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Sewage

Sewage refers to the wastewater and waste matter that is carried away from homes, businesses, and other buildings through a system of pipes and sewers.
This waste material can contain a variety of contaminants, including human waste, detergents, chemicals, and microorganisms.
Proper treatment and disposal of sewage is important for public health and environmental protection.
Researchers studying sewage may use a variety of protocols and techniques to analyze its composition and identify potential hazards or areas for improvement in sewage management systems.
PubCompare.ai's AI-driven platform can help optimize sewage research protocols by locating the best methods from literature, preprints, and patents, and comparing them using advanced tools to improve reproducibility and accuracy.

Most cited protocols related to «Sewage»

We amplified three separate replicates of the V6 region of ribosomal RNAs from Escherichia coli (E. coli) genomic DNA isolated from pure culture and from 10 metagenomic microbial DNA samples isolated from raw sewage. Custom fusion primers for PCR consisted of the Illumina adaptor, 12 different inline barcodes (forward primer) or 8 dedicated indices (reverse primer), and conserved regions of the V6 sequence (Figure 1). This use of 96 unique barcode-index combinations allows multiplexing 96 samples per lane. Paired indices with dual indexing reads could further increase the level of multiplexing. For each of the 33 libraries, we carried out the PCR in triplicate 33 uL reaction volumes with an amplification cocktail containing 1.0 U Platinum Taq Hi-Fidelity Polymerase (Life Technologies, Carlsbad CA), 1X Hi-Fidelity buffer, 200 uM dNTP PurePeak DNA polymerase mix (Pierce Nucleic Acid Technologies, Milwaukee, WI), 1.5 mM MgSO4 and 0.2 uM of each primer. We added approximately 10–25 ng template DNA to each PCR and ran a no-template control for each primer pair. Cycling conditions were: an initial 94°C, 3 minute denaturation step; 30 cycles of 94°C for 30s, 60°C for 60s, and 72°C for 90s; and a final 10 minute extension at 72°C. The triplicate PCR reactions were pooled after amplification and purified using a Qiaquick PCR 96-well PCR clean up plate (Qiagen, Valencia CA). Purified DNA was eluted in 30 uL of Qiagen buffer EB. PicoGreen quantitation (Life Technologies, Carlsbad CA) provided a basis for pooling equimolar amounts of product. After size-selecting products of 200–240 bp on 1% agarose using Pippin Prep (SageScience, Beverly MA), we employed qPCR (Kapa Biosystems, Woburn MA) to measure concentrations prior to sequencing on one lane of an Illumina Hiseq 100 cycle paired-end run. The remaining 90% of the lane was dedicated to PhiX DNA and served as the run control. The combination of CASAVA 1.8.2 to identify reads by index and a custom Python script that resolved barcodes demultiplexed the datasets.
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Publication 2013
Buffers Conserved Sequence DNA-Directed DNA Polymerase Escherichia coli Genome Metagenome Nucleic Acids Oligonucleotide Primers PicoGreen Platinum Python Ribosomal RNA Sepharose Sewage Sulfate, Magnesium Taq Polymerase
Salvador, the capital of the State of Bahia, in the Northeast Brazil has approximately 2.5 million inhabitants, and is located in the poorest region in the country. Over 80% of the population is black or mixed-race (mulatto). There is a high degree of social inequality: GINI coefficient was 0.66 in 2000 [12 ]. The city currently presents high coverage of childhood vaccination (essentially 100% for neonatal BCG and measles-mumps-rubella vaccine, in 2003), water supply (95% of households with water supply in 2000) and sanitation (75% households with sanitation connection in 2000). The city of Salvador has several advantages as the site for this study. First, a ISAAC survey conducted in 1995 demonstrated a high prevalence of asthma: 27.1% and 12.5% of schoolchildren aged 13–14 years reported wheezing in the last 12 months [13 (link)] and asthma ever, respectively. Another study showed a prevalence of 10% among schoolchildren aged 12–16 years [14 (link)]. Second, significant improvements in living conditions have occurred in recent years. A sanitation programme was recently implemented (increasing the households connected to a safe sewage disposal from 30% to 70%) with subsequent reduction in the prevalence of intestinal parasitic infection and incidence of childhood diarrhoea [15 ]. Third, the health impact of such a sanitation programme has been assessed by a large epidemiologic study[15 ]; the participants of the evaluation of impact of the sanitation programme were recruited as the study population of the present study on allergic diseases.
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Publication 2006
Asthma Diarrhea Households Hypersensitivity Infant, Newborn Intestinal Diseases, Parasitic Measles-Mumps-Rubella Vaccine Sewage Vaccination Coverage
The bacteriophage sensitive strains used during the production and quality control of BFC-1 are P. aeruginosa strain ‘573’, were isolated at the Eliava Institute of Bacteriophage, Microbiology and Virology (EIBMV) in the 1970s from bone marrow interstitial fluid, and S. aureus strain '13 S44 S′, isolated at the Brussels Burn Centre in 2006 from a burn wound. Initially, S. aureus strain Wood 60 (EIBMV collection) was used for propagation of phage ISP, but for the production of this cocktail the phage was propagated on S. aureus 13 S44 S. The absence of temperate phages from the host strains was tested as described in a separate section of this paper.
For bacteriophage isolation from natural samples such as sewage and river water, one millilitre of 10×concentrated LB Broth (Becton Dickinson), 1 ml ‘host bacteria’ suspension, containing 108 cfu in LB broth and 9 ml sewage or river water were mixed in a 14 ml sterile tube. This tube was incubated at 37°C for 1.5–2 h. Subsequently, 200 µl of chloroform (Sigma-Aldrich, Bornem, Belgium) was added and the tube was further incubated at 4°C for 1 h. The lysate was aspirated with a sterile 5 ml syringe and passed through a 0.45 µm membrane filter (Minisart, Sartorius, Vilvoorde, Belgium). Bacteriophages were titrated using the agar overlay method, as described above. All plaques with different morphology were touched with a sterile pipette tip, inoculated into 2 ml of sterile LB broth in 14 ml sterile tubes and incubated at 37°C for 2 h. Subsequently, 50 µl of chloroform was added and the tube(s) were incubated at 4°C for 1 h. For each tube, a dilution series (log(0)−log(−4)) was made in sterile 14 ml tubes filled with LB broth. Each dilution was titrated using the agar overlay method. Plates showing 1–10 plaques were analysed in detail. Again, all plaques with different morphology were touched with a sterile pipette tip, inoculated into 2 ml of sterile LB broth in 14 ml sterile tubes and incubated at 37°C for 2 h. This complete cycle was repeated until one plaque morphotype was obtained (homogeneous plaques).
In the case of bacteriophage ISP, which was isolated in the 1920s, porcelain, rather than membrane filters were employed.
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Publication 2009
Agar Bacteria Bacteriophages Bone Marrow Chloroform Dental Plaque Dental Porcelain Interstitial Fluid isolation Pseudomonas aeruginosa Rivers Senile Plaques Sewage Staphylococcus aureus Sterility, Reproductive Syringes Technique, Dilution Tissue, Membrane Wounds
The bacteriophages were isolated from sewage water sampled at the Käppala waste water treatment plant (location: WGS84: 59°21’22.2"N 18°13’45.3"E), recipient of waste water from Stockholm city including some hospitals, and kept at +4°C before processing. The sampling of water was approved by the owner, Käppalaförbundet, Box 3095, 181 03 Lidingö, Sweden, kappala@kappala.se (Phages are not considered to be protected species). The phages were amplified by mixing 50 ml of waste water with the same amount of double strength LB and 10 ml of a single ECOR strain bacteria cultured overnight. After incubation overnight at 30°C, 10 ml of the mixture was shaken with 1% v/v chloroform and left at room temperature for 30 minutes to kill the bacteria, centrifuged at 3000×g at +4°C for 15 minutes, and sterile filtered through a 0.45 μm membrane filter (Whatman, ref. no. 10462100). After checking the lysates for phages, the titre was measured in plaque assays. Sterile filtered phage lysates were diluted in SM buffer [30 ] or LB to five different dilutions (10-5–10-9). 100 μl of diluted phage and 200 μl of target bacteria were mixed with 2 ml SA, spread on pre-warmed LA plates, and incubated overnight at 30°C [31 (link)]. The harvested phages were selected according to their plaque morphology. Phages displaying large, clear and non-turbid plaques without a halo were classified as virulent. Phages were re-isolated by plaque purification from the LA plates when several phages on the same plate could be suspected. After additional plaque purifications, 25 virulent phages were saved and stored in 50% glycerol at -70°C as well as in LB at +4°C [32 (link)]. These phages were named according to guidelines in Kropinski et al. [33 (link)]. The six phages showing the broadest host range in the spot test (see below) were thus named as follows; vB_EcoP_SU10, vB_EcoP_SU16, vB_EcoP_SU27, vB_EcoP_SU32, vB_EcoP_SU57, and vB_EcoP_SU63, but only the last part of names is used in the following text, e.g. SU10, SU16 and so on.
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Publication 2015
Bacteria Bacteriophages Biological Assay Buffers Chloroform Dental Plaque Glycerin Host Range isolation & purification Plants Senile Plaques Sewage Sterility, Reproductive Technique, Dilution Tissue, Membrane
We conducted studies at three marine beaches affected by treated sewage discharge from nearby Publicly Owned Treatment Works (POTW). In 2005, we studied Edgewater Beach in Biloxi, Mississippi, and in 2007 we studied Goddard Beach in Goddard Memorial State Park in West Warwick, Rhode Island and Fairhope Municipal Beach in Fairhope, Alabama (Figure 1). Each beach site was located within 7 miles or less of a treated sewage discharge outfall from facilities that served populations of at least 15,000. Based on historical records, each beach site showed variability in water quality, but were generally in compliance with local and federal water quality guidelines.
Data collection procedures for the health survey have been described previously [6 (link),7 (link)]. In brief, we conducted surveys on weekends and holidays between May and September. Upon arrival beachgoers were provided a pamphlet describing the study. After reviewing the pamphlet, interviewers approached the household group or individual and offered them the opportunity to enroll in the study. On most days, all beachgoers arriving between approximately 11 AM and 4 PM were offered enrollment. Respondents were ineligible if they had completed the study in the previous 30 days, or if there was no adult (18 years of age or older) household member present. Households provided verbal consent and completed an enrollment questionnaire consisting of demographic information, swimming exposures in the previous two weeks, and the presence of underlying health conditions, such as chronic diarrhea, asthma, or skin conditions. As they left the beach for the day, participants completed a questionnaire to ascertain the extent and duration of their contact with water and other activities during their visit to the beach such as contact with sand and food consumption. Ten to twelve days following the beach visit, we telephoned participants and asked about the occurrence of new gastrointestinal, skin, respiratory, eye, or ear symptoms.
The study procedures, questionnaires, protocols and consent process were reviewed and approved by the Institutional Review Board of the Centers for Disease Control and Prevention.
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Publication 2010
Adult Asthma Diarrhea Ethics Committees, Research Food Households Interviewers Marines Patient Discharge Respiratory Rate Sewage Skin Skin Diseases

Most recents protocols related to «Sewage»

Before HTT, an initial blood sample was collected using an EDTA.K2 anticoagulant tube. A total of 8 ml of venous blood was taken from the patients’ cubital vein. The initial physiological indicators (SBP, DBP, HR, SaO2, and Tcore) were also measured. After HTT, post-exercise blood samples were collected immediately, and physiological data were measured after 5-min breaking. Twenty-four hours after HTT, blood samples for the recovery period were gathered. The feces were collected in the morning of two HTTs as pre-training and post-training samples. Clean cotton swabs were used to collect fresh fecal samples (5–10 g, no mix of urine, disinfectant, and sewage) into 15 ml sterile test tubes. Furthermore, the contents of organ injury biomarkers in plasma were detected, including alanine aminotransferase (ALT), alkaline phosphatase (AST), alkaline phosphatase (ALP), bilirubin, lactic dehydrogenase (LDH), alpha-hydroxybutyric dehydrogenase (α-HBDH), creatinine, urea nitrogen, cholinesterase, creatine kinase, prothrombin time (PT), activated partial prothrombin time (APTT), international normalized ratio (INR), Na+, K+, white blood cell (WBC), platelet (PLT), and hemoglobin.
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Publication 2023
Activated Partial Thromboplastin Time Alkaline Phosphatase Anticoagulants Bilirubin Biological Markers BLOOD Blood Platelets Butyrylcholinesterase Creatine Kinase Creatinine D-Alanine Transaminase Edetic Acid Feces Gossypium Hemoglobin Injuries International Normalized Ratio Leukocytes Nitrogen Oxidoreductase Patients physiology Plasma Sewage Sterility, Reproductive Times, Prothrombin Urea Urine Veins

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Publication 2023
Ammonia Biological Oxygen Demand Chemical Oxygen Demand COVID 19 Dietary Supplements Environmental Pollutants Forests gamma-glutamylaminomethylsulfonic acid Livestock Nitrogen Phosphorus Sewage Water Consumption Water Resources
Environmental assessment of the affected communities was conducted on open defecation, hygiene and sanitary practices, source of drinking water and sewage drainage system.
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Publication 2023
Defecation Drainage Sewage

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Publication 2023
SARS-CoV-2 Sewage

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Publication 2023
Antigens COVID 19 Diagnosis Epidemics Genes Head Sewage Test, Quick T Virus

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More about "Sewage"

Sewage, also known as wastewater or waste matter, refers to the used water and waste products that are carried away from homes, businesses, and other buildings through a system of pipes and sewer lines.
This waste material can contain a variety of contaminants, including human waste, detergents, chemicals, and microorganisms.
Proper treatment and disposal of sewage is crucial for public health and environmental protection.
Researchers studying sewage may utilize a range of protocols and techniques to analyze its composition and identify potential hazards or areas for improvement in sewage management systems.
These methods may include the use of the QIAamp Viral RNA Mini Kit for extracting viral RNA from sewage samples, the Qubit 2.0 Fluorometer for quantifying nucleic acids, and the FastDNA SPIN Kit for Soil for extracting DNA from soil-based sewage components.
Additionally, researchers may employ sodium hydroxide (NaOH) for pH adjustment, 0.22-μm filters for microbial filtration, and hydrochloric acid (HCl) for sample acidification.
The use of mixed cellulose ester membrane filters can also be important for capturing and concentrating microorganisms from sewage samples.
Furthermore, advanced analytical techniques such as MALDI-TOF MS (Matrix-Assisted Laser Desorption/Ionization Time-of-Flight Mass Spectrometry) may be utilized to identify and characterize the microbial communities present in sewage.
The NucliSENS kit, for example, can be used for the extraction and purification of nucleic acids from sewage samples.
By incorporating these tools and techniques, researchers can optimize their sewage research protocols, improve the reproducibility and accuracy of their findings, and contribute to the better understanding and management of this important environmental and public health issue.
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