22/2013 6:30 10/22/2013 6:40 10/22/2013 6:50 10/22/2013 7:00 12.30 12.26 12.21 12.17 12.12 12.07 12.03 11.98 11.93 11.89 11.85 11.80 11.76 11.71 11.67 11.62 11.58 11.54 11.50 11.45 11.40 11.36 11.32 11.28 11.23 11.19 11.15 11.12 11.08 11.04 11.00 10.96 10.93 10.89 7.12 7.05 7.07 7.04 7.01 7.00 6.99 6.97 6.98 6.96 6.93 6.94 6.95 6.96 6.92 6.93 6.92 6.92 6.90 6.91 6.89 6.89 6.92 6.93 6.92 6.90 6.91 6.94 6.89 6.90 6.91 6.91 6.94 6.92 9.01 9.01 9.00 9.00 9.00 8.99 8.99 8.99 8.98 8.98 8.98 8.97 8.97 8.97 8.97 8.96 8.96 8.96 8.96 8.96 8.96 8.96 8.96 8.96 8.96 8.95 8.95 8.95 8.95 8.95 8.95 8.95 8.95 8.95 11/8/2013 22:30 11/8/2013 22:40 11/8/2013 22:50 11/8/2013 23:00 11/8/2013 23:10 11/8/2013 23:20 11/8/2013 23:30 11/8/2013 23:40 11/8/2013 23:50 11/9/2013 0:00 11/9/2013 0:10 11/9/2013 0:20 11/9/2013 0:30 11/9/2013 0:40 11/9/2013 0:50 11/9/2013 1:00 11/9/2013 1:10 11/9/2013 1:20 11/9/2013 1:30 11/9/2013 1:40 11/9/2013 1:50 11/9/2013 2:00 11/9/2013 2:10 11/9/2013 2:20 11/9/2013 2:30 11/9/2013 2:40 11/9/2013 2:50 11/9/2013 3:00 11/9/2013 3:10 11/9/2013 3:20 11/9/2013 3:30 11/9/2013 3:40 11/9/2013 3:50 11/9/2013 4:00 9.56 9.54 9.52 9.51 9.49 9.47 9.45 9.44 9.41 9.39 9.37 9.34 9.32 9.30 9.27 9.26 9.23 9.22 9.20 9.18 9.17 9.15 9.13 9.12 9.10 9.08 9.07 9.06 9.04 9.03 9.02 9.01 8.99 8.98 95 9.70 9.68 9.64 9.55 9.57 9.53 9.46 9.47 9.41 9.37 9.39 9.36 9.32 9.34 9.31 9.29 9.26 9.24 9.21 9.22 9.19 9.17 9.20 9.17 9.15 9.18 9.10 9.11 9.16 9.14 9.13 9.10 9.10 9.13 9.06 9.06 9.06 9.05 9.05 9.05 9.05 9.05 9.04 9.04 9.04 9.04 9.04 9.04 9.04 9.03 9.04 9.03 9.03 9.03 9.03 9.03 9.02 9.03 9.03 9.02 9.02 9.03 9.02 9.02 9.02 9.02 9.03 9.02 12/14/2013 0:30 12/14/2013 0:40 12/14/2013 0:50 12/14/2013 1:00 12/14/2013 1:10 12/14/2013 1:20 12/14/2013 1:30 12/14/2013 1:40 12/14/2013 1:50 12/14/2013 2:00 12/14/2013 2:10 12/14/2013 2:20 12/14/2013 2:30 12/14/2013 2:40 12/14/2013 2:50 12/14/2013 3:00 12/14/2013 3:10 12/14/2013 3:20 12/14/2013 3:30 12/14/2013 3:40 12/14/2013 3:50 12/14/2013 4:00 12/14/2013 4:10 12/14/2013 4:20 12/14/2013 4:30 12/14/2013 4:40 12/14/2013 4:50 12/14/2013 5:00 12/14/2013 5:10 12/14/2013 5:20 12/14/2013 5:30 12/14/2013 5:40 12/14/2013 5:50 12/14/2013 6:00 1.70 1.70 1.70 1.69 1.68 1.67 1.67 1.66 1.65 1.65 1.65 1.64 1.65 1.64 1.63 1.62 1.62 1.62 1.61 1.59 1.55 1.55 1.56 1.58 1.59 1.59 1.58 1.58 1.59 1.59 1.60 1.61 1.62 1.63 13.04 12.99 13.00 13.01 13.01 13.03 13.02 13.02 12.97 12.98 12.99 12.96 12.95 12.95 12.94 12.93 12.90 12.91 12.91 12.87 12.82 12.80 12.79 12.76 12.76 12.74 12.74 12.73 12.67 12.67 12.68 12.64 12.62 12.61 9.53 9.53 9.52 9.52 9.52 9.52 9.51 9.51 9.51 9.51 9.51 9.51 9.51 9.51 9.50 9.50 9.50 9.50 9.50 9.49 9.49 9.49 9.49 9.48 9.48 9.48 9.48 9.48 9.47 9.47 9.47 9.47 9.46 9.46 10/22/2013 7:10 10/22/2013 7:20 10/22/2013 7:30 10/22/2013 7:40 10/22/2013 7:50 10/22/2013 8:00 10/22/2013 8:10 10/22/2013 8:20 10/22/2013 8:30 10/22/2013 8:40 10/22/2013 8:50 10/22/2013 9:00 10/22/2013 9:10 10/22/2013 9:20 10/22/2013 9:30 10/22/2013 9:40 10/22/2013 9:50 10/22/2013 10:00 10/22/2013 10:10 10/22/2013 10:20 10/22/2013 10:30 10/22/2013 10:40 10/22/2013 10:50 10/22/2013 11:00 10/22/2013 11:10 10/22/2013 11:20 10/22/2013 11:30 10/22/2013 11:40 10/22/2013 11:50 10/22/2013 12:00 10/22/2013 12:10 10/22/2013 12:20 10/22/2013 12:30 10/22/2013 12:40 10.85 10.81 10.77 10.74 10.71 10.69 10.66 10.63 10.61 10.60 10.59 10.58 10.59 10.59 10.59 10.59 10.58 10.59 10.59 10.60 10.62 10.63 10.65 10.68 10.71 10.76 10.80 10.84 10.88 10.94 11.01 11.05 11.09 11.14 6.93 6.95 6.94 6.97 7.01 7.04 7.08 7.12 7.19 7.24 7.36 7.41 7.48 7.55 7.56 7.67 7.74 7.80 7.81 7.92 7.95 8.07 8.17 8.24 8.37 8.45 8.59 8.68 8.80 8.87 8.99 9.04 9.14 9.23 8.95 8.95 8.95 8.95 8.95 8.95 8.95 8.96 8.96 8.97 8.98 8.98 8.98 8.99 8.99 9.00 9.00 9.01 9.01 9.01 9.02 9.03 9.04 9.05 9.05 9.06 9.07 9.08 9.08 9.09 9.10 9.11 9.12 9.13 11/9/2013 4:10 11/9/2013 4:20 11/9/2013 4:30 11/9/2013 4:40 11/9/2013 4:50 11/9/2013 5:00 11/9/2013 5:10 11/9/2013 5:20 11/9/2013 5:30 11/9/2013 5:40 11/9/2013 5:50 11/9/2013 6:00 11/9/2013 6:10 11/9/2013 6:20 11/9/2013 6:30 11/9/2013 6:40 11/9/2013 6:50 11/9/2013 7:00 11/9/2013 7:10 11/9/2013 7:20 11/9/2013 7:30 11/9/2013 7:40 11/9/2013 7:50 11/9/2013 8:00 11/9/2013 8:10 11/9/2013 8:20 11/9/2013 8:30 11/9/2013 8:40 11/9/2013 8:50 11/9/2013 9:00 11/9/2013 9:10 11/9/2013 9:20 11/9/2013 9:30 11/9/2013 9:40 8.97 8.95 8.93 8.92 8.89 8.87 8.85 8.82 8.80 8.79 8.78 8.76 8.74 8.72 8.71 8.69 8.67 8.65 8.64 8.61 8.60 8.58 8.57 8.57 8.56 8.55 8.54 8.54 8.55 8.56 8.56 8.58 8.61 8.62 96 9.09 9.11 9.06 9.12 9.10 9.08 9.05 9.08 9.07 9.05 9.06 9.09 9.09 9.04 9.01 9.05 9.03 9.02 9.02 9.05 9.08 9.05 9.09 9.09 9.10 9.17 9.22 9.23 9.28 9.34 9.38 9.42 9.45 9.53 9.02 9.02 9.02 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.03 9.04 9.04 9.04 9.05 9.05 9.05 9.05 9.06 12/14/2013 6:10 12/14/2013 6:20 12/14/2013 6:30 12/14/2013 6:40 12/14/2013 6:50 12/14/2013 7:00 12/14/2013 7:10 12/14/2013 7:20 12/14/2013 7:30 12/14/2013 7:40 12/14/2013 7:50 12/14/2013 8:00 12/14/2013 8:10 12/14/2013 8:20 12/14/2013 8:30 12/14/2013 8:40 12/14/2013 8:50 12/14/2013 9:00 12/14/2013 9:10 12/14/2013 9:20 12/14/2013 9:30 12/14/2013 9:40 12/14/2013 9:50 12/14/2013 10:00 12/14/2013 10:10 12/14/2013 10:20 12/14/2013 10:30 12/14/2013 10:40 12/14/2013 10:50 12/14/2013 11:00 12/14/2013 11:10 12/14/2013 11:20 12/14/2013 11:30 12/14/2013 11:40 1.65 1.67 1.69 1.71 1.72 1.74 1.74 1.75 1.73 1.72 1.73 1.73 1.74 1.75 1.76 1.77 1.77 1.78 1.79 1.81 1.83 1.85 1.86 1.86 1.86 1.85 1.85 1.84 1.82 1.83 1.83 1.83 1.84 1.85 12.64 12.60 12.57 12.58 12.54 12.55 12.51 12.48 12.49 12.45 12.44 12.47 12.48 12.47 12.46 12.46 12.56 12.51 12.58 12.62 12.67 12.73 12.82 12.83 12.90 13.00 13.07 13.09 13.23 13.29 13.40 13.52 13.75 13.83 9.46 9.46 9.46 9.45 9.45 9.45 9.45 9.45 9.45 9.45 9.45 9.45 9.45 9.44 9.45 9.44 9.44 9.45 9.45 9.45 9.45 9.45 9.45 9.45 9.46 9.46 9.46 9.47 9.47 9.48 9.49 9.49 9.50 9.51 10/22/2013 12:50 10/22/2013 13:00 10/22/2013 13:10 10/22/2013 13:20 10/22/2013 13:30 10/22/2013 13:40 10/22/2013 13:50 10/22/2013 14:00 10/22/2013 14:10 10/22/2013 14:20 10/22/2013 14:30 10/22/2013 14:40 10/22/2013 14:50 10/22/2013 15:00 10/22/2013 15:10 10/22/2013 15:20 10/22/2013 15:30 10/22/2013 15:40 10/22/2013 15:50 10/22/2013 16:00 10/22/2013 16:10 10/22/2013 16:20 10/22/2013 16:30 10/22/2013 16:40 10/22/2013 16:50 10/22/2013 17:00 10/22/2013 17:10 10/22/2013 17:20 10/22/2013 17:30 10/22/2013 17:40 10/22/2013 17:50 10/22/2013 18:00 10/22/2013 18:10 10/22/2013 18:20 11.20 11.26 11.32 11.35 11.38 11.42 11.45 11.48 11.49 11.50 11.52 11.52 11.53 11.52 11.52 11.51 11.52 11.52 11.53 11.53 11.53 11.53 11.53 11.54 11.54 11.54 11.54 11.53 11.53 11.52 11.52 11.51 11.50 11.49 9.36 9.42 9.57 9.71 9.80 9.94 10.01 10.09 10.21 10.27 10.38 10.39 10.45 10.46 10.48 10.52 10.55 10.59 10.60 10.58 10.61 10.60 10.57 10.58 10.62 10.64 10.55 10.52 10.45 10.42 10.38 10.31 10.19 10.11 9.14 9.15 9.16 9.17 9.17 9.18 9.19 9.20 9.21 9.22 9.23 9.23 9.24 9.25 9.25 9.26 9.26 9.27 9.28 9.28 9.29 9.30 9.30 9.30 9.31 9.31 9.31 9.32 9.32 9.32 9.32 9.32 9.32 9.32 11/9/2013 9:50 11/9/2013 10:00 11/9/2013 10:10 11/9/2013 10:20 11/9/2013 10:30 11/9/2013 10:40 11/9/2013 10:50 11/9/2013 11:00 11/9/2013 11:10 11/9/2013 11:20 11/9/2013 11:30 11/9/2013 11:40 11/9/2013 11:50 11/9/2013 12:00 11/9/2013 12:10 11/9/2013 12:20 11/9/2013 12:30 11/9/2013 12:40 11/9/2013 12:50 11/9/2013 13:00 11/9/2013 13:10 11/9/2013 13:20 11/9/2013 13:30 11/9/2013 13:40 11/9/2013 13:50 11/9/2013 14:00 11/9/2013 14:10 11/9/2013 14:20 11/9/2013 14:30 11/9/2013 14:40 11/9/2013 14:50 11/9/2013 15:00 11/9/2013 15:10 11/9/2013 15:20 8.65 8.67 8.71 8.74 8.77 8.81 8.85 8.89 8.94 8.99 9.05 9.11 9.17 9.23 9.30 9.36 9.44 9.51 9.58 9.65 9.72 9.78 9.85 9.92 9.99 10.07 10.14 10.20 10.25 10.29 10.33 10.36 10.40 10.44 97 9.59 9.70 9.69 9.81 9.89 9.94 9.98 10.09 10.19 10.26 10.33 10.44 10.52 10.55 10.67 10.76 10.81 10.94 10.99 11.06 11.11 11.18 11.31 11.35 11.37 11.40 11.56 11.65 11.67 11.70 11.68 11.66 11.70 11.73 9.06 9.07 9.07 9.08 9.08 9.08 9.09 9.09 9.10 9.11 9.11 9.12 9.13 9.13 9.14 9.14 9.14 9.15 9.16 9.16 9.17 9.18 9.18 9.19 9.20 9.20 9.21 9.21 9.22 9.22 9.22 9.23 9.23 9.23 12/14/2013 11:50 12/14/2013 12:00 12/14/2013 12:10 12/14/2013 12:20 12/14/2013 12:30 12/14/2013 12:40 12/14/2013 12:50 12/14/2013 13:00 12/14/2013 13:10 12/14/2013 13:20 12/14/2013 13:30 12/14/2013 13:40 12/14/2013 13:50 12/14/2013 14:00 12/14/2013 14:10 12/14/2013 14:20 12/14/2013 14:30 12/14/2013 14:40 12/14/2013 14:50 12/14/2013 15:00 12/14/2013 15:10 12/14/2013 15:20 12/14/2013 15:30 12/14/2013 15:40 12/14/2013 15:50 12/14/2013 16:00 12/14/2013 16:10 12/14/2013 16:20 12/14/2013 16:30 12/14/2013 16:40 12/14/2013 16:50 12/14/2013 17:00 12/14/2013 17:10 12/14/2013 17:20 1.87 1.87 1.86 1.83 1.82 1.83 1.81 1.78 1.78 1.80 1.82 1.84 1.86 1.86 1.87 1.87 1.87 1.87 1.87 1.86 1.86 1.85 1.85 1.85 1.85 1.85 1.87 1.89 1.89 1.91 1.92 1.93 1.95 1.97 13.93 13.94 13.96 14.16 14.27 14.47 14.51 14.60 14.70 14.80 14.90 15.03 15.15 15.27 15.37 15.43 15.54 15.59 15.66 15.64 15.71 15.72 15.75 15.80 15.92 15.91 15.79 15.81 15.78 15.75 15.66 15.60 15.59 15.49 9.52 9.53 9.53 9.54 9.55 9.56 9.57 9.58 9.59 9.59 9.61 9.61 9.62 9.63 9.64 9.65 9.66 9.66 9.67 9.68 9.68 9.69 9.69 9.70 9.71 9.71 9.71 9.72 9.72 9.72 9.72 9.72 9.71 9.71 10/22/2013 18:30 10/22/2013 18:40 10/22/2013 18:50 10/22/2013 19:00 10/22/2013 19:10 10/22/2013 19:20 10/22/2013 19:30 10/22/2013 19:40 10/22/2013 19:50 10/22/2013 20:00 10/22/2013 20:10 10/22/2013 20:20 10/22/2013 20:30 10/22/2013 20:40 10/22/2013 20:50 10/22/2013 21:00 10/22/2013 21:10 10/22/2013 21:20 10/22/2013 21:30 10/22/2013 21:40 10/22/2013 21:50 10/22/2013 22:00 10/22/2013 22:10 10/22/2013 22:20 10/22/2013 22:30 10/22/2013 22:40 10/22/2013 22:50 10/22/2013 23:00 10/22/2013 23:10 10/22/2013 23:20 10/22/2013 23:30 10/22/2013 23:40 10/22/2013 23:50 10/23/2013 0:00 11.48 11.46 11.43 11.40 11.38 11.36 11.34 11.33 11.32 11.30 11.28 11.27 11.26 11.25 11.24 11.24 11.23 11.21 11.21 11.20 11.19 11.18 11.17 11.17 11.16 11.15 11.15 11.14 11.13 11.12 11.11 11.10 11.09 11.09 10.05 9.97 9.90 9.82 9.73 9.69 9.61 9.54 9.44 9.39 9.32 9.21 9.14 9.06 8.98 8.92 8.88 8.77 8.73 8.67 8.62 8.52 8.51 8.39 8.36 8.30 8.29 8.21 8.17 8.13 8.08 8.02 8.00 7.94 9.31 9.31 9.31 9.30 9.30 9.29 9.28 9.28 9.27 9.26 9.25 9.24 9.23 9.22 9.21 9.20 9.19 9.18 9.17 9.16 9.15 9.15 9.14 9.13 9.12 9.11 9.11 9.10 9.09 9.09 9.08 9.07 9.07 9.06 11/9/2013 15:30 11/9/2013 15:40 11/9/2013 15:50 11/9/2013 16:00 11/9/2013 16:10 11/9/2013 16:20 11/9/2013 16:30 11/9/2013 16:40 11/9/2013 16:50 11/9/2013 17:00 11/9/2013 17:10 11/9/2013 17:20 11/9/2013 17:30 11/9/2013 17:40 11/9/2013 17:50 11/9/2013 18:00 11/9/2013 18:10 11/9/2013 18:20 11/9/2013 18:30 11/9/2013 18:40 11/9/2013 18:50 11/9/2013 19:00 11/9/2013 19:10 11/9/2013 19:20 11/9/2013 19:30 11/9/2013 19:40 11/9/2013 19:50 11/9/2013 20:00 11/9/2013 20:10 11/9/2013 20:20 11/9/2013 20:30 11/9/2013 20:40 11/9/2013 20:50 11/9/2013 21:00 10.47 10.49 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.50 10.49 10.48 10.47 10.46 10.45 10.43 10.42 10.41 10.40 10.40 10.39 10.38 10.37 10.36 10.35 10.34 10.33 98 11.83 11.76 11.78 11.79 11.71 11.68 11.68 11.61 11.58 11.58 11.55 11.49 11.46 11.46 11.41 11.34 11.29 11.21 11.14 11.06 11.04 10.90 10.81 10.68 10.64 10.54 10.45 10.34 10.30 10.19 10.12 10.05 9.96 9.96 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.24 9.23 9.23 9.23 9.22 9.22 9.21 9.21 9.20 9.20 9.19 9.18 9.18 9.17 9.17 9.16 9.15 9.15 9.14 12/14/2013 17:30 12/14/2013 17:40 12/14/2013 17:50 12/14/2013 18:00 12/14/2013 18:10 12/14/2013 18:20 12/14/2013 18:30 12/14/2013 18:40 12/14/2013 18:50 12/14/2013 19:00 12/14/2013 19:10 12/14/2013 19:20 12/14/2013 19:30 12/14/2013 19:40 12/14/2013 19:50 12/14/2013 20:00 12/14/2013 20:10 12/14/2013 20:20 12/14/2013 20:30 12/14/2013 20:40 12/14/2013 20:50 12/14/2013 21:00 12/14/2013 21:10 12/14/2013 21:20 12/14/2013 21:30 12/14/2013 21:40 12/14/2013 21:50 12/14/2013 22:00 12/14/2013 22:10 12/14/2013 22:20 12/14/2013 22:30 12/14/2013 22:40 12/14/2013 22:50 12/14/2013 23:00 1.98 2.01 2.03 2.05 2.07 2.08 2.10 2.12 2.13 2.14 2.15 2.17 2.18 2.20 2.21 2.22 2.24 2.25 2.26 2.26 2.27 2.26 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.27 2.28 15.34 15.35 15.22 15.11 14.98 14.91 14.84 14.69 14.62 14.49 14.41 14.29 14.16 14.05 13.95 13.88 13.76 13.71 13.63 13.53 13.44 13.38 13.32 13.24 13.12 13.04 12.98 12.99 12.95 12.88 12.84 12.76 12.73 12.68 9.71 9.70 9.70 9.69 9.69 9.68 9.67 9.66 9.65 9.65 9.64 9.63 9.62 9.61 9.60 9.59 9.59 9.58 9.57 9.56 9.55 9.54 9.54 9.53 9.52 9.52 9.51 9.50 9.50 9.49 9.48 9.48 9.47 9.47 10/23/2013 0:10 10/23/2013 0:20 10/23/2013 0:30 10/23/2013 0:40 10/23/2013 0:50 10/23/2013 1:00 10/23/2013 1:10 10/23/2013 1:20 10/23/2013 1:30 10/23/2013 1:40 10/23/2013 1:50 10/23/2013 2:00 10/23/2013 2:10 10/23/2013 2:20 10/23/2013 2:30 10/23/2013 2:40 10/23/2013 2:50 10/23/2013 3:00 10/23/2013 3:10 10/23/2013 3:20 10/23/2013 3:30 10/23/2013 3:40 10/23/2013 3:50 10/23/2013 4:00 10/23/2013 4:10 10/23/2013 4:20 10/23/2013 4:30 10/23/2013 4:40 10/23/2013 4:50 10/23/2013 5:00 10/23/2013 5:10 10/23/2013 5:20 10/23/2013 5:30 10/23/2013 5:40 11.07 11.05 11.05 11.04 11.02 10.98 10.97 10.94 10.89 10.83 10.76 10.70 10.64 10.59 10.54 10.46 10.40 10.35 10.30 10.27 10.24 10.24 10.24 10.23 10.22 10.19 10.17 10.14 10.09 10.05 10.01 9.97 9.93 9.90 7.92 7.85 7.80 7.76 7.74 7.66 7.67 7.64 7.59 7.57 7.54 7.48 7.48 7.45 7.41 7.43 7.38 7.35 7.33 7.33 7.32 7.30 7.27 7.25 7.24 7.23 7.25 7.21 7.22 7.17 7.20 7.22 7.20 7.20 9.06 9.05 9.04 9.04 9.04 9.03 9.03 9.02 9.02 9.01 9.01 9.01 9.01 9.00 9.00 9.00 9.00 8.99 8.99 8.99 8.99 8.98 8.98 8.98 8.98 8.97 8.97 8.98 8.97 8.97 8.97 8.97 8.96 8.96 11/9/2013 21:10 11/9/2013 21:20 11/9/2013 21:30 11/9/2013 21:40 11/9/2013 21:50 11/9/2013 22:00 11/9/2013 22:10 11/9/2013 22:20 11/9/2013 22:30 11/9/2013 22:40 11/9/2013 22:50 11/9/2013 23:00 11/9/2013 23:10 11/9/2013 23:20 11/9/2013 23:30 11/9/2013 23:40 11/9/2013 23:50 11/10/2013 0:00 11/10/2013 0:10 11/10/2013 0:20 11/10/2013 0:30 11/10/2013 0:40 11/10/2013 0:50 11/10/2013 1:00 11/10/2013 1:10 11/10/2013 1:20 11/10/2013 1:30 11/10/2013 1:40 11/10/2013 1:50 11/10/2013 2:00 11/10/2013 2:10 11/10/2013 2:20 11/10/2013 2:30 11/10/2013 2:40 10.32 10.31 10.30 10.29 10.28 10.27 10.26 10.24 10.23 10.21 10.20 10.18 10.16 10.14 10.13 10.10 10.09 10.08 10.06 10.04 10.03 10.01 10.00 9.98 9.95 9.94 9.91 9.89 9.87 9.84 9.82 9.79 9.76 9.74 99 9.86 9.83 9.72 9.68 9.63 9.54 9.49 9.48 9.39 9.35 9.38 9.28 9.25 9.22 9.18 9.14 9.09 9.07 9.06 9.01 8.96 8.98 8.92 8.90 8.89 8.88 8.86 8.90 8.83 8.83 8.77 8.85 8.79 8.81 9.14 9.13 9.13 9.12 9.12 9.11 9.11 9.11 9.10 9.10 9.09 9.09 9.09 9.08 9.08 9.08 9.07 9.07 9.07 9.06 9.06 9.06 9.05 9.05 9.05 9.05 9.05 9.04 9.04 9.04 9.04 9.04 9.04 9.04 12/14/2013 23:10 12/14/2013 23:20 12/14/2013 23:30 12/14/2013 23:40 12/14/2013 23:50 12/15/2013 0:00 12/15/2013 0:10 12/15/2013 0:20 12/15/2013 0:30 12/15/2013 0:40 12/15/2013 0:50 12/15/2013 1:00 12/15/2013 1:10 12/15/2013 1:20 12/15/2013 1:30 12/15/2013 1:40 12/15/2013 1:50 12/15/2013 2:00 12/15/2013 2:10 12/15/2013 2:20 12/15/2013 2:30 12/15/2013 2:40 12/15/2013 2:50 12/15/2013 3:00 12/15/2013 3:10 12/15/2013 3:20 12/15/2013 3:30 12/15/2013 3:40 12/15/2013 3:50 12/15/2013 4:00 12/15/2013 4:10 12/15/2013 4:20 12/15/2013 4:30 12/15/2013 4:40 2.28 2.28 2.27 2.26 2.25 2.23 2.22 2.21 2.21 2.20 2.20 2.20 2.20 2.21 2.21 2.22 2.22 2.23 2.23 2.23 2.22 2.21 2.21 2.19 2.18 2.17 2.16 2.15 2.13 2.12 2.10 2.09 2.07 2.05 12.71 12.66 12.66 12.57 12.56 12.53 12.58 12.53 12.48 12.47 12.46 12.43 12.45 12.44 12.41 12.37 12.37 12.37 12.37 12.32 12.35 12.32 12.32 12.29 12.33 12.26 12.26 12.32 12.21 12.33 12.29 12.24 12.30 12.30 9.46 9.46 9.46 9.45 9.45 9.45 9.45 9.44 9.44 9.44 9.44 9.43 9.43 9.43 9.42 9.42 9.42 9.42 9.41 9.41 9.41 9.41 9.41 9.41 9.41 9.41 9.41 9.41 9.40 9.40 9.40 9.40 9.40 9.40 10/23/2013 5:50 10/23/2013 6:00 9.86 9.84 7.19 7.20 8.97 8.96 11/10/2013 2:50 11/10/2013 3:00 9.71 9.68 100 8.81 8.75 9.04 9.04 12/15/2013 4:50 12/15/2013 5:00 2.04 2.02 12.28 12.28 9.40 9.40 Appendix 2. Algae Physiochemical Measurements January 1/25/2013 10:00 1/25/2013 10:10 1/25/2013 10:20 1/25/2013 10:30 1/25/2013 10:40 1/25/2013 10:50 1/25/2013 11:00 1/25/2013 11:10 1/25/2013 11:20 1/25/2013 11:30 1/25/2013 11:40 1/25/2013 11:50 1/25/2013 12:00 1/25/2013 12:10 1/25/2013 12:20 1/25/2013 12:30 1/25/2013 12:40 1/25/2013 12:50 1/25/2013 13:00 1/25/2013 13:10 1/25/2013 13:20 1/25/2013 13:30 1/25/2013 13:40 1/25/2013 13:50 1/25/2013 14:00 1/25/2013 14:10 1/25/2013 14:20 1/25/2013 14:30 1/25/2013 14:40 1/25/2013 14:50 1/25/2013 15:00 DO 5.26 5.42 5.66 5.71 5.74 5.74 5.81 5.78 5.80 5.79 5.80 5.80 5.81 5.83 5.84 5.84 5.85 5.86 5.87 5.89 5.91 5.93 5.95 5.96 5.97 5.98 6.00 6.01 6.02 6.03 6.04 DO 5.86 5.60 5.68 5.74 5.76 5.79 5.81 5.84 5.87 5.90 5.92 5.95 5.98 6.00 6.03 6.12 6.09 6.15 6.16 6.21 6.23 6.26 6.30 6.33 6.31 6.33 6.35 6.34 6.35 6.38 6.36 pH 8.66 8.74 8.69 8.67 8.67 8.66 8.65 8.65 8.64 8.63 8.63 8.62 8.65 8.64 8.65 8.65 8.64 8.64 8.64 8.63 8.62 8.62 8.62 8.61 8.61 8.61 8.61 8.61 8.62 8.61 8.61 February 2/7/2013 21:09 2/7/2013 21:19 2/7/2013 21:29 2/7/2013 21:39 2/7/2013 21:49 2/7/2013 21:59 2/7/2013 22:09 2/7/2013 22:19 2/7/2013 22:29 2/7/2013 22:39 2/7/2013 22:49 2/7/2013 22:59 2/7/2013 23:09 2/7/2013 23:19 2/7/2013 23:29 2/7/2013 23:39 2/7/2013 23:49 2/7/2013 23:59 2/8/2013 0:09 2/8/2013 0:19 2/8/2013 0:29 2/8/2013 0:39 2/8/2013 0:49 2/8/2013 0:59 2/8/2013 1:09 2/8/2013 1:19 2/8/2013 1:29 2/8/2013 1:39 2/8/2013 1:49 2/8/2013 1:59 2/8/2013 2:09 DO 6.62 6.62 6.64 6.63 6.61 6.62 6.63 6.61 6.57 6.53 6.48 6.45 6.42 6.40 6.37 6.39 6.37 6.34 6.31 6.25 6.25 6.25 6.25 6.24 6.23 6.24 6.37 6.34 6.32 6.31 6.29 DO 6.32 6.26 6.21 6.18 6.17 6.15 6.14 6.12 6.11 6.10 6.09 6.08 6.07 6.06 6.05 6.05 6.04 6.03 6.03 6.03 6.02 6.01 6.01 6.00 6.00 5.99 5.98 5.98 5.98 5.98 5.98 101 pH 8.79 8.76 8.67 8.76 8.77 8.73 8.75 8.72 8.71 8.73 8.73 8.75 8.69 8.66 8.64 8.64 8.62 8.67 8.66 8.68 8.71 8.68 8.67 8.70 8.67 8.67 8.68 8.68 8.66 8.65 8.65 March 2/28/2013 20:51 2/28/2013 21:01 2/28/2013 21:11 2/28/2013 21:21 2/28/2013 21:31 2/28/2013 21:41 2/28/2013 21:51 2/28/2013 22:01 2/28/2013 22:11 2/28/2013 22:21 2/28/2013 22:31 2/28/2013 22:41 2/28/2013 22:51 2/28/2013 23:01 2/28/2013 23:11 2/28/2013 23:21 2/28/2013 23:31 2/28/2013 23:41 2/28/2013 23:51 3/1/2013 0:01 3/1/2013 0:11 3/1/2013 0:21 3/1/2013 0:31 3/1/2013 0:41 3/1/2013 0:51 3/1/2013 1:01 3/1/2013 1:11 3/1/2013 1:21 3/1/2013 1:31 3/1/2013 1:41 3/1/2013 1:51 DO 5.20 5.25 5.31 5.35 5.37 5.40 5.47 5.48 5.49 5.50 5.50 5.51 5.52 5.50 5.51 5.52 5.51 5.51 5.52 5.53 5.54 5.55 5.54 5.54 5.55 5.55 5.54 5.53 5.51 5.49 5.48 DO 4.78 4.81 4.85 4.87 4.89 4.90 4.91 4.92 4.92 4.92 4.91 4.92 4.91 4.92 4.91 4.91 4.90 4.91 4.88 4.87 4.86 4.86 4.86 4.86 4.85 4.85 4.84 4.82 4.81 4.81 4.80 pH 8.08 8.10 8.07 8.21 8.09 8.09 8.09 8.09 8.12 8.09 8.10 8.09 8.08 8.10 8.09 8.11 8.08 8.10 8.06 8.13 8.10 8.09 8.07 8.08 8.07 8.07 8.05 8.08 8.04 8.03 8.08 April 4/15/2013 0:04 4/15/2013 0:14 4/15/2013 0:24 4/15/2013 0:34 4/15/2013 0:44 4/15/2013 0:54 4/15/2013 1:04 4/15/2013 1:14 4/15/2013 1:24 4/15/2013 1:34 4/15/2013 1:44 4/15/2013 1:54 4/15/2013 2:04 4/15/2013 2:14 4/15/2013 2:24 4/15/2013 2:34 4/15/2013 2:44 4/15/2013 2:54 4/15/2013 3:04 4/15/2013 3:14 4/15/2013 3:24 4/15/2013 3:34 4/15/2013 3:44 4/15/2013 3:54 4/15/2013 4:04 4/15/2013 4:14 4/15/2013 4:24 4/15/2013 4:34 4/15/2013 4:44 4/15/2013 4:54 4/15/2013 5:04 DO 6.73 6.75 6.73 6.73 6.74 6.75 6.67 6.66 6.66 6.67 6.64 6.65 6.66 6.65 6.64 6.63 6.63 6.63 6.61 6.54 6.55 6.59 6.56 6.57 6.57 6.57 6.57 6.57 6.54 6.56 6.56 1/25/2013 15:10 1/25/2013 15:20 1/25/2013 15:30 1/25/2013 15:40 1/25/2013 15:50 1/25/2013 16:00 1/25/2013 16:10 1/25/2013 16:20 1/25/2013 16:30 1/25/2013 16:40 1/25/2013 16:50 1/25/2013 17:00 1/25/2013 17:10 1/25/2013 17:20 1/25/2013 17:30 1/25/2013 17:40 1/25/2013 17:50 1/25/2013 18:00 1/25/2013 18:10 1/25/2013 18:20 1/25/2013 18:30 1/25/2013 18:40 1/25/2013 18:50 1/25/2013 19:00 1/25/2013 19:10 1/25/2013 19:20 1/25/2013 19:30 1/25/2013 19:40 1/25/2013 19:50 1/25/2013 20:00 1/25/2013 20:10 1/25/2013 20:20 1/25/2013 20:30 1/25/2013 20:40 6.04 6.05 6.04 6.04 6.04 6.04 6.02 6.01 6.00 5.99 5.97 5.96 5.94 5.92 5.91 5.89 5.87 5.85 5.83 5.82 5.79 5.78 5.76 5.75 5.74 5.72 5.70 5.69 5.67 5.66 5.65 5.63 5.61 5.62 6.39 6.33 6.33 6.33 6.33 6.32 6.31 6.31 6.30 6.27 6.26 6.24 6.23 6.20 6.18 6.16 6.15 6.13 6.11 6.09 6.07 6.04 6.03 6.00 5.99 5.98 5.96 5.94 5.93 5.92 5.90 5.88 5.86 5.85 8.61 8.59 8.60 8.61 8.61 8.61 8.61 8.61 8.62 8.62 8.62 8.62 8.61 8.61 8.62 8.62 8.62 8.63 8.62 8.62 8.63 8.63 8.63 8.63 8.62 8.62 8.62 8.62 8.62 8.62 8.62 8.62 8.63 8.63 2/8/2013 2:19 2/8/2013 2:29 2/8/2013 2:39 2/8/2013 2:49 2/8/2013 2:59 2/8/2013 3:09 2/8/2013 3:19 2/8/2013 3:29 2/8/2013 3:39 2/8/2013 3:49 2/8/2013 3:59 2/8/2013 4:09 2/8/2013 4:19 2/8/2013 4:29 2/8/2013 4:39 2/8/2013 4:49 2/8/2013 4:59 2/8/2013 5:09 2/8/2013 5:19 2/8/2013 5:29 2/8/2013 5:39 2/8/2013 5:49 2/8/2013 5:59 2/8/2013 6:09 2/8/2013 6:19 2/8/2013 6:29 2/8/2013 6:39 2/8/2013 6:49 2/8/2013 6:59 2/8/2013 7:09 2/8/2013 7:19 2/8/2013 7:29 2/8/2013 7:39 2/8/2013 7:49 6.27 6.27 6.26 6.34 6.32 6.27 6.25 6.23 6.20 6.22 6.19 6.21 6.22 6.21 6.22 6.21 6.18 6.20 6.15 6.15 6.14 6.12 6.09 6.04 6.03 6.03 5.99 5.93 5.90 5.86 5.83 5.82 5.85 5.81 5.96 5.96 5.95 5.95 5.95 5.94 5.94 5.93 5.92 5.93 5.92 5.92 5.91 5.91 5.90 5.89 5.89 5.88 5.88 5.87 5.86 5.85 5.81 5.79 5.77 5.76 5.74 5.73 5.71 5.70 5.70 5.69 5.70 5.70 102 8.66 8.66 8.65 8.64 8.63 8.58 8.55 8.44 8.55 8.48 8.42 8.53 8.50 8.48 8.45 8.44 8.53 8.48 8.42 8.50 8.47 8.41 8.43 8.42 8.44 8.42 8.42 8.37 8.38 8.42 8.38 8.42 8.40 8.43 3/1/2013 2:01 3/1/2013 2:11 3/1/2013 2:21 3/1/2013 2:31 3/1/2013 2:41 3/1/2013 2:51 3/1/2013 3:01 3/1/2013 3:11 3/1/2013 3:21 3/1/2013 3:31 3/1/2013 3:41 3/1/2013 3:51 3/1/2013 4:01 3/1/2013 4:11 3/1/2013 4:21 3/1/2013 4:31 3/1/2013 4:41 3/1/2013 4:51 3/1/2013 5:01 3/1/2013 5:11 3/1/2013 5:21 3/1/2013 5:31 3/1/2013 5:41 3/1/2013 5:51 3/1/2013 6:01 3/1/2013 6:11 3/1/2013 6:21 3/1/2013 6:31 3/1/2013 6:41 3/1/2013 6:51 3/1/2013 7:01 3/1/2013 7:11 3/1/2013 7:21 3/1/2013 7:31 5.52 5.52 5.51 5.52 5.50 5.49 5.49 5.49 5.48 5.48 5.47 5.48 5.48 5.48 5.48 5.47 5.47 5.47 5.47 5.46 5.46 5.46 5.46 5.45 5.41 5.43 5.42 5.39 5.41 5.35 5.37 5.36 5.35 5.34 4.80 4.81 4.81 4.81 4.81 4.82 4.81 4.81 4.78 4.80 4.80 4.79 4.83 4.74 4.85 4.74 4.78 4.73 4.74 4.80 4.76 4.75 4.82 4.73 4.66 4.81 4.74 4.74 4.73 4.70 4.73 4.73 4.73 4.67 8.09 8.14 8.47 8.37 8.32 8.27 8.22 8.20 8.16 8.11 8.09 8.06 8.03 8.03 8.00 7.98 7.96 7.94 7.92 7.91 7.91 7.90 7.91 7.93 7.92 7.94 7.94 7.99 7.97 7.98 8.01 8.01 8.05 8.02 4/15/2013 5:14 4/15/2013 5:24 4/15/2013 5:34 4/15/2013 5:44 4/15/2013 5:54 4/15/2013 6:04 4/15/2013 6:14 4/15/2013 6:24 4/15/2013 6:34 4/15/2013 6:44 4/15/2013 6:54 4/15/2013 7:04 4/15/2013 7:14 4/15/2013 7:24 4/15/2013 7:34 4/15/2013 7:44 4/15/2013 7:54 4/15/2013 8:04 4/15/2013 8:14 4/15/2013 8:24 4/15/2013 8:34 4/15/2013 8:44 4/15/2013 8:54 4/15/2013 9:04 4/15/2013 9:14 4/15/2013 9:24 4/15/2013 9:34 4/15/2013 9:44 4/15/2013 9:54 4/15/2013 10:04 4/15/2013 10:14 4/15/2013 10:24 4/15/2013 10:34 4/15/2013 10:44 6.55 6.53 6.55 6.54 6.54 6.52 6.55 6.55 6.52 6.51 6.56 6.56 6.57 6.57 6.59 6.64 6.67 6.69 6.73 6.76 6.80 6.83 6.88 6.94 6.97 7.01 7.06 7.11 7.18 7.25 7.32 7.39 7.52 7.62 1/25/2013 20:50 1/25/2013 21:00 1/25/2013 21:10 1/25/2013 21:20 1/25/2013 21:30 1/25/2013 21:40 1/25/2013 21:50 1/25/2013 22:00 1/25/2013 22:10 1/25/2013 22:20 1/25/2013 22:30 1/25/2013 22:40 1/25/2013 22:50 1/25/2013 23:00 1/25/2013 23:10 1/25/2013 23:20 1/25/2013 23:30 1/25/2013 23:40 1/25/2013 23:50 1/26/2013 0:00 1/26/2013 0:10 1/26/2013 0:20 1/26/2013 0:30 1/26/2013 0:40 1/26/2013 0:50 1/26/2013 1:00 1/26/2013 1:10 1/26/2013 1:20 1/26/2013 1:30 1/26/2013 1:40 1/26/2013 1:50 1/26/2013 2:00 1/26/2013 2:10 1/26/2013 2:20 5.60 5.60 5.59 5.60 5.60 5.59 5.58 5.59 5.58 5.59 5.59 5.58 5.58 5.57 5.57 5.57 5.56 5.56 5.55 5.55 5.55 5.53 5.56 5.53 5.53 5.51 5.52 5.51 5.50 5.51 5.50 5.49 5.49 5.48 5.84 5.83 5.82 5.82 5.82 5.81 5.80 5.80 5.79 5.79 5.78 5.78 5.77 5.77 5.77 5.76 5.76 5.76 5.75 5.75 5.74 5.73 5.73 5.72 5.72 5.71 5.70 5.69 5.69 5.69 5.69 5.69 5.69 5.68 8.63 8.62 8.62 8.61 8.61 8.61 8.60 8.61 8.60 8.60 8.60 8.60 8.60 8.60 8.60 8.60 8.59 8.60 8.60 8.60 8.60 8.60 8.59 8.59 8.59 8.59 8.59 8.59 8.59 8.60 8.59 8.60 8.60 8.60 2/8/2013 7:59 2/8/2013 8:09 2/8/2013 8:19 2/8/2013 8:29 2/8/2013 8:39 2/8/2013 8:49 2/8/2013 8:59 2/8/2013 9:09 2/8/2013 9:19 2/8/2013 9:29 2/8/2013 9:39 2/8/2013 9:49 2/8/2013 9:59 2/8/2013 10:09 2/8/2013 10:19 2/8/2013 10:29 2/8/2013 10:39 2/8/2013 10:49 2/8/2013 10:59 2/8/2013 11:09 2/8/2013 11:19 2/8/2013 11:29 2/8/2013 11:39 2/8/2013 11:49 2/8/2013 11:59 2/8/2013 12:09 2/8/2013 12:19 2/8/2013 12:29 2/8/2013 12:39 2/8/2013 12:49 2/8/2013 12:59 2/8/2013 13:09 2/8/2013 13:19 2/8/2013 13:29 5.81 5.81 5.81 5.78 5.76 5.90 5.94 5.94 5.84 5.79 5.80 5.74 5.78 5.84 5.76 5.86 5.87 5.89 5.91 5.85 5.99 6.03 6.03 6.02 5.97 5.94 6.11 6.13 6.13 6.15 6.15 6.16 6.21 6.37 5.69 5.70 5.69 5.70 5.70 5.71 5.71 5.72 5.72 5.72 5.72 5.72 5.73 5.75 5.76 5.77 5.78 5.79 5.82 5.84 5.86 5.88 5.90 5.92 5.93 5.94 5.96 5.97 5.99 6.00 6.01 6.02 6.04 6.06 103 8.43 8.40 8.41 8.43 8.42 8.39 8.38 8.44 8.39 8.39 8.38 8.37 8.38 8.38 8.38 8.43 8.39 8.38 8.39 8.37 8.40 8.38 8.39 8.38 8.51 8.44 8.49 8.48 8.52 8.63 8.56 8.56 8.50 8.58 3/1/2013 7:41 5.37 4.78 3/1/2013 7:51 5.36 4.83 3/1/2013 8:01 5.41 4.80 3/1/2013 8:11 5.40 4.82 3/1/2013 8:21 5.40 4.85 3/1/2013 8:31 5.46 4.86 3/1/2013 8:41 5.52 4.92 3/1/2013 8:51 5.55 4.83 3/1/2013 9:01 5.54 4.81 3/1/2013 9:11 5.51 4.83 3/1/2013 9:21 5.60 4.92 3/1/2013 9:31 6.05 4.71 3/1/2013 9:41 8.43 5.14 3/1/2013 9:51 8.23 5.05 3/1/2013 10:01 8.91 5.12 3/1/2013 10:11 8.35 5.13 3/1/2013 10:21 9.01 5.17 3/1/2013 10:31 8.28 5.11 3/1/2013 10:41 7.87 5.07 3/1/2013 10:51 7.99 5.10 3/1/2013 11:01 8.63 5.14 3/1/2013 11:11 8.61 5.15 3/1/2013 11:21 9.52 5.20 3/1/2013 11:31 8.60 5.11 3/1/2013 11:41 8.47 5.11 3/1/2013 11:51 9.02 5.13 3/1/2013 12:01 8.79 5.15 3/1/2013 12:11 9.23 5.13 3/1/2013 12:21 9.38 5.16 3/1/2013 12:31 9.12 5.14 3/1/2013 12:41 8.87 5.22 3/1/2013 12:51 10.14 5.16 3/1/2013 13:01 9.91 5.20 3/1/2013 13:11 9.42 5.33 8.04 8.05 8.07 8.06 8.08 8.06 8.05 8.06 8.07 8.05 8.06 8.06 8.04 8.02 8.01 8.02 7.98 8.00 7.96 4/15/2013 10:54 4/15/2013 11:04 4/15/2013 11:14 4/15/2013 11:24 4/15/2013 11:34 4/15/2013 11:44 4/15/2013 11:54 4/15/2013 12:04 4/15/2013 12:14 4/15/2013 12:24 4/15/2013 12:34 4/15/2013 12:44 4/15/2013 12:54 4/15/2013 13:04 4/15/2013 13:14 4/15/2013 13:24 4/15/2013 13:34 4/15/2013 13:44 4/15/2013 13:54 4/15/2013 14:04 4/15/2013 14:14 4/15/2013 14:24 4/15/2013 14:34 4/15/2013 14:44 4/15/2013 14:54 4/15/2013 15:04 4/15/2013 15:14 4/15/2013 15:24 4/15/2013 15:34 4/15/2013 15:44 4/15/2013 15:54 4/15/2013 16:04 4/15/2013 16:14 4/15/2013 16:24 7.70 7.79 7.90 8.07 8.26 8.39 8.41 8.45 8.49 8.54 8.53 8.51 8.61 8.69 8.67 8.66 8.71 8.80 8.79 8.80 8.85 8.87 8.88 8.89 8.97 9.11 9.17 9.10 9.14 9.24 9.27 9.21 9.24 9.26 1/26/2013 2:30 1/26/2013 2:40 1/26/2013 2:50 1/26/2013 3:00 1/26/2013 3:10 1/26/2013 3:20 1/26/2013 3:30 1/26/2013 3:40 1/26/2013 3:50 1/26/2013 4:00 1/26/2013 4:10 1/26/2013 4:20 1/26/2013 4:30 1/26/2013 4:40 1/26/2013 4:50 1/26/2013 5:00 1/26/2013 5:10 1/26/2013 5:20 1/26/2013 5:30 1/26/2013 5:40 1/26/2013 5:50 1/26/2013 6:00 1/26/2013 6:10 1/26/2013 6:20 1/26/2013 6:38 1/26/2013 6:48 1/26/2013 6:58 1/26/2013 7:08 1/26/2013 7:18 1/26/2013 7:28 1/26/2013 7:38 1/26/2013 7:48 1/26/2013 7:58 1/26/2013 8:08 5.48 5.48 5.48 5.46 5.47 5.46 5.46 5.46 5.45 5.45 5.45 5.44 5.44 5.42 5.42 5.41 5.40 5.40 5.39 5.39 5.40 5.39 5.39 5.39 5.38 5.40 5.42 5.42 5.42 5.43 5.43 5.43 5.43 5.44 5.68 5.67 5.67 5.66 5.65 5.65 5.65 5.64 5.64 5.63 5.63 5.63 5.62 5.61 5.61 5.60 5.60 5.59 5.59 5.59 5.59 5.59 5.60 5.59 5.60 5.60 5.60 5.60 5.60 5.60 5.60 5.61 5.61 5.61 8.60 8.60 8.60 8.60 8.60 8.60 8.59 8.60 8.60 8.60 8.60 8.60 8.60 8.60 8.60 8.61 8.60 8.61 8.61 8.60 8.60 8.60 8.59 8.59 8.58 8.59 8.59 8.58 8.59 8.59 8.58 8.59 8.60 8.59 2/8/2013 13:39 2/8/2013 13:49 2/8/2013 13:59 2/8/2013 14:09 2/8/2013 14:19 2/8/2013 14:29 2/8/2013 14:39 2/8/2013 14:49 2/8/2013 14:59 2/8/2013 15:09 2/8/2013 15:19 2/8/2013 15:29 2/8/2013 15:39 2/8/2013 15:49 2/8/2013 15:59 2/8/2013 16:09 2/8/2013 16:19 2/8/2013 16:29 2/8/2013 16:39 2/8/2013 16:49 2/8/2013 16:59 2/8/2013 17:09 2/8/2013 17:19 2/8/2013 17:29 2/8/2013 17:39 2/8/2013 17:49 2/8/2013 17:59 2/8/2013 18:09 2/8/2013 18:19 2/8/2013 18:29 2/8/2013 18:39 2/8/2013 18:49 2/8/2013 18:59 2/8/2013 19:09 6.41 6.44 6.46 6.47 6.47 6.48 6.48 6.48 6.48 6.48 6.48 6.49 6.48 6.46 6.45 6.43 6.41 6.40 6.37 6.35 6.34 6.32 6.30 6.28 6.26 6.26 6.24 6.22 6.20 6.17 6.14 6.57 6.54 6.51 6.09 6.10 6.12 6.14 6.15 6.16 6.17 6.17 6.19 6.20 6.21 6.21 6.20 6.20 6.20 6.19 6.18 6.18 6.17 6.14 6.13 6.13 6.11 6.09 6.06 6.04 6.00 5.99 5.97 5.95 5.93 5.91 5.89 5.87 104 8.52 8.55 8.52 8.55 8.51 8.51 8.53 8.54 8.48 8.48 8.49 8.40 8.57 8.58 8.63 8.59 8.66 8.68 8.56 8.59 8.62 8.55 8.56 8.50 8.53 8.45 8.46 8.41 8.59 8.60 8.61 8.60 8.60 8.60 3/1/2013 13:21 3/1/2013 13:31 3/1/2013 13:41 3/1/2013 13:51 3/1/2013 14:01 3/1/2013 14:11 3/1/2013 14:21 3/1/2013 14:31 3/1/2013 14:41 3/1/2013 14:51 3/1/2013 15:01 3/1/2013 15:11 3/1/2013 15:21 3/1/2013 15:31 3/1/2013 15:41 3/1/2013 15:51 3/1/2013 16:01 3/1/2013 16:11 3/1/2013 16:21 3/1/2013 16:31 3/1/2013 16:41 3/1/2013 16:51 3/1/2013 17:01 3/1/2013 17:11 3/1/2013 17:21 3/1/2013 17:31 3/1/2013 17:41 3/1/2013 17:51 3/1/2013 18:01 3/1/2013 18:11 3/1/2013 18:21 3/1/2013 18:31 3/1/2013 18:41 3/1/2013 18:51 8.81 8.94 8.40 8.71 9.05 8.38 8.22 8.34 8.50 8.01 8.25 7.95 7.38 8.82 8.05 8.71 8.40 8.16 9.13 7.94 8.18 7.84 7.72 7.68 7.65 7.54 7.44 7.35 7.22 7.19 7.14 7.05 7.01 6.98 5.38 5.23 5.47 5.93 5.77 6.82 5.71 5.85 7.12 5.70 7.32 6.54 4.94 5.22 5.19 5.21 5.20 5.20 5.23 5.19 5.19 5.18 5.18 5.18 5.16 5.17 5.15 5.15 5.14 5.14 5.13 5.11 5.10 5.10 4/15/2013 16:34 4/15/2013 16:44 4/15/2013 16:54 4/15/2013 17:04 4/15/2013 17:14 4/15/2013 17:24 4/15/2013 17:34 4/15/2013 17:44 4/15/2013 17:54 4/15/2013 18:04 4/15/2013 18:14 4/15/2013 18:24 4/15/2013 18:34 4/15/2013 18:44 4/15/2013 18:54 4/15/2013 19:04 4/15/2013 19:14 4/15/2013 19:24 4/15/2013 19:34 4/15/2013 19:44 4/15/2013 19:54 4/15/2013 20:04 4/15/2013 20:14 4/15/2013 20:24 4/15/2013 20:34 4/15/2013 20:44 4/15/2013 20:54 4/15/2013 21:04 4/15/2013 21:14 4/15/2013 21:24 4/15/2013 21:34 4/15/2013 21:44 4/15/2013 21:54 4/15/2013 22:04 9.20 9.14 9.18 9.23 9.15 9.14 9.14 9.10 9.04 8.99 8.94 8.88 8.81 8.74 8.67 8.61 8.53 8.46 8.39 8.33 8.27 8.19 8.13 8.07 8.01 7.95 7.90 7.85 7.80 7.76 7.71 7.67 7.63 7.59 1/26/2013 8:18 1/26/2013 8:28 1/26/2013 8:38 1/26/2013 8:48 1/26/2013 8:58 1/26/2013 9:08 5.44 5.45 5.46 5.47 5.48 5.50 5.61 5.62 5.62 5.63 5.64 5.65 8.60 8.60 8.60 8.60 8.61 8.60 2/8/2013 19:19 2/8/2013 19:29 2/8/2013 19:39 2/8/2013 19:49 2/8/2013 19:59 2/8/2013 20:09 2/8/2013 20:19 2/8/2013 20:29 2/8/2013 20:39 2/8/2013 20:49 2/8/2013 20:59 2/8/2013 21:09 2/8/2013 21:19 2/8/2013 21:29 2/8/2013 21:39 2/8/2013 21:49 2/8/2013 21:59 2/8/2013 22:09 2/8/2013 22:19 2/8/2013 22:29 2/8/2013 22:39 2/8/2013 22:49 2/8/2013 22:59 2/8/2013 23:09 2/8/2013 23:19 2/8/2013 23:29 2/8/2013 23:39 2/8/2013 23:49 2/8/2013 23:59 2/9/2013 0:09 2/9/2013 0:19 2/9/2013 0:29 2/9/2013 0:39 2/9/2013 0:49 6.50 6.48 6.47 6.46 6.44 6.43 6.41 6.41 6.39 6.39 6.39 6.38 6.37 6.37 6.35 6.35 6.34 6.33 6.33 6.32 6.32 6.31 6.31 6.30 6.30 6.29 6.29 6.28 6.28 6.27 6.26 6.26 6.25 6.25 5.86 5.85 5.84 5.82 5.79 5.78 5.78 5.76 5.75 5.75 5.74 5.74 5.73 5.72 5.71 5.71 5.70 5.69 5.68 5.67 5.67 5.66 5.65 5.65 5.64 5.64 5.63 5.63 5.62 5.61 5.61 5.60 5.60 5.59 105 8.59 8.69 8.66 8.67 8.66 8.58 8.74 8.73 8.70 8.68 8.66 8.63 8.64 8.64 8.64 8.64 8.65 8.63 8.62 8.65 8.64 8.64 8.64 8.65 8.61 8.56 8.57 8.59 8.60 8.64 8.63 8.62 8.61 8.60 3/1/2013 19:01 6.89 5.12 3/1/2013 19:11 6.90 5.09 3/1/2013 19:21 6.89 5.08 3/1/2013 19:31 6.90 5.07 3/1/2013 19:41 6.89 4.70 3/1/2013 19:51 6.92 5.07 3/1/2013 20:01 6.91 4.71 3/1/2013 20:11 6.88 4.44 3/1/2013 20:21 6.91 4.73 3/1/2013 20:31 6.90 4.66 3/1/2013 20:41 6.91 4.57 3/1/2013 20:51 6.99 4.79 3/1/2013 21:01 6.99 4.84 3/1/2013 21:11 7.07 4.73 3/1/2013 21:21 7.01 4.55 3/1/2013 21:31 7.06 4.50 3/1/2013 21:41 7.00 4.54 3/1/2013 21:51 6.96 4.64 3/1/2013 22:01 6.97 4.72 3/1/2013 22:11 6.99 4.76 3/1/2013 22:21 6.99 4.74 3/1/2013 22:31 7.01 4.75 3/1/2013 22:41 7.02 4.72 3/1/2013 22:51 7.03 4.74 3/1/2013 23:01 7.06 4.74 3/1/2013 23:11 7.08 4.79 3/1/2013 23:21 7.02 4.69 3/1/2013 23:31 7.06 4.85 3/1/2013 23:41 7.09 4.84 3/1/2013 23:51 7.06 4.74 3/2/2013 0:01 7.08 4.84 3/2/2013 0:11 16.46 7.90 3/2/2013 0:21 10.19 4.69 3/2/2013 0:31 9.97 5.41 4/15/2013 22:14 4/15/2013 22:24 4/15/2013 22:34 4/15/2013 22:44 4/15/2013 22:54 4/15/2013 23:04 4/15/2013 23:14 4/15/2013 23:24 4/15/2013 23:34 4/15/2013 23:44 4/15/2013 23:54 4/16/2013 0:04 4/16/2013 0:14 4/16/2013 0:24 4/16/2013 0:34 4/16/2013 0:44 4/16/2013 0:54 4/16/2013 1:04 4/16/2013 1:14 4/16/2013 1:24 4/16/2013 1:34 4/16/2013 1:44 4/16/2013 1:54 4/16/2013 2:04 4/16/2013 2:14 4/16/2013 2:24 4/16/2013 2:34 4/16/2013 2:44 4/16/2013 2:54 4/16/2013 3:04 4/16/2013 3:14 4/16/2013 3:24 4/16/2013 3:34 4/16/2013 3:44 7.55 7.52 7.49 7.45 7.42 7.39 7.35 7.33 7.30 7.26 7.24 7.22 7.20 7.18 7.16 7.14 7.12 7.11 7.09 7.07 7.06 7.04 7.03 7.01 7.00 6.99 6.98 6.96 6.94 6.93 6.92 6.91 6.89 6.87 2/9/2013 0:59 2/9/2013 1:09 2/9/2013 1:19 2/9/2013 1:29 2/9/2013 1:39 2/9/2013 1:49 2/9/2013 1:59 2/9/2013 2:09 2/9/2013 2:19 2/9/2013 2:29 2/9/2013 2:39 2/9/2013 2:49 2/9/2013 2:59 2/9/2013 3:09 2/9/2013 3:19 2/9/2013 3:29 2/9/2013 3:39 2/9/2013 3:49 2/9/2013 3:59 2/9/2013 4:09 2/9/2013 4:19 2/9/2013 4:29 2/9/2013 4:39 2/9/2013 4:49 2/9/2013 4:59 2/9/2013 5:09 2/9/2013 5:19 2/9/2013 5:29 2/9/2013 5:39 2/9/2013 5:49 2/9/2013 5:59 2/9/2013 6:09 6.24 6.24 6.23 6.22 6.22 6.21 6.21 6.20 6.20 6.19 6.19 6.17 6.17 6.16 6.16 6.15 6.17 6.17 6.17 6.16 6.16 6.14 6.15 6.14 6.14 6.14 6.13 6.13 6.13 6.12 6.12 6.11 5.59 5.58 5.57 5.57 5.57 5.56 5.56 5.55 5.54 5.53 5.52 5.52 5.51 5.51 5.51 5.51 5.51 5.51 5.51 5.50 5.50 5.49 5.49 5.49 5.48 5.48 5.47 5.48 5.47 5.46 5.46 5.45 106 8.63 8.63 8.62 8.60 8.60 8.59 8.56 8.52 8.55 8.54 8.54 8.55 8.53 8.53 8.30 8.53 8.53 8.53 8.55 8.54 8.55 8.55 8.54 8.55 8.55 8.55 8.56 8.54 8.54 8.53 8.54 8.54 3/2/2013 0:41 3/2/2013 0:51 3/2/2013 1:01 3/2/2013 1:11 3/2/2013 1:21 3/2/2013 1:31 3/2/2013 1:41 3/2/2013 1:51 3/2/2013 2:01 3/2/2013 2:11 3/2/2013 2:21 3/2/2013 2:31 3/2/2013 2:41 3/2/2013 2:51 3/2/2013 3:01 3/2/2013 3:11 3/2/2013 3:21 3/2/2013 3:31 3/2/2013 3:41 3/2/2013 3:51 3/2/2013 4:01 3/2/2013 4:11 3/2/2013 4:21 3/2/2013 4:31 3/2/2013 4:41 3/2/2013 4:51 3/2/2013 5:01 3/2/2013 5:11 3/2/2013 5:21 3/2/2013 5:31 3/2/2013 5:41 3/2/2013 5:51 9.61 9.40 9.26 9.05 9.00 8.87 8.77 8.72 8.66 8.60 8.58 8.50 8.46 8.40 8.38 8.36 8.35 8.29 8.23 8.23 8.20 8.19 8.21 8.13 8.07 7.97 8.01 7.93 7.82 7.81 8.08 8.02 5.40 5.38 5.38 5.37 5.36 5.35 5.34 5.34 5.33 5.32 5.31 5.31 5.31 5.31 5.31 5.31 5.31 5.31 5.30 5.30 5.30 5.29 5.29 5.28 5.28 5.28 5.27 5.26 5.27 5.27 5.26 5.26 4/16/2013 3:54 4/16/2013 4:04 4/16/2013 4:14 4/16/2013 4:24 4/16/2013 4:34 4/16/2013 4:44 4/16/2013 4:54 4/16/2013 5:04 4/16/2013 5:14 4/16/2013 5:24 4/16/2013 5:34 4/16/2013 5:44 4/16/2013 5:54 4/16/2013 6:04 4/16/2013 6:14 4/16/2013 6:24 4/16/2013 6:34 4/16/2013 6:44 4/16/2013 6:54 4/16/2013 7:04 4/16/2013 7:14 4/16/2013 7:24 4/16/2013 7:34 4/16/2013 7:44 4/16/2013 7:54 4/16/2013 8:04 4/16/2013 8:14 4/16/2013 8:24 4/16/2013 8:34 4/16/2013 8:44 4/16/2013 8:54 4/16/2013 9:04 6.86 6.85 6.84 6.83 6.82 6.81 6.80 6.79 6.78 6.78 6.77 6.76 6.75 6.75 6.74 6.74 6.74 6.75 6.76 6.78 6.81 6.83 6.81 6.82 6.84 6.86 6.88 6.92 7.01 7.09 7.15 7.20 Appendix 2. (continued) May 5/30/2013 6:29 5/30/2013 6:39 5/30/2013 6:49 5/30/2013 6:59 5/30/2013 7:09 5/30/2013 7:19 5/30/2013 7:29 5/30/2013 7:39 5/30/2013 7:49 5/30/2013 7:59 5/30/2013 8:09 5/30/2013 8:19 5/30/2013 8:29 5/30/2013 8:39 5/30/2013 8:49 5/30/2013 8:59 5/30/2013 9:09 5/30/2013 9:19 5/30/2013 9:29 5/30/2013 9:39 5/30/2013 9:49 5/30/2013 9:59 5/30/2013 10:09 5/30/2013 10:19 5/30/2013 10:29 5/30/2013 10:39 5/30/2013 10:49 5/30/2013 10:59 5/30/2013 11:09 5/30/2013 11:19 5/30/2013 11:29 5/30/2013 11:39 DO 5.95 5.24 5.06 4.94 4.84 4.80 4.73 4.64 4.64 4.66 4.69 4.69 4.69 4.81 4.84 4.88 4.89 4.94 5.00 5.05 5.11 5.24 5.28 5.38 5.46 5.55 5.63 5.85 5.92 6.06 6.05 6.26 DO 6.09 6.02 5.97 5.93 5.90 5.90 5.86 5.83 5.81 5.81 5.81 5.78 5.73 5.80 5.81 5.83 5.85 5.79 5.81 5.70 5.81 5.82 5.81 5.80 5.78 5.74 5.73 5.64 6.06 6.16 6.18 6.20 pH 7.67 7.66 7.66 7.66 7.66 7.66 7.66 7.65 7.65 7.65 7.65 7.66 7.66 7.66 7.66 7.67 7.67 7.68 7.68 7.68 7.69 7.69 7.70 7.70 7.71 7.72 7.72 7.73 7.73 7.74 7.74 7.76 June 6/17/2013 17:20 6/17/2013 17:30 6/17/2013 17:40 6/17/2013 17:50 6/17/2013 18:00 6/17/2013 18:10 6/17/2013 18:20 6/17/2013 18:30 6/17/2013 18:40 6/17/2013 18:50 6/17/2013 19:00 6/17/2013 19:10 6/17/2013 19:20 6/17/2013 19:30 6/17/2013 19:40 6/17/2013 19:50 6/17/2013 20:00 6/17/2013 20:10 6/17/2013 20:20 6/17/2013 20:30 6/17/2013 20:40 6/17/2013 20:50 6/17/2013 21:00 6/17/2013 21:10 6/17/2013 21:20 6/17/2013 21:30 6/17/2013 21:40 6/17/2013 21:50 6/17/2013 22:00 6/17/2013 22:10 6/17/2013 22:20 6/17/2013 22:30 DO 8.70 8.28 8.33 8.28 8.24 8.11 8.00 8.01 7.92 7.96 7.62 7.79 7.70 7.63 7.49 7.27 7.37 7.16 7.37 7.28 7.22 7.26 7.16 7.07 7.12 7.07 7.05 7.08 7.06 7.07 6.74 6.88 107 DO 6.86 6.73 6.95 7.06 7.34 7.77 7.76 7.43 7.38 7.27 7.02 7.32 7.31 7.42 7.41 7.23 7.02 6.83 7.01 6.90 6.93 7.04 6.98 6.75 6.92 7.06 6.60 6.92 6.76 6.73 6.49 6.69 pH 8.25 8.24 8.24 8.24 8.24 8.24 8.24 8.24 8.24 8.23 8.23 8.23 8.22 8.22 8.22 8.22 8.22 8.21 8.21 8.20 8.19 8.19 8.18 8.18 8.17 8.17 8.17 8.17 8.16 8.14 8.13 8.13 July 7/29/2013 12:03 7/29/2013 12:13 7/29/2013 12:23 7/29/2013 12:33 7/29/2013 12:43 7/29/2013 12:53 7/29/2013 13:03 7/29/2013 13:13 7/29/2013 13:23 7/29/2013 13:33 7/29/2013 13:43 7/29/2013 13:53 7/29/2013 14:03 7/29/2013 14:13 7/29/2013 14:23 7/29/2013 14:33 7/29/2013 14:43 7/29/2013 14:53 7/29/2013 15:03 7/29/2013 15:13 7/29/2013 15:23 7/29/2013 15:33 7/29/2013 15:43 7/29/2013 15:53 7/29/2013 16:03 7/29/2013 16:13 7/29/2013 16:23 7/29/2013 16:33 7/29/2013 16:43 7/29/2013 16:53 7/29/2013 17:03 7/29/2013 17:13 DO 10.66 10.54 10.41 10.31 10.66 11.55 11.65 11.84 11.98 12.03 12.41 12.51 12.45 12.48 11.86 12.61 12.11 12.06 12.11 11.87 12.19 12.52 12.57 13.28 13.27 13.14 11.63 11.51 12.12 11.88 11.90 11.55 DO 15.46 16.10 15.75 15.61 15.72 16.19 16.31 16.62 3.85 2.35 2.20 2.54 2.31 2.57 2.51 2.84 3.04 3.44 3.53 3.48 3.39 3.54 3.54 3.82 3.01 4.18 3.90 4.14 4.33 4.27 4.32 5.27 pH 8.18 8.19 8.24 8.21 8.20 8.23 8.21 8.25 8.31 8.31 8.30 8.28 8.30 8.28 8.28 8.28 8.28 8.22 8.23 8.27 8.22 8.30 8.27 8.30 8.24 8.26 8.21 8.16 8.19 8.23 8.23 8.23 5/30/2013 11:49 5/30/2013 11:59 5/30/2013 12:09 5/30/2013 12:19 5/30/2013 12:29 5/30/2013 12:39 5/30/2013 12:49 5/30/2013 12:59 5/30/2013 13:09 5/30/2013 13:19 5/30/2013 13:29 5/30/2013 13:39 5/30/2013 13:49 5/30/2013 13:59 5/30/2013 14:09 5/30/2013 14:19 5/30/2013 14:29 5/30/2013 14:39 5/30/2013 14:49 5/30/2013 14:59 5/30/2013 15:09 5/30/2013 15:19 5/30/2013 15:29 5/30/2013 15:39 5/30/2013 15:49 5/30/2013 15:59 5/30/2013 16:09 5/30/2013 16:19 5/30/2013 16:29 5/30/2013 16:39 5/30/2013 16:49 5/30/2013 16:59 5/30/2013 17:09 5/30/2013 17:19 6.41 6.49 6.66 6.76 6.89 6.93 7.08 7.19 7.41 7.44 7.73 7.76 7.71 7.83 7.71 7.97 8.11 8.11 8.09 8.19 8.15 8.29 8.43 8.46 8.52 8.34 8.41 8.32 8.20 8.17 8.18 8.18 8.25 8.16 6.21 6.21 6.24 6.24 6.26 6.26 6.26 6.26 6.29 6.27 6.32 6.31 6.28 6.30 6.31 6.34 6.34 6.36 6.34 6.37 6.38 6.39 6.38 6.42 6.43 6.43 6.41 6.44 6.41 6.41 6.41 6.40 6.42 6.42 7.76 7.77 7.78 7.78 7.79 7.80 7.80 7.80 7.82 7.82 7.82 7.83 7.83 7.84 7.83 7.84 7.86 7.87 7.86 7.86 7.87 7.87 7.87 7.88 7.89 7.87 7.87 7.88 7.88 7.87 7.87 7.87 7.87 7.87 6/17/2013 22:40 6/17/2013 22:50 6/17/2013 23:00 6/17/2013 23:10 6/17/2013 23:20 6/17/2013 23:30 6/17/2013 23:40 6/17/2013 23:50 6/18/2013 0:00 6/18/2013 0:10 6/18/2013 0:20 6/18/2013 0:30 6/18/2013 0:40 6/18/2013 0:50 6/18/2013 1:00 6/18/2013 1:10 6/18/2013 1:20 6/18/2013 1:30 6/18/2013 1:40 6/18/2013 1:50 6/18/2013 2:00 6/18/2013 2:10 6/18/2013 2:20 6/18/2013 2:30 6/18/2013 2:40 6/18/2013 2:50 6/18/2013 3:00 6/18/2013 3:10 6/18/2013 3:20 6/18/2013 3:30 6/18/2013 3:40 6/18/2013 3:50 6/18/2013 4:00 6/18/2013 4:10 6.98 7.10 6.75 6.97 6.91 6.94 6.98 6.90 6.92 6.73 6.94 6.89 6.91 6.72 6.71 6.84 6.70 6.72 6.68 6.65 6.52 6.65 6.77 6.77 6.57 6.53 6.65 6.63 6.64 6.52 6.70 6.64 6.54 6.51 108 6.81 6.93 6.90 6.82 6.73 6.96 6.84 6.99 6.85 6.71 6.80 6.75 6.74 6.63 6.73 6.70 6.59 6.61 6.90 6.78 6.77 6.74 6.91 6.87 6.78 6.81 6.87 6.79 6.70 6.64 6.87 6.93 6.73 6.71 8.13 8.15 8.14 8.14 8.14 8.14 8.14 8.14 8.13 8.12 8.13 8.12 8.12 8.12 8.12 8.12 8.11 8.11 8.11 8.11 8.11 8.10 8.10 8.10 8.10 8.10 8.11 8.10 8.10 8.10 8.10 8.10 8.10 8.09 7/29/2013 17:23 7/29/2013 17:33 7/29/2013 17:43 7/29/2013 17:53 7/29/2013 18:03 7/29/2013 18:13 7/29/2013 18:23 7/29/2013 18:33 7/29/2013 18:43 7/29/2013 18:53 7/29/2013 19:03 7/29/2013 19:13 7/29/2013 19:23 7/29/2013 19:33 7/29/2013 19:43 7/29/2013 19:53 7/29/2013 20:03 7/29/2013 20:13 7/29/2013 20:23 7/29/2013 20:33 7/29/2013 20:43 7/29/2013 20:53 7/29/2013 21:03 7/29/2013 21:13 7/29/2013 21:23 7/29/2013 21:33 7/29/2013 21:43 7/29/2013 21:53 7/29/2013 22:03 7/29/2013 22:13 7/29/2013 22:23 7/29/2013 22:33 7/29/2013 22:43 7/29/2013 22:53 11.92 9.43 11.42 11.21 11.11 10.83 10.86 10.66 10.69 10.35 10.18 10.09 9.90 9.67 9.51 9.34 9.17 9.02 8.86 8.73 8.60 8.47 8.29 8.14 7.95 7.73 7.61 7.50 7.49 7.36 7.26 7.01 6.94 6.82 5.34 5.23 5.24 5.16 5.15 5.05 5.02 5.00 5.03 4.86 4.81 4.87 4.70 4.53 4.52 4.41 4.46 4.40 4.35 4.33 4.25 4.13 4.09 3.97 3.86 3.82 3.75 3.70 3.66 3.67 3.66 3.58 3.54 3.65 8.23 8.24 8.24 8.25 8.20 8.21 8.21 8.21 8.23 8.21 8.21 8.19 8.18 8.18 8.18 8.17 8.16 8.13 8.12 8.12 8.12 8.11 8.09 8.08 8.08 8.07 8.06 8.05 8.06 8.05 8.04 8.02 8.02 8.01 5/30/2013 17:29 5/30/2013 17:39 5/30/2013 17:49 5/30/2013 17:59 5/30/2013 18:09 5/30/2013 18:19 5/30/2013 18:29 5/30/2013 18:39 5/30/2013 18:49 5/30/2013 18:59 5/30/2013 19:09 5/30/2013 19:19 5/30/2013 19:29 5/30/2013 19:39 5/30/2013 19:49 5/30/2013 19:59 5/30/2013 20:09 5/30/2013 20:19 5/30/2013 20:29 5/30/2013 20:39 5/30/2013 20:49 5/30/2013 20:59 5/30/2013 21:09 5/30/2013 21:19 5/30/2013 21:29 5/30/2013 21:39 5/30/2013 21:49 5/30/2013 21:59 5/30/2013 22:09 5/30/2013 22:19 5/30/2013 22:29 5/30/2013 22:39 5/30/2013 22:49 5/30/2013 22:59 8.05 8.01 7.87 7.99 7.67 7.56 7.36 7.34 7.33 7.37 7.34 7.19 7.01 6.91 6.81 6.66 6.64 6.65 6.52 6.43 6.34 6.19 6.09 6.05 5.92 5.91 5.84 5.79 5.63 5.63 5.59 5.47 5.41 5.37 6.40 6.41 6.39 6.40 6.36 6.36 6.33 6.32 6.33 6.32 6.32 6.31 6.23 6.27 6.24 6.22 6.21 6.20 6.19 6.17 6.16 6.13 6.13 6.11 6.09 6.10 6.10 6.07 6.07 6.07 6.06 6.03 6.04 6.03 7.87 7.87 7.86 7.86 7.87 7.86 7.86 7.86 7.85 7.85 7.85 7.84 7.83 7.82 7.81 7.80 7.80 7.80 7.79 7.79 7.78 7.77 7.77 7.77 7.76 7.76 7.76 7.75 7.75 7.74 7.73 7.73 7.72 7.72 6/18/2013 4:20 6/18/2013 4:30 6/18/2013 4:40 6/18/2013 4:50 6/18/2013 5:00 6/18/2013 5:10 6/18/2013 5:20 6/18/2013 5:30 6/18/2013 5:40 6/18/2013 5:50 6/18/2013 6:00 6/18/2013 6:10 6/18/2013 6:20 6/18/2013 6:30 6/18/2013 6:40 6/18/2013 6:50 6/18/2013 7:00 6/18/2013 7:10 6/18/2013 7:20 6/18/2013 7:30 6/18/2013 7:40 6/18/2013 7:50 6/18/2013 8:00 6/18/2013 8:10 6/18/2013 8:20 6/18/2013 8:30 6/18/2013 8:40 6/18/2013 8:50 6/18/2013 9:00 6/18/2013 9:10 6/18/2013 9:20 6/18/2013 9:30 6/18/2013 9:40 6/18/2013 9:50 6.50 6.30 6.56 6.47 5.77 6.43 6.56 5.96 6.64 6.22 6.22 5.95 6.28 6.78 6.65 6.33 6.44 6.25 6.15 6.08 6.42 6.34 6.40 6.46 6.50 6.45 6.56 6.41 6.66 6.39 6.48 6.44 6.55 6.45 109 6.67 6.48 6.64 6.65 5.97 6.70 6.54 6.12 6.72 6.48 6.39 6.19 6.40 6.82 6.60 6.53 6.72 6.50 6.59 6.57 6.50 6.46 6.47 6.53 6.58 6.59 6.63 6.48 6.62 6.47 6.59 6.46 6.66 6.41 8.10 8.10 8.10 8.10 8.08 8.09 8.07 8.06 8.08 8.07 8.08 8.06 8.07 8.07 8.06 8.06 8.06 8.06 8.06 8.06 8.06 8.06 8.06 8.05 8.06 8.06 8.06 8.06 8.07 8.07 8.07 8.07 8.08 8.08 7/29/2013 23:03 7/29/2013 23:13 7/29/2013 23:23 7/29/2013 23:33 7/29/2013 23:43 7/29/2013 23:53 7/30/2013 0:03 7/30/2013 0:13 7/30/2013 0:23 7/30/2013 0:33 7/30/2013 0:43 7/30/2013 0:53 7/30/2013 1:03 7/30/2013 1:13 7/30/2013 1:23 7/30/2013 1:33 7/30/2013 1:43 7/30/2013 1:53 7/30/2013 2:03 7/30/2013 2:13 7/30/2013 2:23 7/30/2013 2:33 7/30/2013 2:43 7/30/2013 2:53 7/30/2013 3:03 7/30/2013 3:13 7/30/2013 3:23 7/30/2013 3:33 7/30/2013 3:43 7/30/2013 3:53 7/30/2013 4:03 7/30/2013 4:13 7/30/2013 4:23 7/30/2013 4:33 6.85 6.72 6.68 6.66 6.56 6.55 6.43 6.38 6.33 6.25 6.24 6.19 6.10 6.01 6.01 6.01 5.96 5.93 5.80 5.79 5.69 5.56 5.40 5.36 5.36 5.28 5.29 5.29 5.43 5.40 5.36 5.34 5.34 5.31 3.72 3.68 3.61 3.71 3.76 3.71 3.74 3.74 3.71 3.69 3.71 3.70 3.64 3.63 3.66 3.54 3.60 3.70 3.58 3.67 3.60 3.66 3.74 4.25 4.00 4.26 4.32 4.44 4.79 4.94 4.88 5.23 4.65 4.95 8.00 7.99 7.98 7.98 7.97 8.01 8.00 8.00 8.00 7.97 7.99 7.98 7.97 7.96 7.93 7.95 7.95 7.93 7.93 7.92 7.93 7.92 7.93 7.92 7.92 7.91 7.90 7.88 7.87 7.88 7.88 7.87 7.89 7.88 5/30/2013 23:09 5/30/2013 23:19 5/30/2013 23:29 5/30/2013 23:39 5/30/2013 23:49 5/30/2013 23:59 5/31/2013 0:09 5/31/2013 0:19 5/31/2013 0:29 5/31/2013 0:39 5/31/2013 0:49 5/31/2013 0:59 5/31/2013 1:09 5/31/2013 1:19 5/31/2013 1:29 5/31/2013 1:39 5/31/2013 1:49 5/31/2013 1:59 5/31/2013 2:09 5/31/2013 2:19 5/31/2013 2:29 5/31/2013 2:39 5/31/2013 2:49 5/31/2013 2:59 5/31/2013 3:09 5/31/2013 3:19 5/31/2013 3:29 5/31/2013 3:39 5/31/2013 3:49 5/31/2013 3:59 5/31/2013 4:09 5/31/2013 4:19 5/31/2013 4:29 5/31/2013 4:39 5.34 5.30 5.21 5.20 5.09 5.07 5.08 4.96 4.95 4.90 4.98 4.93 4.95 4.83 4.90 4.92 4.78 4.85 4.78 4.73 4.78 4.76 4.77 4.79 4.73 4.75 4.74 4.69 4.68 4.71 4.73 4.72 4.73 4.67 6.00 6.03 5.99 5.99 5.99 5.98 5.98 5.96 5.95 5.97 5.97 5.97 5.96 5.94 5.96 5.96 5.94 5.93 5.94 5.95 5.93 5.91 5.94 5.94 5.92 5.94 5.93 5.91 5.93 5.93 5.91 5.93 5.93 5.90 7.71 7.71 7.70 7.70 7.70 7.70 7.70 7.70 7.70 7.70 7.70 7.70 7.70 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 6/18/2013 10:00 6/18/2013 10:10 6/18/2013 10:20 6/18/2013 10:30 6/18/2013 10:40 6/18/2013 10:50 6/18/2013 11:00 6/18/2013 11:10 6/18/2013 11:20 6/18/2013 11:30 6/18/2013 11:40 6/18/2013 11:50 6/18/2013 12:00 6/18/2013 12:10 6/18/2013 12:20 6/18/2013 12:30 6/18/2013 12:40 6/18/2013 12:50 6/18/2013 13:00 6/18/2013 13:10 6/18/2013 13:20 6/18/2013 13:30 6/18/2013 13:40 6/18/2013 13:50 6/18/2013 14:00 6/18/2013 14:10 6/18/2013 14:20 6/18/2013 14:30 6/18/2013 14:40 6/18/2013 14:50 6/18/2013 15:00 6/18/2013 15:10 6/18/2013 15:20 6/18/2013 15:30 6.79 6.84 6.80 6.66 6.84 6.89 6.60 7.02 6.72 6.97 6.84 7.32 7.27 7.33 7.57 7.58 7.37 7.82 7.84 7.96 8.21 8.48 8.60 8.51 8.52 8.53 8.56 8.32 8.55 9.27 9.04 9.31 8.89 8.71 110 6.57 6.49 6.57 6.68 6.52 6.65 6.50 6.69 6.68 6.95 6.75 6.86 6.99 6.89 7.13 7.16 7.18 7.22 7.02 7.28 7.30 7.36 7.51 7.31 7.42 7.26 7.31 7.27 7.10 7.26 7.13 7.14 7.30 6.82 8.08 8.07 8.08 8.08 8.09 8.09 8.08 8.09 8.10 8.10 8.10 8.10 8.10 8.10 8.10 8.10 8.11 8.11 8.09 8.10 8.11 8.12 8.12 8.12 8.13 8.12 8.12 8.12 8.12 8.12 8.12 8.12 8.13 8.12 7/30/2013 4:43 7/30/2013 4:53 7/30/2013 5:03 7/30/2013 5:13 7/30/2013 5:23 7/30/2013 5:33 7/30/2013 5:43 7/30/2013 5:53 7/30/2013 6:03 7/30/2013 6:13 7/30/2013 6:23 7/30/2013 6:33 7/30/2013 6:43 7/30/2013 6:53 7/30/2013 7:03 7/30/2013 7:13 7/30/2013 7:23 7/30/2013 7:33 7/30/2013 7:43 7/30/2013 7:53 7/30/2013 8:03 7/30/2013 8:13 7/30/2013 8:23 7/30/2013 8:33 7/30/2013 8:43 7/30/2013 8:53 7/30/2013 9:03 7/30/2013 9:13 7/30/2013 9:23 7/30/2013 9:33 7/30/2013 9:43 7/30/2013 9:53 7/30/2013 10:03 7/30/2013 10:13 5.15 5.25 5.24 3.54 5.19 5.13 5.14 5.13 5.16 5.12 5.10 5.00 5.10 5.11 5.17 5.22 5.33 5.35 5.39 5.15 5.40 5.54 5.56 5.58 5.75 5.72 5.79 6.03 6.08 6.25 6.45 6.61 7.55 7.41 4.55 5.19 4.80 5.00 4.90 4.77 4.92 4.80 4.73 4.53 4.66 4.92 4.59 4.68 4.34 4.42 4.74 4.66 4.46 4.32 3.85 4.11 4.25 3.94 3.88 3.51 3.13 3.48 3.34 3.18 3.12 3.09 3.12 3.01 7.89 7.89 7.88 7.86 7.87 7.86 7.86 7.86 7.85 7.85 7.85 7.86 7.85 7.85 7.86 7.87 7.86 7.85 7.85 7.84 7.83 7.82 7.83 7.82 7.82 7.82 7.83 7.85 7.82 7.82 7.83 7.83 7.84 7.86 5/31/2013 4:49 5/31/2013 4:59 5/31/2013 5:09 5/31/2013 5:19 5/31/2013 5:29 5/31/2013 5:39 5/31/2013 5:49 5/31/2013 5:59 5/31/2013 6:09 5/31/2013 6:19 5/31/2013 6:29 5/31/2013 6:39 5/31/2013 6:49 5/31/2013 6:59 5/31/2013 7:09 5/31/2013 7:19 5/31/2013 7:29 5/31/2013 7:39 5/31/2013 7:49 5/31/2013 7:59 5/31/2013 8:09 5/31/2013 8:19 5/31/2013 8:29 5/31/2013 8:39 5/31/2013 8:49 5/31/2013 8:59 5/31/2013 9:09 5/31/2013 9:19 5/31/2013 9:29 5/31/2013 9:39 5/31/2013 9:49 5/31/2013 9:59 5/31/2013 10:09 5/31/2013 10:19 4.63 4.70 4.65 4.68 4.71 4.46 4.67 4.58 4.59 4.58 4.59 4.59 4.60 4.53 4.62 4.63 4.66 4.60 4.64 4.64 4.65 4.82 4.76 4.78 4.87 4.90 4.84 4.93 4.97 4.84 5.03 5.05 5.04 5.08 5.92 5.93 5.91 5.93 5.90 5.87 5.92 5.92 5.92 5.94 5.93 5.92 5.91 5.90 5.94 5.91 5.94 5.91 5.90 5.93 5.91 5.94 5.95 5.94 5.96 5.97 5.95 5.97 5.97 6.01 6.01 6.01 6.02 6.05 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.69 7.70 7.70 7.70 7.70 7.70 7.70 7.70 7.69 7.69 7.70 7.70 7.70 7.70 7.70 7.71 7.71 7.71 7.71 7.69 7.71 7.71 7.70 7.61 6/18/2013 15:40 6/18/2013 15:50 6/18/2013 16:00 6/18/2013 16:10 6/18/2013 16:20 6/18/2013 16:30 6/18/2013 16:40 6/18/2013 16:50 6/18/2013 17:00 6/18/2013 17:10 6/18/2013 17:20 6/18/2013 17:30 6/18/2013 17:40 6/18/2013 17:50 6/18/2013 18:00 6/18/2013 18:10 6/18/2013 18:20 6/18/2013 18:30 6/18/2013 18:40 6/18/2013 18:50 6/18/2013 19:00 6/18/2013 19:10 6/18/2013 19:20 6/18/2013 19:30 6/18/2013 19:40 6/18/2013 19:50 6/18/2013 20:00 6/18/2013 20:10 6/18/2013 20:20 6/18/2013 20:30 6/18/2013 20:40 6/18/2013 20:50 6/18/2013 21:00 6/18/2013 21:10 8.34 8.13 8.62 9.15 9.55 9.42 9.57 9.33 9.39 9.10 9.16 8.78 8.82 8.85 8.62 8.79 9.20 8.40 8.60 7.97 8.07 8.02 8.15 8.06 7.95 7.69 8.05 8.16 8.45 7.81 7.77 8.13 7.80 7.91 111 7.15 7.00 6.88 6.89 7.10 6.87 6.85 6.89 6.89 6.46 6.66 6.71 6.85 7.11 6.80 6.53 7.00 6.87 7.03 6.71 6.52 6.90 6.92 6.54 6.34 6.68 6.47 7.19 6.98 6.33 6.48 6.86 6.41 6.63 8.13 8.12 8.12 8.13 8.14 8.13 8.13 8.13 8.14 8.13 8.14 8.15 8.16 8.16 8.15 8.14 8.15 8.14 8.14 8.13 8.14 8.15 8.15 8.15 8.14 8.14 8.14 8.14 8.16 8.13 8.14 8.15 8.13 8.13 7/30/2013 10:23 7/30/2013 10:33 7/30/2013 10:43 7/30/2013 10:53 7/30/2013 11:03 7/30/2013 11:13 7/30/2013 11:23 7/30/2013 11:33 7/30/2013 11:43 7/30/2013 11:53 7/30/2013 12:03 7/30/2013 12:13 7/30/2013 12:23 7/30/2013 12:33 7/30/2013 12:43 7/30/2013 12:53 7/30/2013 13:03 7/30/2013 13:13 7/30/2013 13:23 7/30/2013 13:33 7/30/2013 13:43 7/30/2013 13:53 7/30/2013 14:03 7/30/2013 14:13 7/30/2013 14:23 7/30/2013 14:33 7/30/2013 14:43 7/30/2013 14:53 7/30/2013 15:03 7/30/2013 15:13 7/30/2013 15:23 7/30/2013 15:33 7/30/2013 15:43 7/30/2013 15:53 7.36 7.55 8.10 9.58 8.71 8.77 8.67 12.82 10.84 10.33 11.93 15.89 13.08 11.50 11.19 11.41 11.58 11.46 13.33 14.50 10.42 10.38 10.00 10.62 10.71 10.92 10.76 10.66 10.09 10.20 11.61 13.59 13.75 14.99 3.10 2.66 2.60 2.20 2.61 2.47 2.21 2.12 2.37 2.35 2.44 2.15 2.68 2.38 2.47 2.14 2.49 2.13 2.25 2.22 2.13 2.16 2.19 2.31 2.27 2.26 2.37 2.36 2.45 2.57 2.64 2.71 2.79 2.80 7.86 7.87 7.88 7.93 7.91 7.92 7.95 7.96 7.97 7.99 7.99 8.00 8.04 8.04 8.03 8.06 8.07 8.05 8.06 8.06 8.07 8.04 8.03 8.04 8.03 8.05 8.06 8.05 8.03 8.03 8.05 8.05 8.08 8.09 5/31/2013 10:29 5/31/2013 10:39 5/31/2013 10:49 5/31/2013 10:59 5/31/2013 11:09 5/31/2013 11:19 5/31/2013 11:29 5/31/2013 11:39 5/31/2013 11:49 5/31/2013 11:59 5/31/2013 12:09 5/31/2013 12:19 5/31/2013 12:29 5/31/2013 12:39 5/31/2013 12:49 5/31/2013 12:59 5/31/2013 13:09 5/31/2013 13:19 5/31/2013 13:29 5/31/2013 13:39 5/31/2013 13:49 5/31/2013 13:59 5/31/2013 14:09 5/31/2013 14:19 5/31/2013 14:29 5/31/2013 14:39 5/31/2013 14:49 5/31/2013 14:59 5/31/2013 15:09 5/31/2013 15:19 5/31/2013 15:29 5.04 5.07 5.14 5.20 5.18 5.10 5.29 5.58 5.57 5.52 5.40 5.58 5.67 5.62 5.71 5.94 5.87 5.95 5.82 5.97 6.08 6.09 5.95 6.29 6.45 6.53 6.28 6.28 6.23 6.12 6.20 6.14 6.14 6.13 6.22 6.22 6.24 6.27 6.29 6.34 6.28 6.25 6.26 6.27 6.25 6.26 6.27 6.30 6.32 6.30 6.31 6.32 6.31 6.32 6.32 6.19 6.21 6.20 6.20 6.21 6.24 6.22 7.70 7.71 7.72 7.72 7.73 7.74 7.72 7.74 7.73 7.72 7.72 7.72 7.71 7.71 7.72 7.73 7.73 7.72 7.72 7.72 7.73 7.73 7.73 7.73 7.75 7.75 7.73 7.73 7.72 7.71 7.71 6/18/2013 21:20 6/18/2013 21:30 6/18/2013 21:40 6/18/2013 21:50 6/18/2013 22:00 6/18/2013 22:10 6/18/2013 22:20 6/18/2013 22:30 6/18/2013 22:40 6/18/2013 22:50 6/18/2013 23:00 6/18/2013 23:10 6/18/2013 23:20 6/18/2013 23:30 6/18/2013 23:40 6/18/2013 23:50 6/19/2013 0:00 6/19/2013 0:10 6/19/2013 0:20 6/19/2013 0:30 6/19/2013 0:40 6/19/2013 0:50 6/19/2013 1:00 6/19/2013 1:10 6/19/2013 1:20 6/19/2013 1:30 6/19/2013 1:40 6/19/2013 1:50 6/19/2013 2:00 6/19/2013 2:10 6/19/2013 2:20 7.79 7.67 7.63 7.35 7.40 7.39 7.30 7.29 6.97 7.40 7.18 7.27 7.32 7.26 7.25 7.18 7.09 7.09 7.00 6.95 6.85 6.79 6.80 6.77 6.66 6.00 6.65 6.22 6.34 6.43 6.57 112 6.57 6.52 6.56 6.47 6.40 6.46 6.44 6.42 6.43 6.46 6.41 6.36 6.36 6.33 6.41 6.36 6.36 6.32 6.47 6.36 6.36 6.36 6.34 6.36 6.33 6.35 6.31 6.29 6.29 6.26 6.26 8.14 8.14 8.14 8.14 8.15 8.15 8.15 8.15 8.14 8.15 8.15 8.15 8.16 8.16 8.16 8.16 8.17 8.16 8.18 8.18 8.18 8.18 8.18 8.19 8.19 8.19 8.19 8.19 8.19 8.19 8.19 7/30/2013 16:03 7/30/2013 16:13 7/30/2013 16:23 7/30/2013 16:33 7/30/2013 16:43 7/30/2013 16:53 7/30/2013 17:03 7/30/2013 17:13 7/30/2013 17:23 7/30/2013 17:33 7/30/2013 17:43 7/30/2013 17:53 7/30/2013 18:03 7/30/2013 18:13 7/30/2013 18:23 7/30/2013 18:33 7/30/2013 18:43 7/30/2013 18:53 7/30/2013 19:03 7/30/2013 19:13 7/30/2013 19:23 7/30/2013 19:33 7/30/2013 19:43 7/30/2013 19:53 7/30/2013 20:03 7/30/2013 20:13 7/30/2013 20:23 7/30/2013 20:33 7/30/2013 20:43 7/30/2013 20:53 7/30/2013 21:03 13.79 12.46 14.45 13.53 12.28 11.18 10.77 10.61 9.01 10.16 9.93 9.62 9.57 9.46 9.34 9.28 8.32 9.65 9.05 9.03 8.83 8.55 8.32 8.27 8.03 7.81 6.72 7.46 7.25 7.11 7.06 2.83 2.87 2.88 2.89 2.86 2.86 2.90 2.88 2.89 2.91 2.93 2.93 2.93 2.93 2.93 2.96 2.92 2.93 2.90 2.91 2.88 2.89 2.88 2.89 2.90 2.92 2.96 2.98 2.89 2.89 2.88 8.10 8.09 8.10 8.12 8.11 8.11 8.11 8.10 8.10 8.09 8.07 8.06 8.04 8.04 8.03 8.03 8.03 8.03 8.03 8.02 8.01 8.00 7.99 7.99 7.98 7.97 7.96 7.95 7.94 7.93 7.92 Appendix 2. (continued) August 8/6/2013 11:14 8/6/2013 11:24 8/6/2013 11:34 8/6/2013 11:44 8/6/2013 11:54 8/6/2013 12:04 8/6/2013 12:14 8/6/2013 12:24 8/6/2013 12:34 8/6/2013 12:44 8/6/2013 12:54 8/6/2013 13:04 8/6/2013 13:14 8/6/2013 13:24 8/6/2013 13:34 8/6/2013 13:44 8/6/2013 13:54 8/6/2013 14:04 8/6/2013 14:14 8/6/2013 14:24 8/6/2013 14:34 8/6/2013 14:44 8/6/2013 14:54 8/6/2013 15:04 8/6/2013 15:14 8/6/2013 15:24 8/6/2013 15:34 8/6/2013 15:44 DO 8.65 7.34 7.26 7.21 7.08 7.36 7.48 7.43 7.66 7.83 7.4 7.36 7.18 7.25 7.14 7.06 7 7.25 7.69 7.95 8.06 8.07 8.21 8.72 8.59 8.35 8.31 8.12 DO 9.37 9.65 9.84 10.76 10.46 10.23 10.39 10.36 10.59 10.92 10.34 10.38 10.05 10.23 10.1 10.03 9.96 10.37 10.95 11.06 11.34 11.44 11.68 11.95 12.11 11.86 11.7 11.31 pH 8 7.96 7.96 7.95 7.97 8 8.01 8.02 8.03 8.05 8.03 8.03 8.02 8.02 8.02 8.01 8.02 8.03 8.04 8.05 8.07 8.09 8.1 8.11 8.11 8.11 8.1 8.09 September 9/11/2013 19:27 9/11/2013 19:37 9/11/2013 19:47 9/11/2013 19:57 9/11/2013 20:07 9/11/2013 20:17 9/11/2013 20:27 9/11/2013 20:37 9/11/2013 20:47 9/11/2013 20:57 9/11/2013 21:07 9/11/2013 21:17 9/11/2013 21:27 9/11/2013 21:37 9/11/2013 21:47 9/11/2013 21:57 9/11/2013 22:07 9/11/2013 22:17 9/11/2013 22:27 9/11/2013 22:37 9/11/2013 22:47 9/11/2013 22:57 9/11/2013 23:07 9/11/2013 23:17 9/11/2013 23:27 9/11/2013 23:37 9/11/2013 23:47 9/11/2013 23:57 113 DO 9.54 7.93 7.34 7.03 6.8 6.58 6.53 6.45 6.41 6.38 6.29 6.28 6.18 6.23 6.09 6.08 5.95 6.02 6.07 5.83 5.54 5.47 5.38 5.38 5.2 5.14 5.01 4.93 DO 0.23 0.19 0.17 0.19 0.09 0.07 0.06 0.05 0.07 0.05 0.03 0.03 0.02 0.01 0.01 0.01 0.03 0.01 0 0 0 -0.01 -0.01 -0.01 -0.01 -0.02 -0.01 -0.02 pH 8.44 8.42 8.41 8.38 8.36 8.32 8.33 8.28 8.29 8.29 8.25 8.23 8.23 8.23 8.24 8.24 8.22 8.2 8.2 8.15 8.17 8.15 8.14 8.14 8.13 8.11 8.1 8.08 8/6/2013 15:54 8/6/2013 16:04 8/6/2013 16:14 8/6/2013 16:24 8/6/2013 16:34 8/6/2013 16:44 8/6/2013 16:54 8/6/2013 17:04 8/6/2013 17:14 8/6/2013 17:24 8/6/2013 17:34 8/6/2013 17:44 8/6/2013 17:54 8/6/2013 18:04 8/6/2013 18:14 8/6/2013 18:24 8/6/2013 18:34 8/6/2013 18:44 8/6/2013 18:54 8/6/2013 19:04 8/6/2013 19:14 8/6/2013 19:24 8/6/2013 19:34 8/6/2013 19:44 8/6/2013 19:54 8/6/2013 20:04 8/6/2013 20:14 8/6/2013 20:24 8/6/2013 20:34 8/6/2013 20:44 8/6/2013 20:54 8.09 8.11 8.39 8.45 8.54 8.59 8.52 8.44 8.44 8.5 8.42 8.46 8.43 8.51 8.46 8.34 8.26 8.18 8.07 8.01 7.9 7.95 8.19 8.05 8.11 8.02 7.93 7.96 7.8 7.71 7.55 11.43 11.52 11.78 12.04 11.97 12.08 12.04 11.91 11.91 11.93 11.89 11.94 11.9 11.96 11.94 11.78 11.65 11.56 11.44 11.34 11.24 11.21 11.21 11.16 11.09 11.01 10.73 10.84 10.73 10.62 10.52 8.09 8.09 8.11 8.12 8.12 8.12 8.12 8.12 8.12 8.12 8.12 8.12 8.12 8.12 8.11 8.05 8.12 8.12 8.11 8.11 8.11 8.12 8.11 8.11 8.1 8.1 8.1 8.1 8.09 8.09 8.07 9/12/2013 0:07 9/12/2013 0:17 9/12/2013 0:27 9/12/2013 0:37 9/12/2013 0:47 9/12/2013 0:57 9/12/2013 1:07 9/12/2013 1:17 9/12/2013 1:27 9/12/2013 1:37 9/12/2013 1:47 9/12/2013 1:57 9/12/2013 2:07 9/12/2013 2:17 9/12/2013 2:27 9/12/2013 2:37 9/12/2013 2:47 9/12/2013 2:57 9/12/2013 3:07 9/12/2013 3:17 9/12/2013 3:27 9/12/2013 3:37 9/12/2013 3:47 9/12/2013 3:57 9/12/2013 4:07 9/12/2013 4:17 9/12/2013 4:27 9/12/2013 4:37 9/12/2013 4:47 9/12/2013 4:57 9/12/2013 5:07 114 4.82 4.84 4.69 4.59 4.46 4.48 4.35 4.27 4.13 4.11 4.08 4.09 4 4 4.03 3.93 3.9 3.92 3.82 3.77 3.79 3.7 3.68 3.51 3.53 3.48 3.45 3.59 3.51 3.67 3.72 -0.02 -0.02 -0.03 -0.03 -0.04 -0.03 -0.03 -0.05 -0.04 -0.03 -0.04 -0.04 -0.05 -0.04 -0.05 -0.04 -0.04 -0.06 -0.06 -0.06 -0.07 -0.07 -0.06 -0.06 -0.06 -0.05 -0.05 -0.05 -0.05 -0.06 -0.06 8.07 8.09 8.08 8.07 8.07 8.06 8.05 8.05 8.05 8.05 8.04 8.04 8.04 8.04 8.03 8.03 8.02 8.01 8.01 8 8 7.98 7.97 7.98 7.99 7.98 7.97 7.98 7.99 7.99 7.98 8/6/2013 21:04 8/6/2013 21:14 8/6/2013 21:24 8/6/2013 21:34 8/6/2013 21:44 8/6/2013 21:54 8/6/2013 22:04 8/6/2013 22:14 8/6/2013 22:24 8/6/2013 22:34 8/6/2013 22:44 8/6/2013 22:54 8/6/2013 23:04 8/6/2013 23:14 8/6/2013 23:24 8/6/2013 23:34 8/6/2013 23:44 8/6/2013 23:54 8/7/2013 0:04 8/7/2013 0:14 8/7/2013 0:24 8/7/2013 0:34 8/7/2013 0:44 8/7/2013 0:54 8/7/2013 1:04 8/7/2013 1:14 8/7/2013 1:24 8/7/2013 1:34 8/7/2013 1:44 8/7/2013 1:54 8/7/2013 2:04 7.53 7.44 7.38 7.29 7.19 7.13 6.93 7.1 7.03 6.99 6.85 6.83 6.75 6.63 6.56 6.5 6.44 6.36 6.32 6.25 6.22 6.17 6.11 6.07 6.04 5.96 5.92 5.87 5.84 5.78 5.73 10.35 10.29 10.19 10.1 9.97 9.86 9.75 9.67 9.58 9.52 9.62 9.45 9.29 9.19 9.05 8.94 8.86 8.77 8.72 8.66 8.68 8.62 8.52 8.44 8.43 8.38 8.27 8.23 8.15 8.11 8.07 8.07 8.06 8.05 8.05 8.04 8.03 8.03 8.03 8.02 8.01 8.01 8 7.99 7.99 7.98 7.98 7.97 7.96 7.96 7.95 7.95 7.94 7.94 7.93 7.93 7.93 7.92 7.91 7.91 7.91 7.9 9/12/2013 5:17 9/12/2013 5:27 9/12/2013 5:37 9/12/2013 5:47 9/12/2013 5:57 9/12/2013 6:07 9/12/2013 6:17 9/12/2013 6:27 9/12/2013 6:37 9/12/2013 6:47 9/12/2013 6:57 9/12/2013 7:07 9/12/2013 7:17 9/12/2013 7:27 9/12/2013 7:37 9/12/2013 7:47 9/12/2013 7:57 9/12/2013 8:07 9/12/2013 8:17 9/12/2013 8:27 9/12/2013 8:37 9/12/2013 8:47 9/12/2013 8:57 9/12/2013 9:07 9/12/2013 9:17 9/12/2013 9:27 9/12/2013 9:37 9/12/2013 9:47 9/12/2013 9:57 9/12/2013 10:07 9/12/2013 10:17 115 3.67 3.63 3.52 3.62 3.48 3.43 3.47 3.46 0.58 4.11 3.23 3.93 2.82 4.12 3.3 3.95 4.44 4.48 4.39 4.82 5 5.33 5.58 5.55 5.43 5.59 6.02 6.13 5.61 5.18 5.15 -0.06 -0.07 -0.06 -0.07 -0.07 -0.06 -0.06 -0.06 -0.07 -0.08 -0.07 -0.07 -0.07 0.41 0.55 -0.07 -0.07 -0.04 -0.07 5.41 5.52 5.86 6.1 6.04 5.92 6.06 6.49 6.65 6.16 5.83 5.57 7.97 7.96 7.96 7.97 7.96 7.96 7.96 7.96 7.95 7.96 7.94 7.94 7.93 7.92 7.91 7.9 7.9 7.93 7.94 7.99 8.01 8.03 8.05 8.05 8.04 8.05 8.09 8.11 8.07 8.03 7.88 8/7/2013 2:14 8/7/2013 2:24 8/7/2013 2:34 8/7/2013 2:44 8/7/2013 2:54 8/7/2013 3:04 8/7/2013 3:14 8/7/2013 3:24 8/7/2013 3:34 8/7/2013 3:44 8/7/2013 3:54 8/7/2013 4:04 8/7/2013 4:14 8/7/2013 4:24 8/7/2013 4:34 8/7/2013 4:44 8/7/2013 4:54 8/7/2013 5:04 8/7/2013 5:14 8/7/2013 5:24 8/7/2013 5:34 8/7/2013 5:44 8/7/2013 5:54 8/7/2013 6:04 8/7/2013 6:14 8/7/2013 6:24 8/7/2013 6:34 8/7/2013 6:44 8/7/2013 6:54 8/7/2013 7:04 8/7/2013 7:14 5.7 5.42 5.4 5.25 5.28 5.26 5.25 5.16 5.2 5.07 5.03 4.99 4.93 4.88 4.87 4.76 4.83 4.72 4.75 4.73 4.65 4.64 4.67 4.61 4.64 4.61 4.58 4.66 4.66 4.71 4.85 8.04 8.03 7.94 7.89 7.86 7.83 7.79 7.72 7.69 7.68 7.66 7.6 7.6 7.53 7.45 7.51 7.46 7.43 7.36 7.35 7.31 7.32 7.2 7.25 6.98 6.96 6.95 6.88 6.79 6.84 6.95 7.9 7.9 7.89 7.89 7.88 7.88 7.88 7.87 7.87 7.87 7.86 7.85 7.85 7.85 7.84 7.84 7.84 7.83 7.83 7.83 7.83 7.82 7.82 7.82 7.81 7.82 7.82 7.82 7.82 7.81 7.81 9/12/2013 10:27 9/12/2013 10:37 9/12/2013 10:47 9/12/2013 10:57 9/12/2013 11:07 9/12/2013 11:17 9/12/2013 11:27 9/12/2013 11:37 9/12/2013 11:47 9/12/2013 11:57 9/12/2013 12:07 9/12/2013 12:17 9/12/2013 12:27 9/12/2013 12:37 9/12/2013 12:47 9/12/2013 12:57 9/12/2013 13:07 9/12/2013 13:17 9/12/2013 13:27 9/12/2013 13:37 9/12/2013 13:47 9/12/2013 13:57 9/12/2013 14:07 9/12/2013 14:17 9/12/2013 14:27 9/12/2013 14:37 9/12/2013 14:47 9/12/2013 14:57 9/12/2013 15:07 9/12/2013 15:17 9/12/2013 15:27 116 5.02 0.71 0.36 5.12 4.34 4.87 5.04 5.05 5.08 5.15 5.19 5.18 5.21 5.27 5.33 5.37 5.43 5.49 5.53 5.49 5.5 5.53 5.59 5.54 5.42 5.17 5.06 5.05 5.02 4.97 4.98 5.66 5.64 4.29 5.74 5.73 5.67 5.71 5.55 5.5 5.48 5.53 5.55 5.56 5.55 5.56 5.62 5.74 5.77 5.8 5.87 5.88 5.89 5.88 5.89 6.29 5.3 5.39 5.35 5.5 5.49 5.47 7.82 7.83 7.75 7.74 7.71 7.67 7.17 7.65 7.65 7.65 7.66 7.66 7.66 7.68 7.68 7.66 7.65 7.63 7.65 7.66 7.65 7.64 7.63 7.62 7.62 7.59 7.58 7.57 7.55 7.53 7.52 8/7/2013 7:24 8/7/2013 7:34 8/7/2013 7:44 8/7/2013 7:54 8/7/2013 8:04 8/7/2013 8:14 8/7/2013 8:24 8/15/2013 20:10 8/15/2013 20:20 8/15/2013 20:30 8/15/2013 20:40 8/15/2013 20:50 8/15/2013 21:00 8/15/2013 21:10 8/15/2013 21:20 8/15/2013 21:30 8/15/2013 21:40 8/15/2013 21:50 8/15/2013 22:00 8/15/2013 22:10 8/15/2013 22:20 8/15/2013 22:30 8/15/2013 22:40 8/15/2013 22:50 8/15/2013 23:00 8/15/2013 23:10 8/15/2013 23:20 8/15/2013 23:30 8/15/2013 23:40 8/15/2013 23:50 8/16/2013 0:00 4.81 4.85 4.89 4.9 5.07 5.08 5.28 6.13 3.83 1.36 1.13 1.89 0.7 0.9 0.79 0.25 0.47 0.35 0.1 -0.05 -0.04 -0.26 -0.04 -0.25 -0.01 0.06 0.26 -0.26 0.87 -0.21 0.93 7.06 7.17 7.26 7.32 7.39 7.37 7.61 8.97 7.87 8.52 7.47 7.85 8.08 8.29 7.7 8.03 7.82 7.75 6.75 7.26 7.76 7.62 7.14 7.23 7.58 6.85 6.51 6.75 6.95 6.56 6.89 7.82 7.82 7.82 7.82 7.82 7.82 7.83 6.92 7.28 8.41 8.46 8.43 8.45 8.4 8.36 8.41 8.34 8.39 8.37 8.37 8.36 8.37 8.34 8.35 8.31 8.32 8.31 8.31 8.29 8.29 8.29 9/12/2013 15:37 9/12/2013 15:47 9/12/2013 15:57 9/12/2013 16:07 9/12/2013 16:17 9/12/2013 16:27 9/12/2013 16:37 9/12/2013 16:47 9/12/2013 16:57 9/12/2013 17:07 9/12/2013 17:17 9/12/2013 17:27 9/12/2013 17:37 9/12/2013 17:47 9/12/2013 17:57 9/12/2013 18:07 9/12/2013 18:17 9/12/2013 18:27 9/12/2013 18:37 9/12/2013 18:47 9/12/2013 18:57 9/12/2013 19:07 9/12/2013 19:17 9/12/2013 19:27 9/12/2013 19:37 9/12/2013 19:47 9/12/2013 19:57 9/12/2013 20:07 9/12/2013 20:17 9/12/2013 20:27 9/12/2013 20:37 117 4.94 4.94 4.88 4.9 4.84 4.77 4.76 4.78 4.75 4.78 4.74 4.72 4.79 4.83 4.86 4.8 4.71 4.66 4.71 4.61 4.66 4.61 4.58 4.45 4.55 4.47 4.4 4.3 4.23 4.12 4.03 5.38 5.42 4.64 4.72 4.69 4.68 4.65 4.71 4.49 4.46 4.48 4.39 4.44 4.48 4.66 4.71 4.73 4.75 4.7 4.98 5.06 4.89 4.9 4.76 4.61 4.66 4.53 4.35 4.3 4.35 4.42 7.48 7.48 7.43 7.42 7.41 7.37 7.37 7.37 7.36 7.34 7.33 7.34 7.33 7.32 7.32 7.29 7.3 7.31 7.3 7.28 7.28 7.28 7.27 7.27 7.26 7.23 7.22 7.22 7.2 7.19 7.17 8/16/2013 0:10 8/16/2013 0:20 8/16/2013 0:30 8/16/2013 0:40 8/16/2013 0:50 8/16/2013 1:00 8/16/2013 1:10 8/16/2013 1:20 8/16/2013 1:30 8/16/2013 1:40 8/16/2013 1:50 8/16/2013 2:00 8/16/2013 2:10 8/16/2013 2:20 8/16/2013 2:30 8/16/2013 2:40 8/16/2013 2:50 8/16/2013 3:00 8/16/2013 3:10 8/16/2013 3:20 8/16/2013 3:30 8/16/2013 3:40 8/16/2013 3:50 8/16/2013 4:00 8/16/2013 4:10 8/16/2013 4:20 8/16/2013 4:30 8/16/2013 4:40 8/16/2013 4:50 8/16/2013 5:00 8/16/2013 5:10 -0.08 -0.36 -0.4 -0.42 -0.41 -0.29 -0.25 -0.39 -0.29 -0.44 -0.34 -0.43 -0.2 -0.27 -0.48 -0.3 -0.42 -0.29 -0.35 0.57 -0.49 -0.16 -0.3 0.38 0.3 0.87 0.29 0.22 0.07 0.32 0.6 6.92 7.14 7.03 6.03 5.33 6.77 6.2 6.7 6.83 6.74 6.51 6.53 6.62 6.58 6.43 6.5 6.49 6.27 6.44 6.18 6.31 6.35 6.25 6.13 6.16 6.23 6.19 6.1 6.14 6.03 6.07 8.25 8.23 8.14 8.14 8.25 8.27 8.25 8.24 8.24 8.24 8.23 8.22 8.22 8.21 8.21 8.2 8.2 8.2 8.2 8.19 8.18 8.17 8.17 8.15 8.17 8.17 8.15 8.13 8.1 8.03 8.11 9/12/2013 20:47 9/12/2013 20:57 9/12/2013 21:07 9/12/2013 21:17 9/12/2013 21:27 9/12/2013 21:37 9/12/2013 21:47 9/12/2013 21:57 9/12/2013 22:07 9/12/2013 22:17 9/12/2013 22:27 9/12/2013 22:37 9/12/2013 22:47 9/12/2013 22:57 9/12/2013 23:07 9/12/2013 23:17 9/12/2013 23:27 9/12/2013 23:37 9/12/2013 23:47 9/12/2013 23:57 9/13/2013 0:07 9/13/2013 0:17 9/13/2013 0:27 9/13/2013 0:37 9/13/2013 0:47 9/13/2013 0:57 9/13/2013 1:07 9/13/2013 1:17 9/13/2013 1:27 9/13/2013 1:37 9/13/2013 1:47 118 3.97 3.98 4.14 3.92 4 4.04 3.85 3.51 3.71 3.45 3.6 3.46 3.44 3.55 3.45 3.36 3.39 3.19 3.26 3.2 3.07 2.88 2.99 2.99 3 2.98 3.03 3.06 3.01 2.99 3.26 4.47 4.46 4.39 4.35 4.35 4.32 4.32 4.37 4.33 4.31 4.28 4.17 4.11 4.07 4 3.9 3.8 3.7 3.56 3.66 3.59 3.56 3.61 3.57 3.58 3.51 3.57 3.47 3.47 3.48 3.6 7.13 7.03 6.96 6.98 6.97 6.96 6.96 6.98 6.99 6.99 7.01 7.03 7.02 7.03 7.02 6.98 6.97 6.96 6.96 6.97 6.97 6.97 6.97 6.97 6.98 6.99 7 7.01 7.02 7.03 7.03 8/16/2013 5:20 8/16/2013 5:30 8/16/2013 5:40 8/16/2013 5:50 8/16/2013 6:00 8/16/2013 6:10 8/16/2013 6:20 8/16/2013 6:30 8/16/2013 6:40 8/16/2013 6:50 8/16/2013 7:00 8/16/2013 7:10 8/16/2013 7:20 8/16/2013 7:30 8/16/2013 7:40 8/16/2013 7:50 1.04 0.67 1.08 1.39 0.39 0.31 1.28 1.09 1.97 1.57 1.35 1.94 1.03 1.54 2.39 3.87 6.07 6.05 6.07 6.04 5.97 5.93 5.94 5.88 5.95 5.95 5.89 5.96 5.94 5.97 6 6.13 8.13 8.12 8.13 8.12 8.12 8.13 8.13 8.11 8.12 8.1 8.11 8.11 8.09 8.09 8.09 8.09 9/13/2013 1:57 9/13/2013 2:07 9/13/2013 2:17 9/13/2013 2:27 9/13/2013 2:37 9/13/2013 2:47 9/13/2013 2:57 9/13/2013 3:07 9/13/2013 3:17 9/13/2013 3:27 9/13/2013 3:37 9/13/2013 3:47 9/13/2013 3:57 9/13/2013 4:07 9/13/2013 4:17 9/13/2013 4:27 3.05 3 3.13 3.11 2.89 2.69 2.85 2.99 2.94 2.76 2.83 3.02 2.61 2.8 2.41 2.37 3.59 3.7 3.7 3.7 3.79 3.86 3.78 3.76 3.74 3.76 3.73 3.71 3.79 3.77 3.82 3.72 7.03 7 7 7.25 7.43 7.55 7.64 7.69 7.69 7.71 7.72 7.75 7.75 7.74 7.73 7.73 Appendix 2. (continued) October 10/21/13 18:23 10/21/13 18:33 10/21/13 18:43 10/21/13 18:53 10/21/13 19:03 10/21/13 19:13 10/21/13 19:23 10/21/13 19:33 10/21/13 19:43 10/21/13 19:53 10/21/13 20:03 10/21/13 20:13 10/21/13 20:23 DO 8.91 7.85 7.46 7.28 7.18 7.09 7.02 6.91 6.84 6.82 6.77 6.64 6.61 DO 7.29 7.18 7.10 7.03 6.96 6.87 6.81 6.74 6.70 6.64 6.57 6.52 6.46 pH 8.49 8.49 8.63 8.56 8.50 8.67 8.61 8.59 8.56 8.55 8.54 8.53 8.52 November 11/8/2013 16:36 11/8/2013 16:46 11/8/2013 16:56 11/8/2013 17:06 11/8/2013 17:16 11/8/2013 17:26 11/8/2013 17:36 11/8/2013 17:46 11/8/2013 17:56 11/8/2013 18:06 11/8/2013 18:16 11/8/2013 18:26 11/8/2013 18:36 DO 7.80 6.35 5.91 5.77 5.66 5.62 5.29 5.34 5.42 5.55 5.54 5.48 5.43 119 DO 6.52 6.45 6.43 6.44 6.42 6.39 6.38 6.34 6.32 6.29 6.26 6.22 6.17 pH 8.60 8.61 8.62 8.62 8.62 8.62 8.63 8.63 8.65 8.65 8.65 8.65 8.65 December 12/13/2013 16:44 12/13/2013 16:54 12/13/2013 17:04 12/13/2013 17:14 12/13/2013 17:24 12/13/2013 17:34 12/13/2013 17:44 12/13/2013 17:54 12/13/2013 18:04 12/13/2013 18:14 12/13/2013 18:24 12/13/2013 18:34 12/13/2013 18:44 DO 8.96 6.93 6.37 6.11 5.91 5.76 5.64 5.56 5.49 5.39 5.34 5.27 5.22 DO 5.61 5.57 5.44 5.45 5.21 5.01 4.95 4.97 4.93 4.97 4.84 4.82 4.79 pH 8.70 8.69 8.71 8.71 8.70 8.70 8.71 8.70 8.67 8.64 8.65 8.64 8.64 10/21/13 20:33 10/21/13 20:43 10/21/13 20:53 10/21/13 21:03 10/21/13 21:13 10/21/13 21:23 10/21/13 21:33 10/21/13 21:43 10/21/13 21:53 10/21/13 22:03 10/21/13 22:13 10/21/13 22:23 10/21/13 22:33 10/21/13 22:43 10/21/13 22:53 10/21/13 23:03 10/21/13 23:13 10/21/13 23:23 10/21/13 23:33 10/21/13 23:43 10/21/13 23:53 10/22/13 0:03 10/22/13 0:13 10/22/13 0:23 10/22/13 0:33 10/22/13 0:43 10/22/13 0:53 10/22/13 1:03 10/22/13 1:13 10/22/13 1:23 10/22/13 1:33 10/22/13 1:43 10/22/13 1:53 10/22/13 2:03 6.53 6.47 6.40 6.30 6.30 6.27 6.19 6.14 6.08 5.95 5.96 5.88 5.84 5.81 5.73 5.62 5.61 5.54 5.49 5.44 5.36 5.34 5.28 5.26 5.22 5.15 5.10 5.08 5.03 4.98 4.92 4.89 4.83 4.82 6.42 6.28 6.28 6.23 6.19 6.14 6.09 6.03 5.97 5.92 5.88 5.83 5.78 5.73 5.67 5.63 5.59 5.55 5.52 5.48 5.44 5.41 5.36 5.32 5.29 5.26 5.24 5.20 5.17 5.14 5.12 5.09 5.05 5.02 8.50 8.49 8.48 8.43 8.47 8.46 8.44 8.43 8.42 8.37 8.37 8.36 8.35 8.34 8.33 8.32 8.32 8.32 8.31 8.30 8.31 8.30 8.30 8.30 8.29 8.29 8.29 8.26 8.26 8.25 8.27 8.25 8.25 8.25 11/8/2013 18:46 11/8/2013 18:56 11/8/2013 19:06 11/8/2013 19:16 11/8/2013 19:26 11/8/2013 19:36 11/8/2013 19:46 11/8/2013 19:56 11/8/2013 20:06 11/8/2013 20:16 11/8/2013 20:26 11/8/2013 20:36 11/8/2013 20:46 11/8/2013 20:56 11/8/2013 21:06 11/8/2013 21:16 11/8/2013 21:26 11/8/2013 21:36 11/8/2013 21:46 11/8/2013 21:56 11/8/2013 22:06 11/8/2013 22:16 11/8/2013 22:26 11/8/2013 22:36 11/8/2013 22:46 11/8/2013 22:56 11/8/2013 23:06 11/8/2013 23:16 11/8/2013 23:26 11/8/2013 23:36 11/8/2013 23:46 11/8/2013 23:56 11/9/2013 0:06 11/9/2013 0:16 5.21 5.26 5.15 5.05 4.97 4.96 4.95 4.92 4.97 4.86 4.77 4.71 4.56 4.54 4.36 4.39 4.39 3.90 3.38 3.42 3.68 3.96 3.89 4.20 4.00 4.04 4.00 4.00 3.98 4.04 4.04 4.02 4.03 4.02 120 6.13 6.07 6.03 5.97 5.93 5.88 5.84 5.79 5.74 5.69 5.64 5.60 5.55 5.50 5.48 5.44 5.41 5.33 5.33 5.29 5.26 5.23 5.21 5.19 5.15 5.14 5.11 5.08 5.05 5.03 5.02 5.00 4.99 4.97 8.64 8.63 8.62 8.61 8.61 8.59 8.59 8.58 8.58 8.57 8.56 8.56 8.55 8.47 8.44 8.47 8.49 8.50 8.46 8.52 8.51 8.51 8.50 8.41 8.39 8.48 8.46 8.48 8.48 8.48 8.47 8.48 8.48 8.48 12/13/2013 18:54 12/13/2013 19:04 12/13/2013 19:14 12/13/2013 19:24 12/13/2013 19:34 12/13/2013 19:44 12/13/2013 19:54 12/13/2013 20:04 12/13/2013 20:14 12/13/2013 20:24 12/13/2013 20:34 12/13/2013 20:44 12/13/2013 20:54 12/13/2013 21:04 12/13/2013 21:14 12/13/2013 21:24 12/13/2013 21:34 12/13/2013 21:44 12/13/2013 21:54 12/13/2013 22:04 12/13/2013 22:14 12/13/2013 22:24 12/13/2013 22:34 12/13/2013 22:44 12/13/2013 22:54 12/13/2013 23:04 12/13/2013 23:14 12/13/2013 23:24 12/13/2013 23:34 12/13/2013 23:44 12/13/2013 23:54 12/14/2013 0:04 12/14/2013 0:14 12/14/2013 0:24 5.16 5.11 5.11 5.05 4.97 4.96 4.93 4.86 4.79 4.67 4.52 4.52 4.60 4.51 4.49 4.46 4.42 4.58 4.48 4.38 4.26 4.19 4.13 4.06 4.01 3.94 3.89 3.84 3.82 3.76 3.74 3.69 3.64 3.65 4.77 4.71 5.38 5.36 5.33 5.27 5.20 5.20 5.17 3.00 3.01 3.13 3.20 3.27 3.32 3.35 3.38 3.34 3.36 3.38 3.42 3.42 3.40 3.38 3.39 3.41 3.38 3.37 3.36 3.33 3.32 3.32 3.31 3.29 8.62 8.59 8.59 8.57 8.56 8.63 8.59 8.56 8.49 8.41 8.37 8.35 8.34 8.32 8.33 8.31 8.28 8.26 8.24 8.22 8.21 8.19 8.17 8.16 8.12 8.11 8.11 8.30 8.42 8.37 8.42 8.39 8.41 8.39 10/22/13 2:13 10/22/13 2:23 10/22/13 2:33 10/22/13 2:43 10/22/13 2:53 10/22/13 3:03 10/22/13 3:13 10/22/13 3:23 10/22/13 3:33 10/22/13 3:43 10/22/13 3:53 10/22/13 4:03 10/22/13 4:13 10/22/13 4:23 10/22/13 4:33 10/22/13 4:43 10/22/13 4:53 10/22/13 5:03 10/22/13 5:13 10/22/13 5:23 10/22/13 5:33 10/22/13 5:43 10/22/13 5:53 10/22/13 6:03 10/22/13 6:13 10/22/13 6:23 10/22/13 6:33 10/22/13 6:43 10/22/13 6:53 10/22/13 7:03 10/22/13 7:13 10/22/13 7:23 10/22/13 7:33 10/22/13 7:43 4.76 4.71 4.69 4.65 4.58 4.58 4.56 4.52 4.54 4.50 4.48 4.47 4.41 4.36 4.36 4.34 4.31 4.28 4.26 4.24 4.21 4.22 4.22 4.22 4.20 4.23 4.23 4.25 4.24 4.21 4.22 4.18 4.20 4.18 5.00 4.98 4.95 4.93 4.91 4.89 4.87 4.86 4.84 4.83 4.81 4.80 4.78 4.75 4.74 4.73 4.72 4.71 4.70 4.69 4.69 4.68 4.67 4.66 4.65 4.65 4.64 4.63 4.62 4.62 4.61 4.61 4.60 4.60 8.24 8.24 8.24 8.23 8.23 8.22 8.21 8.22 8.22 8.22 8.21 8.21 8.21 8.21 8.21 8.21 8.21 8.21 8.21 8.21 8.20 8.20 8.20 8.20 8.20 8.19 8.20 8.20 8.20 8.19 8.20 8.20 8.20 8.20 11/9/2013 0:26 11/9/2013 0:36 11/9/2013 0:46 11/9/2013 0:56 11/9/2013 1:06 11/9/2013 1:16 11/9/2013 1:26 11/9/2013 1:36 11/9/2013 1:46 11/9/2013 1:56 11/9/2013 2:06 11/9/2013 2:16 11/9/2013 2:26 11/9/2013 2:36 11/9/2013 2:46 11/9/2013 2:56 11/9/2013 3:06 11/9/2013 3:16 11/9/2013 3:26 11/9/2013 3:36 11/9/2013 3:46 11/9/2013 3:56 11/9/2013 4:06 11/9/2013 4:16 11/9/2013 4:26 11/9/2013 4:36 11/9/2013 4:46 11/9/2013 4:56 11/9/2013 5:06 11/9/2013 5:16 11/9/2013 5:26 11/9/2013 5:36 11/9/2013 5:46 11/9/2013 5:56 3.78 3.74 3.52 3.78 3.66 3.60 3.62 3.62 3.55 3.52 3.35 3.29 3.29 3.32 3.29 3.29 3.33 3.32 3.31 3.14 3.04 3.16 3.19 3.05 2.73 3.10 3.05 2.93 2.69 2.45 3.10 2.96 3.05 2.73 121 4.96 4.94 4.93 4.92 4.90 4.89 4.87 4.86 4.85 4.84 4.78 4.74 4.70 4.66 4.67 4.65 4.66 4.66 4.62 4.62 4.61 4.55 4.52 4.57 4.52 4.49 4.49 4.41 4.47 4.47 4.40 4.47 4.39 4.46 8.47 8.47 8.46 8.45 8.46 8.46 8.46 8.45 8.45 8.45 8.45 8.45 8.45 8.44 8.44 8.44 8.43 8.42 8.40 8.37 8.35 8.36 8.37 8.35 8.36 8.40 8.41 8.41 8.40 8.38 8.37 8.35 8.39 8.41 12/14/2013 0:34 12/14/2013 0:44 12/14/2013 0:54 12/14/2013 1:04 12/14/2013 1:14 12/14/2013 1:24 12/14/2013 1:34 12/14/2013 1:44 12/14/2013 1:54 12/14/2013 2:04 12/14/2013 2:14 12/14/2013 2:24 12/14/2013 2:34 12/14/2013 2:44 12/14/2013 2:54 12/14/2013 3:04 12/14/2013 3:14 12/14/2013 3:24 12/14/2013 3:34 12/14/2013 3:44 12/14/2013 3:54 12/14/2013 4:04 12/14/2013 4:14 12/14/2013 4:24 12/14/2013 4:34 12/14/2013 4:44 12/14/2013 4:54 12/14/2013 5:04 12/14/2013 5:14 12/14/2013 5:24 12/14/2013 5:34 12/14/2013 5:44 12/14/2013 5:54 12/14/2013 6:04 3.72 3.57 3.69 3.59 3.57 3.69 3.45 3.54 3.59 3.50 3.36 3.32 3.62 3.45 3.45 3.47 3.40 3.38 3.49 3.39 3.10 3.27 3.31 3.17 3.63 3.43 3.14 3.29 3.22 3.34 3.22 3.26 3.25 3.14 3.27 3.27 3.27 3.27 3.27 3.29 3.33 3.34 3.33 3.33 3.33 3.33 3.34 3.38 3.40 3.39 4.25 4.28 4.29 4.28 4.26 4.25 4.26 4.27 4.21 4.21 4.22 4.22 4.20 4.19 4.18 4.19 4.18 4.18 8.32 8.24 8.03 8.02 8.04 8.07 8.24 8.25 8.23 8.27 8.23 8.20 8.22 8.27 8.24 8.23 8.16 8.32 8.33 7.99 8.00 8.20 8.10 7.99 8.12 8.11 8.10 8.14 8.07 7.93 7.96 8.00 8.07 8.04 10/22/13 7:53 10/22/13 8:03 10/22/13 8:13 10/22/13 8:23 10/22/13 8:33 10/22/13 8:43 10/22/13 8:53 10/22/13 9:03 10/22/13 9:13 10/22/13 9:23 10/22/13 9:33 10/22/13 9:43 10/22/13 9:53 10/22/13 10:03 10/22/13 10:13 10/22/13 10:23 10/22/13 10:33 10/22/13 10:43 10/22/13 10:53 10/22/13 11:03 10/22/13 11:13 10/22/13 11:23 10/22/13 11:33 10/22/13 11:43 10/22/13 11:53 10/22/13 12:03 10/22/13 12:13 10/22/13 12:23 10/22/13 12:33 10/22/13 12:43 10/22/13 12:53 10/22/13 13:03 10/22/13 13:13 10/22/13 13:23 4.12 4.11 4.12 4.11 4.13 4.14 4.17 4.23 4.24 4.28 4.32 4.41 4.38 4.41 4.42 4.47 4.50 4.55 4.61 4.65 4.69 4.73 4.82 4.92 4.99 5.12 5.21 5.27 5.29 5.38 5.45 5.53 5.60 5.68 4.59 4.59 4.60 4.60 4.61 4.64 4.65 4.68 4.72 4.76 4.83 4.87 4.92 4.96 5.00 5.04 5.08 5.11 5.16 5.21 5.25 5.32 5.42 5.49 5.58 5.68 5.77 5.84 5.91 6.03 6.07 6.15 6.23 6.32 8.21 8.18 8.22 8.21 8.21 8.22 8.22 8.23 8.23 8.23 8.23 8.24 8.25 8.25 8.25 8.25 8.25 8.25 8.26 8.26 8.26 8.27 8.28 8.29 8.30 8.30 8.31 8.32 8.32 8.33 8.34 8.34 8.35 8.36 11/9/2013 6:06 11/9/2013 6:16 11/9/2013 6:26 11/9/2013 6:36 11/9/2013 6:46 11/9/2013 6:56 11/9/2013 7:06 11/9/2013 7:16 11/9/2013 7:26 11/9/2013 7:36 11/9/2013 7:46 11/9/2013 7:56 11/9/2013 8:06 11/9/2013 8:16 11/9/2013 8:26 11/9/2013 8:36 11/9/2013 8:46 11/9/2013 8:56 11/9/2013 9:06 11/9/2013 9:16 11/9/2013 9:26 11/9/2013 9:36 11/9/2013 9:46 11/9/2013 9:56 11/9/2013 10:06 11/9/2013 10:16 11/9/2013 10:26 11/9/2013 10:36 11/9/2013 10:46 11/9/2013 10:56 11/9/2013 11:06 11/9/2013 11:16 11/9/2013 11:26 11/9/2013 11:36 3.25 3.25 3.48 3.51 3.41 3.35 3.37 3.36 3.33 3.30 3.28 3.32 3.41 3.42 3.43 3.46 3.45 3.49 3.52 3.57 3.61 3.58 3.72 3.68 3.68 3.67 3.70 3.68 3.78 4.31 4.34 5.03 4.68 4.65 122 4.44 4.19 4.66 4.66 4.66 4.65 4.64 4.61 4.62 4.63 4.63 4.64 4.65 4.67 4.63 4.63 4.69 4.71 4.76 4.79 4.85 4.89 4.92 4.96 5.00 5.03 5.10 5.14 5.18 5.23 5.28 5.34 5.40 5.46 8.40 8.44 8.44 8.44 8.44 8.44 8.44 8.44 8.44 8.44 8.44 8.44 8.44 8.44 8.34 8.30 8.37 8.43 8.42 8.44 8.45 8.45 8.46 8.46 8.47 8.48 8.48 8.48 8.48 8.45 8.48 8.48 8.47 8.49 12/14/2013 6:14 12/14/2013 6:24 12/14/2013 6:34 12/14/2013 6:44 12/14/2013 6:54 12/14/2013 7:04 12/14/2013 7:14 12/14/2013 7:24 12/14/2013 7:34 12/14/2013 7:44 12/14/2013 7:54 12/14/2013 8:04 12/14/2013 8:14 12/14/2013 8:24 12/14/2013 8:34 12/14/2013 8:44 12/14/2013 8:54 12/14/2013 9:04 12/14/2013 9:14 12/14/2013 9:24 12/14/2013 9:34 12/14/2013 9:44 12/14/2013 9:54 12/14/2013 10:04 12/14/2013 10:14 12/14/2013 10:24 12/14/2013 10:34 12/14/2013 10:44 12/14/2013 10:54 12/14/2013 11:04 12/14/2013 11:14 12/14/2013 11:24 12/14/2013 11:34 12/14/2013 11:44 3.25 3.12 2.89 3.04 2.79 2.91 3.04 3.04 3.13 3.13 3.04 2.96 3.05 3.13 2.90 3.36 3.01 3.04 3.26 3.08 3.11 3.16 3.03 3.14 3.24 3.21 3.13 3.29 3.28 3.32 3.33 3.36 3.40 3.96 4.18 4.17 4.15 4.17 4.18 4.19 4.18 4.17 4.17 4.17 4.17 4.17 4.18 4.19 4.22 4.23 4.27 4.30 4.31 4.36 4.41 4.45 4.51 4.53 4.57 4.60 4.62 4.65 4.69 4.77 4.88 4.95 4.93 4.95 7.88 8.20 8.19 8.24 8.22 8.18 8.22 8.21 8.22 8.19 8.20 7.99 8.00 7.93 7.99 8.06 8.12 8.13 8.21 8.16 8.13 8.23 8.33 8.26 8.21 8.25 8.23 8.19 8.23 8.21 8.20 8.10 8.06 8.19 10/22/13 13:33 10/22/13 13:43 10/22/13 13:53 10/22/13 14:03 10/22/13 14:13 10/22/13 14:23 10/22/13 14:33 10/22/13 14:43 10/22/13 14:53 10/22/13 15:03 10/22/13 15:13 10/22/13 15:23 10/22/13 15:33 10/22/13 15:43 10/22/13 15:53 10/22/13 16:03 10/22/13 16:13 10/22/13 16:23 10/22/13 16:33 10/22/13 16:43 10/22/13 16:53 10/22/13 17:03 10/22/13 17:13 10/22/13 17:23 10/22/13 17:33 10/22/13 17:43 10/22/13 17:53 10/22/13 18:03 10/22/13 18:13 10/22/13 18:23 10/22/13 18:33 10/22/13 18:43 10/22/13 18:53 10/22/13 19:03 5.76 5.85 5.94 6.02 6.09 6.16 6.27 6.36 6.44 6.45 6.51 6.52 6.53 6.55 6.56 6.57 6.58 6.58 6.61 6.60 6.60 6.60 6.60 6.61 6.62 6.62 6.58 6.54 6.52 6.48 6.41 6.37 6.31 6.26 6.41 6.49 6.59 6.69 6.79 6.86 6.95 7.04 7.10 7.15 7.20 7.23 7.24 7.26 7.27 7.29 7.30 7.30 7.31 7.31 7.31 7.31 7.31 7.31 7.30 7.30 7.27 7.24 7.19 7.16 7.11 7.05 7.01 6.95 8.37 8.37 8.38 8.40 8.41 8.41 8.43 8.44 8.44 8.45 8.46 8.47 8.49 8.49 8.50 8.51 8.51 8.52 8.52 8.53 8.53 8.54 8.55 8.56 8.55 8.54 8.54 8.53 8.53 8.53 8.53 8.54 8.53 8.52 11/9/2013 11:46 11/9/2013 11:56 11/9/2013 12:06 11/9/2013 12:16 11/9/2013 12:26 11/9/2013 12:36 11/9/2013 12:46 11/9/2013 12:56 11/9/2013 13:06 11/9/2013 18:29 11/9/2013 18:39 11/9/2013 18:49 11/9/2013 18:59 11/9/2013 19:09 11/9/2013 19:19 11/9/2013 19:29 11/9/2013 19:39 11/9/2013 19:49 11/9/2013 19:59 11/9/2013 20:09 11/9/2013 20:19 11/9/2013 20:29 11/9/2013 20:39 11/9/2013 20:49 11/9/2013 20:59 11/9/2013 21:09 11/9/2013 21:19 11/9/2013 21:29 11/9/2013 21:39 11/9/2013 21:49 11/9/2013 21:59 11/9/2013 22:09 11/9/2013 22:19 11/9/2013 22:29 5.90 5.47 4.31 4.76 4.37 4.43 4.41 4.48 4.56 7.98 5.94 5.67 5.54 5.31 5.30 5.23 5.16 5.07 4.97 4.91 4.81 4.74 4.66 4.59 4.53 4.49 4.45 4.03 4.22 4.22 4.17 3.96 3.93 3.97 123 5.51 5.57 5.62 5.68 5.76 5.82 5.88 5.94 5.99 6.40 6.28 6.28 6.15 6.09 6.02 5.95 5.89 5.84 5.78 5.75 5.69 5.63 5.60 5.56 5.52 5.48 5.44 5.05 5.24 5.22 5.19 5.09 5.11 5.08 8.49 8.49 8.47 8.45 8.48 8.50 8.50 8.51 8.51 8.57 8.42 8.52 8.53 8.52 8.54 8.54 8.52 8.52 8.50 8.50 8.48 8.48 8.47 8.46 8.46 8.45 8.44 8.44 8.44 8.45 8.44 8.44 8.43 8.43 12/14/2013 11:54 12/14/2013 12:04 12/14/2013 12:14 12/14/2013 12:24 12/14/2013 12:34 12/14/2013 12:44 12/14/2013 12:54 12/14/2013 13:04 12/14/2013 13:14 12/14/2013 13:24 12/14/2013 13:34 12/14/2013 13:44 12/14/2013 13:54 12/14/2013 14:04 12/14/2013 14:14 12/14/2013 14:24 12/14/2013 14:34 12/14/2013 14:44 12/14/2013 14:54 12/14/2013 15:04 12/14/2013 15:14 12/14/2013 15:24 12/14/2013 15:34 12/14/2013 15:44 12/14/2013 15:54 12/14/2013 16:04 12/14/2013 16:14 12/14/2013 16:24 12/14/2013 16:34 12/14/2013 16:44 12/14/2013 16:54 12/14/2013 17:04 12/14/2013 17:14 12/14/2013 17:24 3.51 3.55 3.49 3.65 3.77 3.67 3.77 3.70 3.71 3.81 3.88 3.89 3.84 4.01 3.97 4.13 3.94 3.97 3.93 4.00 3.80 3.99 3.96 4.08 3.99 3.92 4.01 4.02 3.84 3.90 4.00 3.94 3.90 3.91 4.91 5.00 5.22 5.29 5.37 5.34 5.28 5.34 5.41 5.54 5.58 5.61 5.61 5.71 5.56 5.67 5.77 5.70 5.51 5.57 5.65 5.67 5.61 5.60 5.51 5.52 5.50 5.47 5.43 5.41 5.40 5.33 5.31 5.27 8.12 8.13 8.22 8.49 8.39 8.45 8.40 8.40 8.39 8.39 8.41 8.35 8.32 8.35 8.32 8.38 8.43 8.42 8.36 8.38 8.33 8.38 8.41 8.41 8.35 8.38 8.36 8.40 8.40 8.41 8.36 8.37 8.36 8.37 10/22/13 19:13 10/22/13 19:23 10/22/13 19:33 10/22/13 19:43 10/22/13 19:53 10/22/13 20:03 10/22/13 20:13 10/22/13 20:23 10/22/13 20:33 10/22/13 20:43 10/22/13 20:53 10/22/13 21:03 10/22/13 21:13 10/22/13 21:23 10/22/13 21:33 10/22/13 21:43 10/22/13 21:53 10/22/13 22:03 10/22/13 22:13 10/22/13 22:23 10/22/13 22:33 10/22/13 22:43 10/22/13 22:53 10/22/13 23:03 10/22/13 23:13 10/22/13 23:23 10/22/13 23:33 10/22/13 23:43 10/22/13 23:53 10/23/13 0:03 10/23/13 0:13 10/23/13 0:23 10/23/13 0:33 10/23/13 0:43 6.21 6.09 6.01 5.93 5.85 5.88 5.82 5.76 5.71 5.66 5.61 5.56 5.51 5.47 5.43 5.38 5.33 5.30 5.26 5.22 5.18 5.13 5.10 5.06 5.17 5.12 5.07 5.03 4.96 4.91 4.86 4.82 4.80 4.75 6.89 6.83 6.75 6.70 6.63 6.56 6.51 6.46 6.41 6.36 6.30 6.24 6.19 6.14 6.09 6.03 5.97 5.93 5.89 5.84 5.80 5.75 5.71 5.66 5.62 5.58 5.55 5.51 5.48 5.45 5.42 5.37 5.34 5.31 8.53 8.52 8.53 8.50 8.49 8.48 8.47 8.46 8.45 8.44 8.43 8.41 8.40 8.39 8.38 8.36 8.35 8.34 8.33 8.32 8.32 8.31 8.31 8.30 8.30 8.29 8.29 8.28 8.27 8.26 8.26 8.25 8.24 8.24 11/9/2013 22:39 11/9/2013 22:49 11/9/2013 22:59 11/9/2013 23:09 11/9/2013 23:19 11/9/2013 23:29 11/9/2013 23:39 11/9/2013 23:49 11/9/2013 23:59 11/10/2013 0:09 11/10/2013 0:19 11/10/2013 0:29 11/10/2013 0:39 11/10/2013 0:49 11/10/2013 0:59 11/10/2013 1:09 11/10/2013 1:19 11/10/2013 1:29 11/10/2013 1:39 11/10/2013 1:49 11/10/2013 1:59 11/10/2013 2:09 11/10/2013 2:19 11/10/2013 2:29 11/10/2013 2:39 11/10/2013 2:49 11/10/2013 2:59 11/10/2013 3:09 11/10/2013 3:19 11/10/2013 3:29 11/10/2013 3:39 11/10/2013 3:49 11/10/2013 3:59 11/10/2013 4:09 3.82 3.81 3.79 3.98 3.76 3.69 3.75 3.53 3.59 3.57 4.10 3.95 3.90 3.77 3.74 3.76 3.71 3.70 3.67 3.66 3.66 3.64 3.63 3.63 3.61 3.60 3.58 3.57 3.56 3.54 3.55 3.50 3.51 3.52 124 5.06 4.97 4.95 4.93 4.90 4.84 4.86 4.81 4.76 4.77 4.95 4.92 4.89 4.78 4.68 4.76 4.71 4.66 4.76 4.69 4.65 4.69 4.67 4.67 4.66 4.68 4.65 4.72 4.71 4.70 4.70 4.69 4.68 4.68 8.43 8.43 8.42 8.42 8.42 8.42 8.41 8.41 8.41 8.41 8.40 8.38 8.38 8.37 8.36 8.36 8.36 8.35 8.35 8.34 8.34 8.35 8.34 8.34 8.34 8.35 8.35 8.35 8.36 8.38 8.38 8.38 8.38 8.38 12/14/2013 17:34 12/14/2013 17:44 12/14/2013 17:54 12/14/2013 18:04 12/14/2013 18:14 12/14/2013 18:24 12/14/2013 18:34 12/14/2013 18:44 12/14/2013 18:54 12/14/2013 19:04 12/14/2013 19:14 12/14/2013 19:24 12/14/2013 19:34 12/14/2013 19:44 12/14/2013 19:54 12/14/2013 20:04 12/14/2013 20:14 12/14/2013 20:24 12/14/2013 20:34 12/14/2013 20:44 12/14/2013 20:54 12/14/2013 21:04 12/14/2013 21:14 12/14/2013 21:24 12/14/2013 21:34 12/14/2013 21:44 12/14/2013 21:54 12/14/2013 22:04 12/14/2013 22:14 12/14/2013 22:24 12/14/2013 22:34 12/14/2013 22:44 12/14/2013 22:54 12/14/2013 23:04 3.70 3.70 3.68 3.69 3.69 3.61 3.59 3.56 3.52 3.53 3.45 3.44 3.41 3.37 3.33 3.32 3.27 3.24 3.23 3.20 3.16 3.14 3.10 3.07 3.04 3.02 3.00 2.99 2.96 2.95 2.92 2.90 2.90 2.88 5.24 5.21 5.18 5.15 5.13 5.10 5.07 5.02 5.00 4.96 4.93 4.89 4.86 4.83 4.80 4.77 4.74 4.70 4.68 4.65 4.62 4.60 4.57 4.55 4.53 4.51 4.48 4.47 4.46 4.43 4.41 4.37 4.36 4.36 8.30 8.34 8.37 8.47 8.50 8.54 8.54 8.53 8.56 8.53 8.53 8.53 8.51 8.50 8.48 8.46 8.44 8.43 8.42 8.40 8.39 8.37 8.36 8.33 8.34 8.33 8.32 8.31 8.33 8.34 8.33 8.31 8.34 8.33 10/23/13 0:53 10/23/13 1:03 10/23/13 1:13 10/23/13 1:23 10/23/13 1:33 10/23/13 1:43 10/23/13 1:53 10/23/13 2:03 10/23/13 2:13 10/23/13 2:23 10/23/13 2:33 10/23/13 2:43 10/23/13 2:53 10/23/13 3:03 10/23/13 3:13 10/23/13 3:23 4.72 4.69 4.66 4.64 4.62 4.58 4.56 4.58 4.49 4.44 4.41 4.38 4.36 4.33 4.30 4.30 5.27 5.24 5.21 5.19 5.16 5.13 5.10 5.06 5.02 4.99 4.95 4.92 4.89 4.87 4.83 4.81 8.23 8.23 8.22 8.20 8.20 8.19 8.19 8.19 8.19 8.20 8.19 8.18 8.19 8.20 8.18 8.19 11/10/2013 4:19 11/10/2013 4:29 11/10/2013 4:39 11/10/2013 4:49 11/10/2013 4:59 11/10/2013 5:09 11/10/2013 5:19 11/10/2013 5:29 11/10/2013 5:39 11/10/2013 5:49 11/10/2013 5:59 11/10/2013 6:09 11/10/2013 6:19 11/10/2013 6:29 11/10/2013 6:39 11/10/2013 6:49 3.50 3.48 3.49 3.46 3.49 3.52 3.25 3.30 3.25 3.28 3.21 3.20 3.24 3.27 3.22 3.40 125 4.68 4.67 4.67 4.66 4.65 4.65 4.63 4.64 4.63 4.62 4.62 4.61 4.60 4.60 4.59 4.59 8.30 8.29 8.35 8.35 8.30 8.34 8.36 8.35 8.38 8.38 8.40 8.39 8.39 8.39 8.39 8.44 12/14/2013 23:14 12/14/2013 23:24 12/14/2013 23:34 12/14/2013 23:44 12/14/2013 23:54 12/15/2013 0:04 12/15/2013 0:14 12/15/2013 0:24 12/15/2013 0:34 12/15/2013 0:44 12/15/2013 0:54 12/15/2013 1:04 12/15/2013 1:14 12/15/2013 1:24 12/15/2013 1:34 12/15/2013 1:44 2.88 2.87 2.85 2.84 2.84 2.82 2.80 2.79 2.79 2.80 2.79 2.77 2.78 2.77 2.76 2.76 4.34 4.32 4.31 4.30 4.29 4.29 4.27 4.26 4.26 4.25 4.25 4.24 4.24 4.23 4.22 4.23 8.33 8.34 8.34 8.32 8.33 8.31 8.27 8.23 8.26 8.24 8.23 8.21 8.19 8.21 8.20 8.21 Appendix 3. Date Jan Jan Jan Jan Jan Feb Feb Feb Feb Feb Feb Feb Feb Feb Feb Feb Feb Feb Feb Feb Mar Mar Mar Mar Mar Mar Mar Mar Mar Mar Mar Mar Mar Mar Mar Apr May May May May Jun Jun Jun Jun Jul Algae Dry Mass (g) 0.1851 0.1563 0.1825 0.1481 0.1711 0.2865 0.1167 0.0968 0.4371 0.2654 0.1758 0.303 0.3412 0.1945 0.1677 0.1093 0.1315 0.1167 0.1709 0.158 0.2843 0.058 0.4075 0.5052 0.3781 0.4242 0.6822 0.4225 0.6113 0.4657 0.6931 0.2703 0.4542 0.5557 0.2101 0.2627 0.1786 0.281 0.2452 0.3167 0.1022 0.0398 0.0559 0.0116 0.1456 126 Jul Jul Jul Aug Aug Aug Aug Aug Sep Sep Sep Sep Sep Oct Oct Oct Oct Oct Nov Nov Nov Nov Nov Dec Dec Dec Dec Dec 0.0851 0.1456 0.2073 0.0308 0.022 0.1392 0.2164 0.0599 0.2026 0.1339 0.1778 0.1317 0.298 0.0808 0.1459 0.2594 0.2875 0.2747 0.0955 0.2532 0.2176 0.2566 0.0464 0.4601 0.3015 0.2218 0.4556 0.3306 127 Appendix 4. Time 0:00 6:00 9:00 12:00 15:00 18:00 0:00 6:00 9:00 12:00 15:00 18:00 0:00 6:00 9:00 12:00 15:00 18:00 January 2.256164 2.107671 2.121442 3.20 3.49 3.53 3.38 3.05 3.37 3.01 2.94 2.91 2.76 3.12 3.069841 2.356985 2.380766 February 3.10 3.55 3.28 3.30 2.94 3.14 3.52 3.44 3.29 3.27 3.24 3.44 3.63 3.40 3.25 3.52 3.19 3.38 March April 5.39 18.54 5.16 5.60 4.76 5.10 4.65 5.77 4.47 5.16 4.84 5.11 3.55 4.85 3.49 4.60 3.38 4.41 3.28 4.38 3.48 4.23 3.52 4.09 3.85 3.35 3.34 3.43 3.45 3.67 May Water Column TOC, mg L-1 June July August September 4.14 3.97 13.60 3.47 8.15 3.06 13.28 8.65 8.52 4.00 22.29 10.12 3.48 16.44 3.36 7.26 3.81 4.95 3.05 4.71 4.48 4.08 3.88 4.35 3.89 4.16 3.68 4.05 3.94 4.11 3.7465 4.09 17.09 4.16 3.69 3.96 3.79 4.30 3.84 3.78 3.66 3.70 3.71 3.78 3.63 3.67 3.53 3.48 3.42 3.49 128 4.14 3.73 4.07 4.52 3.65 3.48 3.29 3.45 3.35 3.92 3.64 4.08 4.14 3.97 3.45 3.81 7.31 8.20 5.28 10.03 5.69 3.64 4.46 4.50 5.03 3.86 4.25 3.96 4.58 4.40 4.29 5.19 4.53 3.59 October 3.80 3.64 3.26 3.06 3.80 3.59 3.61 3.74 3.82 3.29 3.61 3.45 3.90 4.26 4.19 4.17 November 6.77 4.99 4.91 4.91 4.51 4.76 4.54 5.27 4.65 4.49 4.55 4.21 4.04 4.18 4.72 4.11 4.21 7.34 December 4.27 3.74 3.42 3.29 4.51 4.15 4.11 3.58 3.29 3.25 4.029 3.65 3.393 3.085 3.1525 3.044 3.19 3.4595 Appendix 5. Time January February March April May 0:00 6.059749 5.06 6.73 13.90 7.367 6:00 4.82673 5.07 7.94 10.03 4.7365 9:00 3.255742 6.46 7.37 7.32 5.8575 12:00 5.10 4.10 10.30 7.78 7.59 15:00 5.62 6.12 8.67 9.14 6.717 18:00 5.03 5.48 8.75 6.18 0:00 4.59 4.55 5.78 6.36 4.858 6:00 5.33 6.94 5.27 9:00 4.11 6.04 5.13 6.16 4.19 12:00 4.06 6.20 5.26 5.90 4.0675 15:00 3.24 6.50 6.37 4.87 4.2125 18:00 6.38 6.12 5.92 4.19 4.30 0:00 3.09 5.97 8.02 4.7765 6:00 5.15 13.52 4.49 9:00 5.22 6.25 3.58 12:00 10.34631 9.36 7.10 4.592 15:00 4.702073 5.60 7.39 5.1475 18:00 6.339647 4.96 4.44 4.5845 Algal Biofilm TOC, mg L-1 June July August September October November December 5.60 5.27 8.10 5.36 8.39 5.46 4.37 3.74 5.15 5.67 5.17 10.86 4.42 4.22 4.71 5.80 4.79 10.03 4.29 4.85 6.33 4.82 5.59 4.44 8.15 4.60 3.94 4.97 4.73 5.32 13.45 8.83 4.31 3.85 4.65 4.28 9.46 6.09 5.15 3.95 5.10 4.99 3.53 5.32 4.35 4.56 3.97 5.53 4.71 5.35 3.91 4.41 3.86 3.83 4.52 3.99 5.20 3.63 4.80 4.34 4.79 4.47 4.15 5.19 3.84 5.04 3.91 4.20 4.25 4.62 5.39 4.9995 4.72 4.13 4.29 4.85 5.34 5.63 4.42 2.30 4.02 4.68 5.94 4.63 5.18 3.912 4.44 4.17 5.62 4.37 4.33 3.9185 4.34 4.14 4.24 4.13 5.25 4.82 4.016 4.38 4.16 3.87 5.12 4.52 4.80 4.5295 4.54 4.47 3.62 4.52 4.72 4.16 4.30 4.41 4.01 3.81 4.12 4.70 3.07 4.202 129 Appendix 6. Diurnal water column nitrate concentrations, mg L-1 January February March WC 0600 14.100 WC 0000 31.528 25.844 36.222 WC 0000 88.978 87.531 104.620 108.071 WC 0600 14.396 WC 0000 33.984 25.719 37.543 WC 0000 94.397 88.159 102.500 98.007 WC 0600 14.629 WC 0000 33.975 24.708 36.986 WC 0000 92.395 91.922 107.148 106.560 WC 0600 14.082 WC 0000 34.083 25.782 38.308 WC 0000 90.183 86.680 98.809 101.841 WC 0600 14.798 WC 0000 33.355 25.273 38.281 WC 0600 93.622 85.719 95.424 95.586 WC 0600 14.736 WC 0000 34.187 25.636 38.506 WC 0600 88.501 87.216 94.224 94.573 WC 0900 13.987 WC 0600 39.394 27.420 39.295 WC 0600 88.996 82.505 99.578 94.735 WC 0900 13.949 WC 0600 39.285 27.568 38.561 WC 0600 90.332 86.278 108.044 95.214 WC 0900 13.835 WC 0600 35.341 26.683 38.262 WC 0900 96.501 92.899 110.992 93.527 WC 0900 13.532 WC 0600 38.793 27.954 38.808 WC 0900 90.323 84.101 84.697 93.945 WC 0900 14.327 WC 0600 34.111 27.242 39.145 WC 0900 86.946 73.039 97.092 85.318 WC 0900 13.377 WC 0600 32.162 27.286 40.041 WC 0900 85.455 83.867 99.902 89.230 WC 1200 10.721 14.237 WC 0900 34.118 26.491 37.005 WC 1200 89.592 84.902 86.315 88.346 WC 1200 10.630 14.678 WC 0900 34.511 27.940 36.232 WC 1200 91.682 85.492 88.103 84.701 WC 1200 9.207 14.889 WC 0900 35.762 26.488 37.938 WC 1200 78.952 85.553 90.260 84.795 WC 1200 9.829 14.140 WC 0900 36.290 27.843 38.916 WC 1200 79.528 87.051 88.243 85.124 WC 1200 10.207 14.246 WC 0900 36.701 18.919 38.712 WC 1500 93.014 78.997 96.606 82.539 WC 1200 10.383 13.854 WC 0900 39.240 20.485 37.217 WC 1500 87.478 75.046 94.517 91.533 WC 1500 11.087 14.713 WC 1200 30.200 27.598 39.902 WC 1500 89.031 82.673 85.230 82.770 WC 1500 10.771 15.484 WC 1200 30.633 27.941 37.078 WC 1500 87.621 86.408 87.872 84.935 WC 1500 10.544 14.560 WC 1200 30.859 27.816 32.166 WC 1800 91.135 84.520 91.698 81.151 130 WC 1500 11.225 14.473 WC 1200 30.666 27.727 32.190 WC 1800 86.942 83.380 97.267 83.206 WC 1500 10.835 14.042 WC 1200 29.155 27.954 38.649 WC 1800 91.488 83.856 101.004 82.991 WC 1500 11.088 15.153 WC 1200 29.707 27.446 38.097 WC 1800 90.517 83.232 98.585 81.309 WC 1800 11.571 15.143 WC 1500 25.764 30.550 35.563 WC 1800 11.451 14.851 WC 1500 26.905 31.577 37.033 WC 1800 11.376 14.709 WC 1500 23.984 30.869 37.038 WC 1800 11.343 14.650 WC 1500 24.655 29.778 37.988 WC 1800 11.284 14.880 WC 1500 25.838 29.748 37.614 WC 1800 11.718 15.356 WC 1500 25.566 31.144 38.372 WC 0000 12.336 14.955 WC 1800 24.005 32.278 37.191 WC 0000 12.104 15.003 WC 1800 24.913 32.044 39.919 WC 0000 11.436 14.000 WC 1800 22.980 31.380 38.809 WC 0000 11.885 15.269 WC 1800 24.638 32.325 35.386 WC 0000 11.836 14.679 WC 1800 24.966 33.080 35.663 WC 0000 12.308 14.899 WC 1800 24.853 32.909 Appendix 6. (continued) WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0000 0000 0600 0600 April 16.613 14.164 19.261 20.195 18.182 18.212 20.473 20.443 May 23.941 25.001 28.248 28.979 30.57 30.681 30.696 31.29 WC WC WC WC WC WC WC WC _0000 _0000 _0000 _0000 _0000 _0000 _0000 _0000 13.418 12.472 13.226 13.428 12.85 12.915 13.278 13.786 29.738 30.886 29.101 28.513 32.648 32.787 31.558 31.229 131 WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0600 0600 0600 0600 June 92.51 88.819 89.928 90.666 86.825 88.644 68.591 80.391 79.129 74.909 82.67 73.632 72.888 74.531 73.065 68.734 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 15.483 15.91 18.643 17.25 19.754 20.13 12.811 11.691 18.535 18.046 17.591 17.834 15.234 15.467 17.889 19.995 16.434 16.93 19.83 18.72 21.276 20.078 19.036 19.669 19.81 19.389 18.265 18.735 27.564 28.352 31.321 31.387 20.703 23.004 16.497 20.362 27.748 27.614 23.453 24.532 21.966 24.238 26.69 26.006 26.008 23.712 23.236 22.475 26.47 26.835 24.665 24.225 24.591 24.229 24.322 23.688 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC _0600 _0600 _0600 _0600 _0600 _0600 _0600 _0600 _0900 _0900 _0900 _0900 _0900 _0900 _0900 _0900 _1200 _1200 _1200 _1200 _1200 _1200 _1200 _1200 _1500 _1500 _1500 _1500 _1500 _1500 _1500 15.046 14.502 17.011 17.905 16.698 16.905 16.749 16.793 17.053 17.522 14.472 14.43 16.75 17.288 16.711 17.497 10.827 10.627 11.346 11.671 8.357 8.706 10.876 10.536 11.938 12.204 12.176 12.278 11.655 12.457 11.775 18.281 19.285 19.668 19.213 19.157 19.159 20.415 20.316 17.587 18.883 19.008 18.915 18.909 18.327 18.228 19.19 132 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 93.036 86.068 67.756 74.488 79.104 82.162 76.541 75.794 82.062 78.686 75.993 75.432 78.404 78.312 76.718 73.48 75.815 72.939 60.548 74.358 70.409 71.878 67.477 68.074 70.112 68.766 69.139 68.771 69.064 70.889 67.923 68.506 WC WC WC WC WC WC WC WC WC _1500 _1800 _1800 _1800 _1800 _1800 _1800 _1800 _1800 11.717 28.075 28.3 29.063 28.217 28.407 28.238 29.266 30.332 20.793 20.069 20.281 21.73 19.712 20.784 20.831 20.472 Appendix 6. (continued) WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 July 64.046 65.402 62.416 65.459 72.979 73.773 75.206 70.835 75.958 72.542 70.22 72.586 79.776 77.726 76.807 76.018 74.84 50.977 53.892 53.143 55.78 61.235 62.769 60.762 65.342 81.15 64.914 83.636 77.652 74.555 74.846 77.261 73.152 59.405 46.181 49.002 45.841 46.208 53.568 58.058 50.055 58.711 61.194 60.627 61.748 60.97 39.573 43.129 44.617 51.208 56.285 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 August 33.244 27.963 31.103 31.477 31.908 31.805 26.722 27.394 31.376 30.587 31.637 34.118 29.492 28.733 28.23 29.259 31.124 27.195 26.724 25.953 25.983 24.602 26.323 24.049 23.626 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 33.902 WC 133 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 September 7.877 3.21 7.946 3.92 3.259 14.419 2.968 13.611 6.065 2.101 6.149 1.262 6.918 1 6.949 1.174 10.555 12.203 10.485 13.346 11.665 13.391 11.467 12.275 7.582 2.219 7.446 1.138 7.75 12.29 8.012 12.343 11.483 17.49 3.353 3.67 8.48 8.538 8.31 8.588 9.871 9.659 6.937 7.089 5.769 5.738 6.575 6.293 6.49 6.476 5.382 WC WC WC WC WC WC WC 1500 1500 1500 1800 1800 1800 1800 69.941 73.502 72.906 70.114 67.684 66.109 65.897 60.227 69.389 70.104 53.28 56.484 59.581 58.425 53.959 44.894 48.886 40.848 45.436 38.323 44.324 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 29.347 30.598 30.378 28.428 27.96 26.977 28.203 29.874 28.213 26.68 27.891 28.275 28.308 25.079 26.494 27.115 29.536 28.966 30.292 28.274 32.185 29.71 29.214 28.396 30.408 27.222 28.909 30.312 30.621 26.97 28.875 29.954 29.945 30.617 27.926 30.173 31.849 32.241 42.853 45.421 43.931 46.328 44.368 43.575 41.718 43.589 43.051 42.474 37.418 33.404 36.807 36.342 33.145 31.747 35.275 34.945 39.131 39.243 38.633 37.795 35.351 32.592 134 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 10.775 6.387 6.485 7.081 6.801 8.816 8.177 8.957 8.935 12.134 11.692 8.712 8.122 7.99 8.632 8.295 8.663 6.355 6.336 7.338 7.314 6.673 6.495 9.835 10.208 10.563 10.427 9.718 7.187 3.432 4.005 16.29 15.075 14.458 12.966 13.11 22.761 23.938 5.08 6.272 7.254 8.892 17.971 18.741 23.445 23.966 23.162 24.479 14.686 14.238 21.89 22.93 22.438 21.983 0.855 0.875 19.239 17.001 21.141 23.318 13.746 13.483 5.052 1.11 1.172 5.14 5.179 5.316 5.327 5.661 4.109 5.553 5.733 5.659 5.253 2.295 2.241 1.573 1.65 4.759 4.656 1.983 1.955 0.353 0.507 3.041 2.998 1.38 1.411 2.125 2.024 0.767 0.721 Appendix 6. (continued) WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 October 37.003 37.830 38.180 37.537 36.690 34.571 35.362 37.509 23.451 23.933 22.480 21.791 39.203 79.701 79.108 32.137 35.671 43.208 46.021 44.578 47.469 60.708 61.103 31.932 30.148 35.953 36.941 65.881 53.307 70.844 63.273 61.358 68.185 57.433 64.211 67.790 66.068 67.716 62.555 64.273 66.425 45.464 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 November 18.453 31.000 18.108 31.636 20.217 18.978 19.333 19.444 24.966 20.909 24.608 21.275 15.315 21.440 16.128 22.305 24.696 33.858 26.006 35.694 18.299 22.433 18.306 22.978 26.680 35.180 25.855 34.268 25.870 34.572 25.714 33.174 16.124 18.969 16.012 20.269 12.757 21.419 13.177 22.051 24.498 19.319 23.678 24.102 24.038 28.181 25.088 28.287 21.604 34.491 21.393 33.419 17.921 26.637 17.818 25.307 19.601 24.748 135 27.522 28.331 25.833 25.847 37.398 37.188 29.453 29.377 26.747 26.151 33.510 34.359 39.075 40.162 35.352 33.937 15.318 15.164 17.768 18.705 26.649 26.636 19.987 19.206 21.902 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 23.685 WC 24.373 WC 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 December 3.090 3.545 3.427 3.653 3.245 3.853 3.841 4.452 3.980 4.810 3.631 5.028 3.794 5.291 3.081 5.292 2.779 2.480 2.896 2.673 3.009 2.630 2.893 2.928 3.034 3.089 2.967 3.207 2.972 3.465 2.596 3.431 2.972 0.546 2.478 0.524 3.044 0.465 2.985 0.561 3.013 0.552 3.155 0.541 3.101 0.495 2.606 0.456 2.725 0.455 2.547 0.378 2.577 0.388 2.517 0.423 2.741 0.407 11.632 11.943 11.931 11.017 4.304 9.972 10.009 9.223 9.398 8.924 9.155 9.078 9.103 9.386 0.187 8.796 8.707 8.980 9.364 8.432 8.693 9.792 9.660 8.240 7.950 8.231 8.106 8.225 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 41.585 26.869 25.926 25.883 26.035 34.744 34.981 37.213 38.515 28.448 28.660 34.706 34.181 32.030 33.781 20.439 20.296 35.630 36.716 48.026 72.342 76.584 62.904 58.969 69.321 67.876 67.462 65.954 55.706 68.968 63.187 54.950 77.047 69.914 44.870 44.438 66.422 67.569 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 18.723 17.902 16.365 21.274 20.945 14.394 12.520 15.755 15.936 16.221 16.954 17.246 17.227 22.860 19.413 16.876 16.453 13.325 11.405 24.212 19.470 20.045 29.933 30.253 30.893 29.502 19.221 19.197 15.848 16.463 23.983 23.921 15.082 14.839 20.087 20.548 19.115 19.430 136 19.277 19.495 35.682 36.556 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 2.442 2.621 1.779 2.278 1.686 1.866 2.077 2.093 2.083 2.067 2.275 2.277 2.147 2.350 1.493 1.416 1.620 1.516 1.425 0.440 0.523 0.416 2.987 2.967 3.217 3.210 2.958 3.121 3.413 3.057 5.023 5.396 5.616 5.109 5.340 5.773 5.714 5.678 7.881 7.845 7.884 8.051 7.592 7.471 7.894 8.558 7.270 7.467 7.687 7.841 8.247 8.125 6.719 8.342 8.264 4.934 8.014 Appendix 7. Diurnal algal biofilm nitrate concentrations, mg L-1 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 January 14.726 13.953 14.158 14.555 8.584 8.469 9.442 9.696 9.585 9.524 9.136 9.315 11.163 10.808 11.135 11.355 10.856 10.534 10.135 10.091 13.229 14.022 14.098 13.291 13.077 13.029 12.416 13.335 14.179 14.659 14.411 14.322 14.235 14.167 13.970 14.780 14.165 14.258 14.914 14.051 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 February 36.116 27.377 36.065 26.743 36.286 26.671 35.424 27.243 38.099 27.970 39.559 27.185 37.819 30.315 37.914 28.409 38.424 33.941 38.052 29.106 35.813 28.433 37.664 27.586 32.763 28.179 31.910 28.126 29.300 27.832 31.062 29.152 26.482 27.085 26.116 29.894 27.137 28.611 33.857 25.176 23.729 24.466 26.052 22.970 24.215 23.910 32.170 137 47.681 46.772 47.175 47.011 49.620 47.695 46.723 46.097 50.864 45.822 47.912 47.920 47.991 49.048 45.872 49.433 46.395 46.046 28.151 31.795 45.279 44.360 47.364 46.971 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 58.984 57.780 55.451 56.387 57.852 55.894 55.286 56.451 55.709 55.110 54.653 55.293 54.010 53.102 54.773 55.047 54.010 54.563 52.467 52.498 53.777 54.503 54.897 53.362 March 55.774 54.734 54.559 54.473 52.789 52.789 51.831 51.823 54.081 44.172 51.467 52.197 51.920 50.535 51.018 52.438 50.590 51.348 49.565 51.065 51.840 51.867 50.940 51.893 42.786 41.464 46.972 46.561 44.730 44.806 43.183 45.242 46.989 43.107 40.659 41.658 40.823 41.505 41.483 40.424 39.340 40.034 40.083 41.267 38.153 39.683 40.195 41.222 47.524 47.316 48.100 49.143 47.157 47.110 46.034 47.197 50.567 47.632 48.383 48.067 45.630 46.128 43.005 41.939 44.580 43.564 44.677 45.107 45.182 45.131 41.275 43.372 Appendix 7. (continued) Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore _0:00 _0:00 _0:00 _0:00 _0:00 _0:00 _0:00 _0:00 _6:00 _6:00 _6:00 _6:00 _6:00 _6:00 _6:00 _6:00 _9:00 _9:00 _9:00 _9:00 _9:00 _9:00 _9:00 _9:00 _12:00 _12:00 _12:00 _12:00 April 17.994 18.244 17.45 17.663 18.15 18.273 18.34 18.403 17.191 16.976 15.461 16.076 16.005 16.267 16.872 16.918 16.751 15.207 15.717 15.877 16.344 15.769 16.18 15.978 15.627 16.206 15.38 15.768 14.014 13.201 17.185 16.911 13.127 13.057 16.24 15.995 16.558 16.357 15.6 15.718 13.663 14.31 15.02 14.683 14.047 13.946 14.472 14.673 14.172 14.027 15.149 14.46 15.737 15.09 15.657 15.985 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore _0000 _0000 _0000 _0000 _0000 _0000 _0000 _0000 _6:00 _6:00 _6:00 _6:00 _6:00 _6:00 _6:00 _6:00 _9:00 _9:00 _9:00 _9:00 _9:00 _9:00 _9:00 _9:00 _1200 _1200 _1200 _1200 May 12.574 12.104 15.01 15.099 17.392 17.535 17.827 17.611 17.976 18.068 18.253 18.691 17.672 18.081 17.781 18.268 18.27 17.529 17.473 17.284 June 12.816 13.247 12.942 13.191 12.999 12.921 12.508 12.53 16.555 17.715 17.118 9.152 9.122 10.719 11.319 138 28.645 29.002 28.679 28.869 28.956 28.369 25.706 26.791 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 81.2 84.004 90.701 88.71 83.26 84.061 91.05 85.847 89.575 83.789 84.861 84.05 71.797 75.242 67.141 76.242 71.867 80.913 75.78 72.835 78.201 76.637 73.814 75.069 76.668 78.005 75.194 78.731 75.549 74.316 77.154 73.198 79.648 71.816 72.391 72.95 66.648 68.199 70.303 70.086 66.695 66.231 69.479 66.316 66.449 66.638 67.497 68.935 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore _12:00 _12:00 _12:00 _12:00 _15:00 _15:00 _15:00 _15:00 _15:00 _15:00 _15:00 _15:00 _18:00 _18:00 _18:00 _18:00 _18:00 _18:00 _18:00 _18:00 15.895 16.343 16.312 16.132 15.175 16.166 15.676 15.702 15.489 15.833 15.038 15.335 17.086 16.347 16.2 15.346 15.731 15.874 15.411 15.638 13.704 13.489 14.512 14.989 14.041 13.878 9.132 9.181 14.753 14.216 15.21 15.777 13.231 12.893 13.285 14.254 12.314 12.53 13.187 13.16 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore _1200 _1200 _1200 _1200 _1500 _1500 _1500 _1500 _1500 _1500 _1500 _1500 _1800 _1800 _1800 _1800 _1800 _1800 _1800 _1800 16.253 15.107 16.413 16.516 13.409 13.175 15.029 15.367 11.356 11.58 10.122 9.442 12.097 11.795 12.26 11.997 11.938 12.36 11.874 12.287 29.311 28.027 30.81 29.24 26.891 26.823 31.58 30.72 18.26 18.92 20.552 20.436 19.556 19.166 20.767 19.837 Appendix 7. (continued) Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0600 0600 0600 July 72.947 77.423 68.75 77.198 79.064 83.449 80.9 76.256 79.463 75.549 72.497 81.542 74.332 72.81 53.968 53.279 57.007 55.504 59.878 59.143 64.997 Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0000 0000 0000 August 35.79 33.333 35.21 34.548 28.873 32.022 34.049 139 31.203 29.859 32.784 33.867 33.353 31.581 29.616 Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0000 0000 0000 September 17.339 19.285 24.676 25.169 23.526 22.792 16.279 4.966 5.111 6.952 6.715 5.05 5.468 4.533 16.122 12.466 12.76 13.154 19.701 12.783 11.64 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 89.279 91.004 92.751 93.598 89.393 92.714 97.429 94.012 99.536 72.027 73.565 77.722 91.382 76.08 77.71 73.275 77.918 76.589 92.896 74.216 72.474 77.691 83.528 81.329 82.116 77.836 72.471 69.954 51.457 64.119 61.304 69.987 70.526 73.396 64.211 65.897 63.714 67.035 64.198 60.153 57.22 57.878 56.419 55.147 54.426 50.452 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 34.941 34 35.885 35.148 33.866 30.682 30.46 29.303 29.45 30.931 32.955 32.805 31.959 34.435 33.67 35.435 36.568 32.188 31.28 34.698 33.945 32.645 32.627 33.852 33.58 34.39 33.629 37.012 35.633 35.987 35.424 140 30.784 Pore Pore Pore Pore Pore Pore Pore Pore Pore 37.178 Pore 35.139 Pore 37.055 Pore 37.041 Pore 31.963 Pore 32.8 Pore 36.539 Pore 38.262 Pore 53.742 Pore 55.163 Pore 53.334 Pore 54.794 Pore 54.738 Pore 48.502 Pore 49.632 Pore 48.984 Pore 39.947 Pore 41.537 Pore 33.555 Pore 33.271 Pore 44.59 Pore 44.025 Pore 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 12.436 23.075 21.152 22.802 23.374 24.783 23.068 20.789 21.88 15.476 13.993 22.886 23.663 21.637 20.894 23.055 21.984 23.331 24.032 20.758 21.489 20.901 21.589 21.624 22.102 23.558 24.552 25.196 24.633 25.158 25.515 4.673 9.001 8.852 8.535 8.454 8.617 8.431 6.822 6.877 10.85 10.824 9.894 9.71 5.803 5.592 5.672 5.734 12.865 12.815 12.676 12.062 13.81 13.35 14.488 13.889 7.007 6.708 11.227 11.705 13.831 13.657 12.182 9.527 9.426 9.281 9.751 9.038 8.578 9.304 7.906 7.182 8.82 14.056 8.939 6.24 14.426 6.492 6.482 6.649 11.095 12.13 11.348 6.454 6.519 5.889 5.858 4.47 4.541 5.036 6.229 4.898 5.088 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 35.602 35.604 34.126 34.256 33.391 33.344 34.517 35.952 33.394 33.197 40.884 40.188 49.033 49.683 47.253 48.533 48.851 49.156 47.614 47.983 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 25.568 25.58 17.092 16.649 22.618 22.154 24.38 23.079 24.847 24.827 12.686 12.001 7.833 8.32 8.907 8.766 9.823 10.041 4.856 4.216 2.686 2.772 3.245 3.429 3.787 3.899 3.786 3.582 5.278 4.777 Appendix 7. (continued) Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 October 35.406 34.559 34.289 34.929 34.587 34.158 33.938 33.618 46.844 43.518 44.144 45.292 40.314 36.645 39.946 36.033 44.118 46.457 41.747 40.277 48.521 43.211 43.699 44.376 41.785 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 November 24.803 31.699 25.956 30.723 26.130 30.012 25.500 32.651 26.871 30.503 26.922 29.783 25.059 23.252 28.033 24.758 25.754 25.425 25.887 26.150 24.384 31.781 24.088 32.212 19.875 27.070 20.255 27.813 25.894 32.852 24.652 33.168 24.296 33.527 141 34.014 34.499 37.764 37.889 34.341 34.172 34.278 35.007 23.295 23.746 40.409 40.651 33.739 32.602 33.347 34.277 29.237 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0600 0600 0900 December 2.228 8.012 2.202 8.061 2.142 8.305 1.996 8.418 1.783 6.617 1.695 7.321 1.564 7.590 1.121 7.761 1.967 5.226 1.929 5.355 1.962 8.676 1.606 5.629 1.307 6.051 1.309 5.702 1.956 6.038 1.312 5.778 1.350 8.776 8.641 8.139 9.720 10.645 10.706 11.642 12.514 11.147 12.102 10.148 9.942 10.598 10.794 10.172 9.862 8.818 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 37.433 39.029 32.236 33.375 37.288 39.231 38.835 39.376 30.965 33.685 23.247 24.013 32.405 31.702 33.486 31.760 26.426 26.228 27.429 26.382 35.015 35.779 35.892 35.571 40.374 28.111 28.436 49.332 44.971 44.881 46.713 46.955 44.705 39.235 38.454 45.692 42.358 43.498 42.809 43.558 45.152 46.540 43.293 45.286 48.885 47.228 44.443 35.479 34.457 39.870 39.058 38.252 42.273 43.848 40.605 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 25.332 27.975 26.851 27.164 25.632 23.040 22.112 25.781 25.493 21.396 20.863 23.338 22.267 23.756 24.891 24.151 23.974 24.888 25.436 14.173 13.879 23.835 23.124 22.728 22.524 15.859 15.810 24.677 24.272 22.137 22.214 32.996 26.981 27.840 28.052 28.987 31.546 33.827 23.531 23.961 26.216 26.435 25.515 25.673 25.421 26.461 21.755 22.194 28.767 27.853 28.633 29.151 24.368 23.251 23.998 24.987 22.774 23.056 18.824 18.580 23.188 23.035 142 29.812 30.708 29.385 39.863 39.424 29.892 29.439 24.660 22.990 35.364 33.865 22.691 24.242 29.635 26.943 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0900 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 1500 1500 1500 1500 1800 1800 1800 1800 1800 1800 1800 1800 1.317 1.257 1.430 1.479 1.104 1.112 1.118 1.104 1.184 1.593 1.336 1.141 1.339 1.196 1.209 1.472 1.620 1.474 1.459 1.501 1.248 1.134 0.960 0.673 0.611 0.567 0.568 0.507 0.518 0.637 0.967 2.261 2.517 2.475 2.804 2.955 2.822 2.611 0.200 0.163 0.216 0.207 0.190 0.185 0.162 0.161 3.408 3.468 3.569 3.523 4.075 3.756 3.892 0.006 5.912 5.954 5.977 6.352 6.271 5.337 6.297 6.277 9.256 9.429 9.786 9.759 9.829 9.472 9.013 8.773 8.206 8.905 9.540 9.247 8.978 8.489 8.290 9.527 9.105 8.951 9.214 9.026 9.201 8.978 9.251 10.080 9.856 7.781 8.255 4.635 8.640 8.268 7.394 Appendix 8. Diurnal water column phosphate concentrations, mg L-1 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC January 1200 0.018 1200 0.000 1200 0.001 1200 0.000 1200 0.001 1500 0.003 1500 0.000 1500 0.000 1500 0.002 1500 0.000 1500 0.002 1800 0.006 1800 0.001 1800 0.000 1800 0.000 1800 0.000 1800 0.000 0000 0.000 0000 0.003 0000 0.000 0000 0.002 0000 0.000 0000 0.000 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 February 4.556 0.070 3.296 0.570 1.427 1.024 1.568 1.265 2.223 0.268 2.427 0.566 1.359 0.145 1.657 0.108 3.697 0.081 2.676 0.045 1.437 0.130 1.453 0.159 0.545 0.151 0.459 0.171 2.580 0.076 2.767 0.037 4.115 2.261 4.366 1.680 3.792 0.201 3.066 0.231 1.167 0.274 0.725 0.244 0.536 0.216 0.287 0.232 0.431 0.159 0.481 0.123 0.235 0.125 0.837 0.107 1.548 0.595 2.251 2.885 4.031 5.898 5.200 3.976 5.880 5.571 5.279 4.593 2.609 2.908 3.061 3.048 3.040 3.915 3.870 2.561 3.291 3.371 3.973 2.569 1.395 0.206 3.381 4.059 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 143 March 0.029 0.069 0.038 0.037 0.136 0.065 0.007 0.082 0.005 0.015 0.030 0.011 0.005 0.031 0.036 0.001 0.067 0.028 0.092 0.049 0.079 0.058 0.003 0.025 0.023 0.033 0.040 0.029 0.045 0.011 0.012 0.013 0.064 0.011 0.049 0.021 0.039 0.055 0.039 0.038 0.004 0.079 0.025 0.029 0.014 0.041 0.065 0.024 0.031 0.028 0.046 0.046 0.029 0.005 0.032 0.035 1.370 0.037 0.014 0.001 0.003 0.006 0.040 0.002 0.033 0.033 0.015 0.057 0.042 0.034 0.014 0.028 0.009 0.022 0.002 0.039 0.020 0.035 0.051 0.828 0.008 0.212 0.148 0.166 0.005 0.182 0.377 2.658 3.137 1.674 2.612 4.660 3.597 2.707 2.996 WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC WC 0000 0000 0000 0000 0000 0000 0600 0600 0600 0600 0600 0600 0900 0900 0900 0900 0900 0900 1200 1200 1200 1200 1200 1200 1500 1500 1500 1500 April 0.090 0.053 0.011 0.051 0.006 0.062 0.034 0.035 0.025 0.030 0.014 0.022 0.042 0.044 0.037 0.069 0.011 0.016 0.061 0.066 0.041 0.048 0.017 0.006 0.053 0.048 0.055 0.045 0.031 0.015 0.015 0.046 0.017 0.018 0.037 0.023 0.009 0.007 0.013 0.015 0.013 0.013 0.063 0.042 0.022 0.018 0.012 0.015 0.007 0.009 0.014 0.003 0.017 0.016 0.016 0.019 WC WC WC WC WC WC WC WC 1500 1500 1800 1800 1800 1800 1800 1800 0.261 0.296 0.251 0.093 0.430 0.520 0.256 0.269 0.616 1.174 0.853 0.628 0.404 0.222 1.494 2.764 3.491 2.540 3.008 3.067 3.945 2.856 2.140 WC WC WC WC WC WC WC WC 1500 1500 1800 1800 1800 1800 1800 1800 0.030 0.021 0.031 0.032 0.048 0.029 0.023 0.022 0.014 0.020 0.004 0.001 0.008 0.026 0.034 0.006 Appendix 8. (continued) May WC _0000 WC _0000 WC _0000 WC _0000 WC _0000 WC _0000 WC _0000 WC _0000 WC _0600 WC _0600 WC _0600 WC _0600 WC _0600 WC _0600 WC _0600 WC _0600 WC _0900 WC _0900 WC _0900 10.222 9.045 10.602 12.724 13.993 11.598 9.772 10.047 13.626 11.762 11.686 10.052 9.277 9.924 12.411 11.903 16.448 14.297 9.921 18.989 19.700 13.637 13.336 41.194 46.605 37.055 36.554 10.338 9.530 8.261 WC 0000 WC 0000 WC 0000 WC 0000 WC 0600 WC 0600 WC 0600 WC 0600 WC 0900 WC 0900 WC 0900 WC 0900 WC 1200 WC 1200 WC 1200 WC 1200 WC 1500 WC 1500 WC 1500 June 0.136 0.301 0.313 0.459 0.294 0.396 0.010 0.223 7.756 1.840 1.282 1.563 1.534 1.454 2.161 1.875 3.202 3.213 2.765 79.129 74.909 82.670 73.632 72.888 74.531 73.065 68.734 75.815 72.939 60.548 74.358 70.409 71.878 67.477 68.074 70.112 68.766 69.139 WC 0000 WC 0000 WC 0000 WC 0000 WC 0600 WC 0600 WC 0600 WC 0600 WC 0900 WC 0900 WC 0900 WC 0900 WC 1200 WC 1200 WC 1200 WC 1200 WC 1500 WC 1500 WC 1500 144 July 27.928 29.849 30.380 28.533 34.636 31.247 35.813 33.098 31.797 32.534 30.068 30.059 35.117 33.594 34.299 34.583 27.836 30.399 30.844 26.756 31.450 39.094 41.347 46.243 42.860 42.036 49.597 32.680 44.885 24.101 24.502 41.588 38.893 33.447 34.697 39.326 37.281 33.006 24.433 29.326 25.862 26.524 24.808 24.594 20.825 16.235 23.727 25.963 22.154 19.948 24.808 29.084 28.452 27.265 29.523 28.264 29.830 August WC 0000 6.689 WC 0000 5.753 WC 0000 6.972 WC 0000 8.851 WC 0000 8.248 WC 0000 9.936 WC 0000 3.164 WC 0000 6.979 WC 0600 4.876 WC 0600 6.203 WC 0600 7.516 WC 0600 9.753 WC 0600 9.426 WC 0600 6.647 WC 0600 6.274 WC 0600 6.112 WC 0900 6.056 WC 0900 6.094 WC 0900 6.684 7.334 4.135 2.818 3.179 4.109 5.431 1.256 1.474 5.424 4.540 7.354 6.783 5.554 7.669 6.215 5.502 5.355 5.736 3.582 WC _0900 WC _0900 WC _0900 WC _0900 WC _0900 WC _1200 WC _1200 WC _1200 WC _1200 WC _1200 WC _1200 WC _1200 WC _1200 WC _1500 WC _1500 WC _1500 WC _1500 WC _1500 WC _1500 WC _1500 WC _1500 WC _1800 WC _1800 WC _1800 WC _1800 WC _1800 WC _1800 WC _1800 WC _1800 10.577 9.924 12.039 16.079 15.022 7.489 7.418 7.118 8.381 5.750 5.473 7.617 6.774 5.796 5.841 5.580 5.620 5.755 5.521 4.165 5.547 11.802 5.188 8.163 8.069 4.284 7.019 8.465 11.163 8.830 7.444 7.106 14.111 15.211 45.494 36.347 22.683 42.369 40.603 22.400 29.627 26.080 WC 1500 WC 1800 WC 1800 WC 1800 WC 1800 2.765 7.061 6.713 4.793 5.187 68.771 69.064 70.889 67.923 68.506 WC 1500 WC 1800 WC 1800 WC 1800 WC 1800 19.392 19.462 20.001 17.063 15.015 14.412 13.842 13.203 145 27.606 27.999 30.496 24.552 24.739 27.360 29.584 31.426 34.249 35.702 28.032 13.028 17.544 14.675 12.266 WC 0900 WC 0900 WC 0900 WC 0900 WC 0900 WC 1200 WC 1200 WC 1200 WC 1200 WC 1200 WC 1200 WC 1200 WC 1200 WC 1500 WC 1500 WC 1500 WC 1500 WC 1500 WC 1500 WC 1500 WC 1500 WC 1800 WC 1800 WC 1800 WC 1800 WC 1800 WC 1800 WC 1800 WC 1800 6.352 5.966 6.452 7.859 7.348 7.054 7.764 6.189 6.629 5.411 6.616 0.928 2.537 3.256 5.297 6.961 7.577 3.979 4.437 4.691 4.844 6.829 7.012 5.400 5.559 8.101 7.689 4.737 5.743 5.294 4.232 3.152 4.923 5.863 7.348 8.441 6.309 6.939 6.911 6.040 8.750 6.565 6.562 4.694 5.886 5.379 5.359 6.913 5.422 4.152 Appendix 9. Diurnal algal biofilm phosphate concentrations, mg L-1 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore January 1200 0.004 1200 0.008 1200 0.002 1200 0.000 1500 0.001 1500 0.000 1500 0.000 1500 0.000 1800 0.001 1800 0.000 1800 0.000 1800 0.000 0000 0.000 0000 0.002 0000 0.000 0000 0.007 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1800 1800 1800 1800 February 3.164 0.036 3.945 0.049 4.149 1.016 5.254 0.797 5.211 0.084 5.128 0.099 5.389 0.352 4.514 0.286 3.236 0.289 4.678 0.274 4.457 0.102 4.447 0.114 4.043 0.130 4.651 0.104 4.554 0.107 4.825 0.059 2.600 0.083 2.215 0.223 5.166 0.155 1.487 0.248 1.182 0.055 2.375 0.027 2.355 0.076 1.155 0.026 0.002 0.010 0.016 0.017 0.002 0.001 0.003 0.022 0.010 0.026 0.002 0.004 0.007 0.002 0.007 0.007 0.010 0.008 0.010 0.004 0.009 0.000 0.000 Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore Pore 0000 0000 0000 0000 0600 0600 0600 0600 0900 0900 0900 0900 1200 1200 1200 1200 1500 1500 1500 1500 1800 1800 1800 1800 146 March 0.009 0.005 0.026 0.011 0.033 0.005 0.053 0.003 0.079 0.003 0.089 0.009 0.093 0.012 0.109 0.002 0.069 0.025 0.021 0.020 0.038 0.004 0.026 0.034 0.014 0.005 0.002 0.005 0.053 0.009 0.015 0.018 0.003 0.023 0.003 0.009 0.005 0.003 0.003 0.018 0.005 0.001 0.015 0.021 0.018 0.002 0.002 0.002 0.247 0.192 0.277 0.795 3.884 4.199 2.535 2.522 7.899 4.741 2.073 1.674 4.180 4.658 5.188 4.842 4.376 4.684 3.840 4.671 2.997 4.778 4.027 4.338 4.129 3.185 4.234 5.163 0.027 0.042 1.013 1.334 9.627 5.973 4.763 5.262 2.094 2.842 0.417 0.283 4.719 4.751 3.819 4.164 5.046 4.752 4.907 3.752 Pore _0:00 Pore _0:00 Pore _0:00 Pore _0:00 Pore _0:00 Pore _0:00 Pore _0:00 Pore _0:00 Pore _6:00 Pore _6:00 Pore _6:00 Pore _6:00 Pore _6:00 Pore _6:00 Pore _6:00 Pore _6:00 Pore _9:00 Pore _9:00 Pore _9:00 Pore _9:00 Pore _9:00 Pore _9:00 Pore _9:00 Pore _9:00 Pore _12:00 Pore _12:00 Pore _12:00 Pore _12:00 April 0.151 0.155 0.174 0.178 0.186 0.187 0.204 0.192 0.131 0.130 0.131 0.150 0.116 0.126 0.149 0.149 0.049 0.064 0.098 0.106 0.056 0.051 0.056 0.061 0.052 0.035 0.095 0.094 0.017 0.014 0.052 0.059 0.011 0.009 0.019 0.025 0.017 0.017 0.036 0.025 0.016 0.023 0.013 0.019 0.025 0.013 0.028 0.026 0.028 0.038 0.017 0.022 0.007 0.008 0.002 0.009 Pore _12:00 Pore _12:00 Pore _12:00 Pore _12:00 Pore _15:00 Pore _15:00 Pore _15:00 Pore _15:00 Pore _15:00 Pore _15:00 Pore _15:00 Pore _15:00 Pore _18:00 Pore _18:00 Pore _18:00 Pore _18:00 Pore _18:00 Pore _18:00 Pore _18:00 Pore _18:00 0.272 0.092 0.082 0.073 0.070 0.053 0.042 0.043 0.155 0.168 0.054 0.051 0.033 0.026 0.030 0.025 0.020 0.021 0.013 0.022 0.001 0.007 0.001 0.005 0.017 0.020 0.035 0.029 0.011 0.016 0.008 0.011 0.011 0.016 0.030 0.032 0.035 0.018 0.009 0.056 Appendix 9. (continued) Pore _0000 Pore _0000 Pore _0000 Pore _0000 Pore _0000 Pore _0000 Pore _0000 May 7.799 7.542 22.490 8.248 6.583 19.353 13.270 9.182 23.400 10.856 7.834 23.864 13.794 9.469 22.717 15.731 10.620 19.331 12.920 7.606 13.479 Pore 0000 Pore 0000 Pore 0000 Pore 0000 Pore 0600 Pore 0600 Pore 0600 June 0.803 0.584 0.851 0.659 0.481 0.157 0.494 76.668 78.005 75.194 78.731 75.549 74.316 77.154 147 Pore 0000 Pore 0000 Pore 0000 Pore 0000 Pore 0600 Pore 0600 Pore 0600 July 28.190 27.420 31.632 24.870 32.811 34.299 31.311 29.193 30.420 34.024 39.562 33.753 43.664 46.753 26.944 24.723 21.953 25.780 22.691 22.201 22.136 Pore 0000 Pore 0000 Pore 0000 Pore 0000 Pore 0000 Pore 0000 Pore 0000 August 9.325 4.246 6.145 7.818 1.742 4.465 4.907 3.820 2.836 6.377 5.619 4.788 4.294 3.657 Pore _0000 Pore _0600 Pore _0600 Pore _0600 Pore _0600 Pore _0600 Pore _0600 Pore _0600 Pore _0600 Pore _0900 Pore _0900 Pore _0900 Pore _0900 Pore _0900 Pore _0900 Pore _0900 Pore _0900 Pore _1200 Pore _1200 Pore _1200 Pore _1200 Pore _1200 Pore _1200 Pore _1200 Pore _1200 Pore _1500 Pore _1500 Pore _1500 Pore _1500 Pore _1500 Pore _1500 14.699 17.576 16.720 15.744 18.682 13.827 11.693 16.471 16.868 15.864 15.184 13.087 15.565 1.906 15.145 12.103 12.519 8.666 11.163 Pore 0600 Pore 0900 Pore 0900 Pore 0900 Pore 0900 Pore 1200 Pore 1200 Pore 1200 Pore 1200 Pore 1500 Pore 1500 Pore 1500 Pore 1500 Pore 1800 Pore 1800 Pore 1800 Pore 1800 0.456 2.262 0.518 0.653 0.513 0.267 0.238 0.260 0.238 0.200 1.242 1.153 0.182 3.854 4.279 3.550 2.244 73.198 79.648 71.816 72.391 72.950 66.648 68.199 70.303 70.086 66.695 66.231 69.479 66.316 66.449 66.638 67.497 68.935 5.915 5.378 9.663 7.526 6.689 7.610 5.998 5.864 5.522 6.750 6.096 4.886 7.545 6.881 148 Pore 0600 Pore 0900 Pore 0900 Pore 0900 Pore 0900 Pore 1200 Pore 1200 Pore 1200 Pore 1200 Pore 1500 Pore 1500 Pore 1500 Pore 1500 Pore 1800 Pore 1800 Pore 1800 Pore 1800 27.939 25.262 31.032 25.082 25.195 31.476 26.815 24.182 18.431 34.526 34.998 32.904 30.743 30.637 31.273 25.139 21.108 44.526 34.269 34.232 41.225 44.508 34.827 34.612 39.398 35.635 34.311 34.570 29.693 33.972 31.666 32.572 33.234 31.290 18.920 23.595 18.346 21.771 20.940 22.801 23.769 22.947 19.931 20.077 20.247 13.925 Pore 0000 Pore 0600 Pore 0600 Pore 0600 Pore 0600 Pore 0600 Pore 0600 Pore 0600 Pore 0600 Pore 0900 Pore 0900 Pore 0900 Pore 0900 Pore 0900 Pore 0900 Pore 0900 Pore 0900 Pore 1200 Pore 1200 Pore 1200 Pore 1200 Pore 1200 Pore 1200 Pore 1200 Pore 1200 Pore 1500 Pore 1500 Pore 1500 Pore 1500 Pore 1500 Pore 1500 7.498 6.397 8.643 4.561 4.008 8.746 8.691 9.443 9.086 12.084 10.069 8.751 8.048 8.947 9.527 10.294 12.574 0.129 0.895 2.556 4.777 0.869 1.025 3.250 3.928 1.962 4.865 3.923 5.888 2.401 2.520 3.912 21.201 21.656 24.795 25.466 9.810 8.082 24.610 28.695 32.601 34.425 38.971 37.027 48.323 42.420 33.250 36.426 27.213 31.299 29.600 30.959 23.346 18.881 23.720 23.354 15.120 13.832 21.765 20.443 22.664 25.613 Pore _1500 Pore _1500 Pore _1800 Pore _1800 Pore _1800 Pore _1800 Pore _1800 Pore _1800 Pore _1800 Pore _1800 7.623 6.597 9.520 10.892 7.749 7.884 8.195 8.464 6.266 4.277 15.909 14.072 25.681 23.255 36.579 35.240 27.848 34.920 Pore 1500 Pore 1500 Pore 1800 Pore 1800 Pore 1800 Pore 1800 Pore 1800 Pore 1800 Pore 1800 Pore 1800 2.479 2.821 16.016 17.548 11.285 11.555 13.795 12.542 149 3.131 25.308 3.238 26.823 3.134 4.426 3.019 3.387 7.178 7.785 6.236 5.943 Appendix 10. Mesocosm physiochemical measurements and respiration Treatment Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Substrate sediment sediment sediment sediment sediment leaves leaves leaves leaves leaves sponge sponge sponge sponge sponge glass glass glass glass glass glass sediment sediment sediment sediment sediment DO 1 DO 2 DO 3 pH 1 pH 2 pH 3 Temp 1 Temp 2 Temp 3 7.63 7.73 7.76 7.77 7.69 7.54 7.38 7.36 7.43 7.47 7.61 7.45 7.79 7.86 7.58 7.66 7.61 7.37 7.74 7.39 7.4 7.54 7.52 7.41 7.37 7.41 7.67 7.77 7.8 7.76 7.71 7.68 7.41 7.51 7.66 7.65 7.42 7.49 7.79 7.91 7.64 7.65 7.75 7.45 7.76 7.45 7.51 7.59 7.71 7.47 7.47 7.54 7.74 7.86 7.85 7.97 7.73 7.53 7.4 7.59 7.53 7.47 7.44 7.35 7.87 7.87 7.6 7.6 7.75 7.46 7.69 7.48 7.51 7.64 7.72 7.55 7.47 7.48 8.59 8.64 8.57 8.59 8.54 8.62 8.58 8.42 8.62 8.63 8.55 8.56 8.59 8.6 8.57 8.61 8.56 8.68 8.65 8.61 8.54 8.61 8.64 8.52 8.6 8.61 8.61 8.62 8.56 8.6 8.56 8.61 8.57 8.45 8.59 8.6 8.53 8.55 8.59 8.61 8.56 8.6 8.55 8.63 8.61 8.59 8.58 8.61 8.63 8.56 8.56 8.58 8.69 8.66 8.67 8.68 8.54 8.71 8.64 8.53 8.65 8.64 8.59 8.6 8.64 8.61 8.59 8.7 8.61 8.58 8.58 8.57 8.51 8.63 8.67 8.62 8.6 8.62 20.3 20.4 20.1 20.5 20 20.1 21.3 20.8 20.9 21.3 21.1 21.7 19.9 19.3 20.8 20.6 20.5 21.8 20.1 21.9 21.7 21.2 20.5 21.4 21.5 21.5 19.9 20.2 19.7 20.1 19.7 20.2 21.3 20.3 20.5 21 21.2 21.5 19.6 18.9 20.3 20.3 19.9 21.6 19.7 21.6 21.5 21 20 21.2 21.2 21.5 20.2 19.9 19.6 19.7 19.5 20.6 21.1 20.3 20.8 21.2 21.8 21.8 19.5 18.9 20.7 20 20 21.9 20 21.8 22 20.9 20 21.2 21.4 21.7 150 μg O2 Consumed / h 0.16870 0.10730 -0.02222 0.28817 0.12293 0.72249 0.62982 0.50142 0.85200 0.20331 0.06933 0.08273 0.09390 0.11399 0.06040 0.07715 0.15754 0.06710 0.10060 0.11399 0.08832 0.04700 0.19773 0.15642 0.14191 0.00000 Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate leaves leaves leaves leaves leaves sponge sponge sponge sponge sponge glass glass glass glass glass glass sediment sediment sediment sediment sediment leaves leaves leaves leaves leaves sponge sponge sponge 8.02 7.55 7.72 7.79 7.68 7.58 7.43 7.52 7.6 7.63 7.7 7.7 7.71 7.76 7.65 7.62 7.56 7.44 7.58 7.57 7.53 7.48 7.54 7.49 7.58 7.42 7.53 7.55 7.39 7.89 7.64 7.82 7.94 7.67 7.66 7.55 7.69 7.76 7.62 7.7 7.74 7.77 8.02 7.73 7.75 7.62 7.42 7.55 7.71 7.64 7.51 7.54 7.43 7.64 7.46 7.53 7.54 7.47 8.08 7.65 7.91 7.78 7.61 7.66 7.45 7.56 7.75 7.6 7.78 7.8 7.83 7.77 7.67 7.74 7.61 7.48 7.47 7.64 7.57 7.39 7.51 7.45 7.66 7.42 7.55 7.52 7.46 8.67 8.6 8.59 8.63 8.52 8.56 8.53 8.52 8.5 8.49 8.63 8.59 8.66 8.61 8.56 8.55 8.68 8.61 8.63 8.65 8.62 8.72 8.62 8.65 8.65 8.53 8.6 8.61 8.6 8.66 8.6 8.59 8.65 8.56 8.56 8.51 8.52 8.53 8.53 8.64 8.57 8.65 8.6 8.54 8.56 8.67 8.61 8.62 8.66 8.62 8.71 8.62 8.65 8.61 8.58 8.58 8.59 8.57 8.76 8.68 8.69 8.73 8.61 8.62 8.56 8.52 8.54 8.5 8.69 8.66 8.68 8.69 8.6 8.59 8.68 8.67 8.67 8.69 8.56 8.78 8.72 8.74 8.67 8.6 8.62 8.62 8.59 151 18.7 20.8 19.8 19.3 20.5 20.5 21.1 20.8 20.1 20.6 20.1 20.5 19.9 19.8 20.2 20.2 20.6 21.5 21.2 20.2 21.1 21.5 21 21.5 20.8 21.8 21 20.9 21 18.3 20.3 19.4 18.8 20 19.9 20.9 20.5 19.7 20.5 19.9 20.1 19.6 19.5 19.8 20.1 20.5 21.6 21.3 20 21 21.3 20.9 21.6 20.3 21.4 21 20.7 20.9 18.4 20.3 19.1 19.4 20.5 20 21 20.6 19.5 21.1 19.8 19.9 19.8 19.7 19.8 20.2 20.8 21.7 21.4 20.1 21.5 21.8 21.3 21.6 20.4 21.4 21.4 21.4 21.4 0.57958 0.58962 0.94690 1.06414 1.39685 0.10171 0.14637 0.09836 0.10730 0.20890 0.09948 0.14191 0.11511 0.08273 0.09613 0.03249 0.09725 0.07045 0.16089 0.03696 0.02802 0.67448 0.90224 0.61642 0.95584 1.00720 0.07938 0.08943 0.04031 Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control sponge sponge glass glass glass glass glass glass sediment sediment sediment sediment sediment leaves leaves leaves leaves leaves sponge sponge sponge sponge sponge glass glass glass glass glass glass 7.49 7.47 7.61 7.5 7.45 7.64 7.6 7.64 7.52 7.48 7.83 7.89 7.6 7.63 7.32 7.58 7.49 7.62 7.49 7.32 7.5 7.61 7.52 7.17 7.73 7.98 7.68 7.67 7.53 7.61 7.49 7.57 7.49 7.53 7.64 7.64 7.78 7.55 7.47 7.85 7.95 7.77 7.71 7.31 7.6 7.57 7.72 7.45 7.38 7.54 7.61 7.6 7.62 7.83 7.99 7.78 7.74 7.62 7.46 7.45 7.61 7.44 7.53 7.73 7.56 7.69 7.51 7.47 7.91 7.91 7.56 7.81 7.4 7.58 7.45 7.63 7.46 7.35 7.41 7.6 7.67 7.48 7.69 7.83 7.72 7.74 7.56 8.59 8.56 8.61 8.68 8.66 8.66 8.71 8.71 8.55 8.56 8.58 8.62 8.62 8.64 8.58 8.64 8.58 8.64 8.53 8.49 8.51 8.54 8.51 8.53 8.6 8.66 8.59 8.52 8.51 8.57 8.54 8.61 8.68 8.67 8.66 8.71 8.66 8.54 8.55 8.57 8.61 8.62 8.66 8.57 8.63 8.56 8.65 8.52 8.49 8.5 8.56 8.51 8.55 8.61 8.62 8.54 8.49 8.53 8.54 8.57 8.72 8.63 8.67 8.7 8.62 8.6 8.57 8.6 8.62 8.6 8.61 8.77 8.6 8.71 8.6 8.61 8.56 8.52 8.56 8.6 8.55 8.6 8.59 8.61 8.55 8.51 8.46 152 21.1 21.3 20.8 21.6 21.2 21 20.8 20.1 21.2 21.6 19.4 19.1 20.8 19.7 22 20.9 21.2 20.6 21.3 22.1 21.1 20.6 21.3 21 20.1 18.6 20.1 20.2 21.3 21.2 21.1 20.9 21.5 21.1 20.8 20.3 19.8 21.3 21.5 19 18.8 20.5 19.4 21.6 20.6 20.9 20.6 21.2 22.1 21 20.4 21.1 20.9 19.9 17.8 19.8 19.9 20.9 21.6 21.4 21.2 21.9 21.3 20.5 20.5 20.3 21.2 21.4 19 19 20.6 19.6 21.7 21 21.2 21 21.4 22.3 21.4 20.6 20.7 21.4 20 18.9 19.8 19.7 21.3 0.17875 0.03584 0.13744 0.16312 0.09278 0.05482 0.10171 0.06152 0.07268 0.12851 0.04477 0.05259 0.09390 0.43108 0.87880 -0.18299 0.61530 1.55875 0.06822 0.05817 0.10395 0.03472 0.04589 0.09390 0.23123 0.05705 0.08273 0.04700 0.06040 Appendix 11. Mesocosm dissolved nutrient and total organic carbon concentrations Treatment Substrate Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Control Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Exudate Leaves Leaves Leaves Leaves Sediment Sediment Sediment Sediment Sponge Sponge Sponge Sponge Glass Glass Glass Glass Leaves Leaves Leaves Leaves Sediment Sediment Sediment Sediment Sponge Day 1 mg NO3 / L 5.785 3.555 3.467 4.460 8.489 8.355 4.855 5.191 0.166 0.149 0.579 0.542 8.371 8.194 7.310 6.992 5.579 5.456 3.478 3.680 6.394 6.405 7.424 7.426 0.093 Day 2 mg NO3 / L 6.862 6.508 6.812 6.687 9.868 10.001 11.236 11.034 1.704 1.679 1.782 1.789 10.928 11.320 11.299 11.175 6.301 6.164 0.804 0.787 9.871 9.964 9.877 9.999 1.612 Day 1 mg PO4 / L 0.017 0.032 0.015 0.003 0.003 0.003 0.000 0.000 0.001 0.005 0.005 0.001 0.001 0.000 0.009 0.000 0.004 0.020 0.008 0.002 0.022 0.078 0.060 0.054 0.041 Day 2 mg PO4 / L 0.023 0.014 0.017 0.022 0.003 0.001 0.004 0.000 0.000 0.000 0.000 0.000 0.003 0.001 0.000 0.001 0.014 0.017 0.004 0.002 0.000 0.001 0.000 0.000 0.003 153 Day 1 mg TOC / L 8.630 8.317 Day 2 mg TOC / L 8.710 9.836 5.631 5.756 5.584 5.290 6.718 6.075 6.138 6.212 6.053 5.763 5.032 4.954 10.060 10.420 10.440 9.355 7.879 7.540 7.653 7.714 9.513 8.388 Exudate Exudate Exudate Exudate Exudate Exudate Exudate Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Sponge Sponge Sponge Glass Glass Glass Glass Leaves Leaves Leaves Leaves Sediment Sediment Sediment Sediment Sponge Sponge Sponge Sponge Glass Glass Glass Glass Leaves Leaves Leaves Leaves Sediment Sediment 0.092 0.040 0.014 5.810 5.912 7.269 7.539 3.869 3.846 4.825 3.667 7.103 7.040 7.674 7.536 0.264 0.269 1.222 1.186 5.364 5.424 9.470 9.340 7.325 7.434 6.534 6.596 7.332 7.064 1.698 1.210 1.194 9.307 9.111 8.129 8.139 6.294 6.352 5.827 5.908 8.908 8.872 7.872 7.923 2.785 2.897 2.869 2.900 11.826 12.085 8.683 8.387 10.520 10.461 10.131 10.803 8.422 8.092 0.000 0.002 0.012 0.045 0.006 0.017 0.015 0.001 0.004 0.027 0.040 0.000 0.000 0.000 0.001 0.003 0.002 0.000 0.000 0.000 0.004 0.005 0.001 0.007 0.001 0.024 0.018 0.000 0.000 0.001 0.000 0.000 0.001 0.000 0.001 0.000 0.029 0.029 0.007 0.006 0.001 0.000 0.002 0.002 0.000 0.001 0.001 0.002 0.001 0.002 0.000 0.001 0.013 0.010 0.017 0.015 0.000 0.000 154 8.539 8.513 7.134 8.005 7.092 7.035 8.600 7.717 8.414 8.183 5.016 5.323 6.027 4.897 6.646 6.847 6.556 6.468 5.422 5.500 5.149 5.816 7.912 9.203 8.129 7.940 5.226 5.078 5.268 4.753 Algae Algae Algae Algae Algae Algae Algae Algae Algae Algae Sediment Sediment Sponge Sponge Sponge Sponge Glass Glass Glass Glass 5.979 6.014 0.204 0.204 0.568 0.630 6.818 6.734 6.832 6.840 9.156 8.954 3.978 3.972 2.195 2.199 9.599 9.360 10.900 10.154 0.002 0.001 0.002 0.001 0.000 0.000 0.009 0.009 0.005 0.000 0.000 0.003 0.000 0.000 0.002 0.000 0.002 0.000 0.000 0.000 155 6.652 6.952 6.589 5.889 6.274 5.478 5.534 5.984