Surface Water Monitoring Results

Total Page:16

File Type:pdf, Size:1020Kb

Surface Water Monitoring Results 2018 Water Quality Monitoring Report January – December 2018 Minnesota Department of Agriculture 625 Robert Street North, Saint Paul, MN 55155 www.mda.state.mn.us Published June 2019 In accordance with the Americans with Disabilities Act, this information is available in alternative forms of communication upon request by calling 651-201-6000. TTY users can call the Minnesota Relay Service at 711. The MDA is an equal opportunity employer and provider. Authors and Contributors Monitoring and Assessment Unit Hydrologists – Heather Johnson, Michael MacDonald, Scott Matteson, Katie Rassmussen, Matt Ribikawskis, Brennon Schaefer, Dylan Timm, and David Tollefson. Monitoring and Assessment Unit Supervisor - Bill VanRyswyk Editor – Heather Johnson Minnesota Department of Agriculture Pesticide and Fertilizer Management Division Monitoring and Assessment Unit Acknowledgements The following personnel and cooperating organizations were critical to the collection of much of the data presented in this report: MDA Laboratory Water Analysis Unit MDA Staff: Stefan Bischof, Russ Derickson, Ryan Lemickson, Jeff Paddock, and Luke Stuewe. Chippewa River Watershed Project, Carver County Water Management Organization, Fillmore County SWCD, Hawk Creek Watershed Project, International Water Institute, Martin County SWCD, Metropolitan Council Environmental Services, Minnesota Department of Natural Resources, Minnesota Pollution Control Agency, Minnesota State University – Mankato, Mower County SWCD, Redwood Cottonwood River Control Area, U.S. Geological Survey, Vermillion Community College and Weck Laboratory. Pursuant to Minn. Stat. § 3.197, the cost of preparing this report was approximately $26,867. Executive Summary Minnesota Department of Agriculture 2018 Annual Monitoring Report* Groundwater 684 pesticide samples were collected from 171 routine groundwater monitoring sites (monitoring wells, springs and private drinking water wells). o Forty different pesticides or pesticide degradates were detected out of 155 pesticide analytes that were analyzed by the MDA Laboratory. o Metolachlor ESA was the most frequently detected analyte (81%). o Glyphosate, and its degradate AMPA, were not detected in the 180 samples that were analyzed. Samples for glyphosate and AMPA were collected at least once from every groundwater site. o Six neonicotinoid insecticides, and two neonicotinoid insecticide degradates, were analyzed in the groundwater samples. There were no detections of neonicotinoids in urban monitoring wells. Detection frequencies of clothianidin, imidacloprid, and thiamethoxam ranged between 10 to 19%. o Isoxaflutole DKN was detected for the first time in MDA’s groundwater monitoring program. o Five pesticides were analyzed for the first time in 2018. Two of these pesticides (fomesafen and sulfentrazone) were detected in 15% and 6% of the samples collected statewide, respectively. o A total of four fomesafen detections exceeded 50% of the human health-based drinking water reference value, including one detection that was greater than the reference value. These samples were collected from three different wells. No other pesticide detections exceeded 50% of an applicable reference value. Private Well Pesticide Sampling 1,589 pesticide samples were collected in 2018 from private wells and analyzed by a contract laboratory. o At least one pesticide was detected in 84% of wells sampled. Eleven percent of the total wells sampled had one pesticide or pesticide degradate detected. Fifty-one percent of the total wells had between two to six pesticide compounds detected. o As many as 16 different pesticide compounds were detected in a single well. o Metolachlor ESA was the most frequently detected pesticide compound (72%). o Four neonicotinoid insecticides were detected infrequently: clothianidin (3%), dinotefuran (<1%), imidacloprid (<1%), and thiamethoxam (<1%). o No pesticide detections were above an applicable human health reference value. Surface water 1,050 pesticide samples were collected from 56 river or stream monitoring locations. o 155 pesticide compounds were analyzed; 72 pesticide compounds were detected. Forty-two of the 72 detected pesticide compounds were detected in less than 10% of the samples. Nine of the 72 detected pesticide compounds were detected in 68% or more of the samples. o A degradate of atrazine (hydroxyatrazine) was the most frequently detected pesticide compound in Minnesota surface water. o The three most detected pesticide parent compounds were 2,4-D, atrazine, and metolachlor. These were detected in 80, 75, and 75% of samples, respectively. o Chlorpyrifos was detected in 11 samples, including 10 detections over the Minnesota chronic standard (41 ng/L) and one detection over the Minnesota maximum standard (83 ng/L). o The neonicotinoid clothianidin was detected 65 times, including 29 detections equal to or over the USEPA benchmark (50 ng/L). o The neonicotinoid imidacloprid was detected 38 times. All imidacloprid detections were over the USEPA benchmark (10 ng/L). o Glyphosate was detected in 9% of samples. The maximum glyphosate detection was <1% of the lowest water quality reference value. o Fomesafen was first analyzed by the MDA in 2018 and was detected in 43% of samples. o Ninety-one detections were above the numeric applicable water quality reference value, including detections of acetochlor (8), atrazine (2), bifenthrin (2), chlorpyrifos (10), clethodim sulfoxide (1), clothianidin (29), diazinon (1), and imidacloprid (38). The MPCA will assess these detections, as well as the duration of concentration, for any applicable violation of water quality standards. 12 pesticide samples were collected from two lake locations. o Chlorpyrifos was detected in one lake sample over the Minnesota chronic standard (41 ng/L). The MPCA will assess this detection along with the duration of concentration to determine if there was a violation of a water quality standard. Rain Monitoring 35 pesticide samples were collected from three rain monitoring locations, and 16 pesticide compounds were detected. *Citation: Minnesota Department of Agriculture 2018 Water Quality Monitoring Report: https://www.mda.state.mn.us/pesticide-fertilizer/water- monitoring-reports-and-resources Table of Contents Table of Contents ............................................................................................................................i List of Figures .................................................................................................................................iv List of Tables ..................................................................................................................................viii List of Appendices ..........................................................................................................................xi Abbreviations ..................................................................................................................................xii Definitions.......................................................................................................................................xiii SECTION 1: Introductions ....................................................................................................... 1-1 1.1 Program history ................................................................................................................ 1-1 1.2 Overall program purpose ................................................................................................. 1-2 1.3 Program elements............................................................................................................. 1-2 1.4 Pesticide Monitoring Regions .......................................................................................... 1-2 1.5 Changes to program activities .......................................................................................... 1-4 1.5.1 Groundwater .......................................................................................................... 1-4 1.5.2 Surface water ......................................................................................................... 1-4 1.6 Recent precipitation patterns............................................................................................ 1-6 1.7 Chemical analytes and 2018 detection summary ............................................................. 1-6 SECTION 2: Groundwater Monitoring Results ..................................................................... 2-1 2.1 2018 Groundwater pesticide sampling summary ............................................................. 2-3 2.1.2 2018 Quality Assurance/Quality Control Summary ........................................... 2-12 2.2 Trend analysis ................................................................................................................ 2-12 2.3 Analysis of the common detection pesticides ................................................................ 2-15 2.3.1 Acetochlor results ................................................................................................ 2-17 2.3.2 Alachlor results .................................................................................................... 2-25 2.3.3 Atrazine results .................................................................................................... 2-32 2.3.4 Metolachlor results .............................................................................................. 2-44 2.3.5 Metribuzin results
Recommended publications
  • 2,4-Dichlorophenoxyacetic Acid
    2,4-Dichlorophenoxyacetic acid 2,4-Dichlorophenoxyacetic acid IUPAC (2,4-dichlorophenoxy)acetic acid name 2,4-D Other hedonal names trinoxol Identifiers CAS [94-75-7] number SMILES OC(COC1=CC=C(Cl)C=C1Cl)=O ChemSpider 1441 ID Properties Molecular C H Cl O formula 8 6 2 3 Molar mass 221.04 g mol−1 Appearance white to yellow powder Melting point 140.5 °C (413.5 K) Boiling 160 °C (0.4 mm Hg) point Solubility in 900 mg/L (25 °C) water Related compounds Related 2,4,5-T, Dichlorprop compounds Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa) 2,4-Dichlorophenoxyacetic acid (2,4-D) is a common systemic herbicide used in the control of broadleaf weeds. It is the most widely used herbicide in the world, and the third most commonly used in North America.[1] 2,4-D is also an important synthetic auxin, often used in laboratories for plant research and as a supplement in plant cell culture media such as MS medium. History 2,4-D was developed during World War II by a British team at Rothamsted Experimental Station, under the leadership of Judah Hirsch Quastel, aiming to increase crop yields for a nation at war.[citation needed] When it was commercially released in 1946, it became the first successful selective herbicide and allowed for greatly enhanced weed control in wheat, maize (corn), rice, and similar cereal grass crop, because it only kills dicots, leaving behind monocots. Mechanism of herbicide action 2,4-D is a synthetic auxin, which is a class of plant growth regulators.
    [Show full text]
  • Agricultural Monitoring Program
    Groundwater Protection Program 918 E Divide Ave, Bismarck ND 58501 701-328-5210 | https://deq.nd.gov Pesticides Monitored in North Dakota as a Part of the Agricultural Groundwater Monitoring Program Updated January 2021 Key: Pesticide Type Use Restrictions Controls Abbreviations Not Restricted in Broadleaf MCL – Maximum Fungicide Insects North Dakota Weeds Contaminant Level Woody HAL – Health Advisory Herbicide Restricted Use Mites Level Plants PAL – Prevention Action Insecticide Not Registered Grasses Fungi Level (25% MCL/HAL) NE – Not Established Banned in the Weeds Degradate µg/L – Micrograms per United States (General) Liter Maximum Contaminant Levels are set by United States Environmental Protection Agency for public drinking water systems. Health Advisory Levels are set by the United States Environmental Protection Agency for lifetime exposure to the chemical. Prevention Action Levels are concentrations that trigger action to prevent further contamination; the level is defined as 25% of the MCL/HAL in the North Dakota Pesticide State Management Plan. Listed trade names are not a comprehensive list. Listing of any trade names does not imply endorsement of the product. Listed pesticide uses are non-exhaustive and largely based on historical use in North Dakota. This information is not to be used in place of advice from a licensed pesticide vendor. Use restrictions are subject to change. Data from the United States Environmental Protection Agency, United States Geological Survey, North Dakota Department of Agriculture, and the National
    [Show full text]
  • Thickening Glyphosate Formulations
    (19) TZZ _T (11) EP 2 959 777 A1 (12) EUROPEAN PATENT APPLICATION (43) Date of publication: (51) Int Cl.: 30.12.2015 Bulletin 2015/53 A01N 57/20 (2006.01) A01N 25/30 (2006.01) A01P 13/00 (2006.01) (21) Application number: 15175726.7 (22) Date of filing: 17.08.2009 (84) Designated Contracting States: (71) Applicant: Akzo Nobel N.V. AT BE BG CH CY CZ DE DK EE ES FI FR GB GR 6824 BM Arnhem (NL) HR HU IE IS IT LI LT LU LV MC MK MT NL NO PL PT RO SE SI SK SM TR (72) Inventor: ZHU, Shawn Stormville, NY New York 12582 (US) (30) Priority: 19.08.2008 US 90010 P 09.09.2008 EP 08163910 (74) Representative: Akzo Nobel IP Department Velperweg 76 (62) Document number(s) of the earlier application(s) in 6824 BM Arnhem (NL) accordance with Art. 76 EPC: 11191518.7 / 2 425 716 Remarks: 09781884.3 / 2 315 524 This application was filed on 07-07-2015 as a divisional application to the application mentioned under INID code 62. (54) THICKENING GLYPHOSATE FORMULATIONS (57) The present invention generally relates to a glyphosate formulation with enhanced viscosity, said formulation containing a thickening composition comprising at least one nitrogen- containing surfactant. EP 2 959 777 A1 Printed by Jouve, 75001 PARIS (FR) EP 2 959 777 A1 Description FIELD OF THE INVENTION 5 [0001] The present invention relates to a glyphosate formulations thickened by nitrogen containing surfactants. BACKGROUND OF THE INVENTION [0002] Glyphosate is the most widely used herbicide in the world.
    [Show full text]
  • Ingleby Prohibited Pesticides May 2018
    1[5] INGLEBY PROHIBITED PESTICIDES MAY 2018 Active ingredient Type Acaricides Cyhexatin Acaricide Parathion-ethyl Acaricide/Insecticide Tetradifon Acaricide Tebufenpyrad Acaricide Fumigants 1,2-Dibromoethane Fumigant 1,2-dichloroethane Fumigant Fungicides 2-Aminobutane (aka sec-butylamine) Fungicide Allyl alcohol Fungicide Benomyl Fungicide Binapacryl Fungicide Bitertanol Fungicide Blasticidin-S Fungicide Cadmium Fungicide Captafol Fungicide Chloranil Fungicide Chloromethoxypropyl-mercuric-acetate (CPMA) Fungicide Chlozolinate Fungicide Di(phenylmercury)dodecenylsuccinate (PMDS) Fungicide Diammonium ethylenebis Fungicide DNOC Fungicide / Herbicide /Insecticide Edifenphos Fungicide Fenarimol Fungicide Fentin acetate Fungicide Flusilazole Fungicide Hexachlorobenzene (HCB) Fungicide Hexaconazole Fungicide Iminoctadine Fungicide Leptophos Fungicide Maneb Fungicide Mercuric oxide Fungicide Mercurous chloride (calomel) Fungicide Mercury compounds Fungicide Nickel bis Fungicide Nuarimol Fungicide Oxadixyl Fungicide Penconazole Fungicide Ingleby Farms & Forests May 2018 Prohibited Active Ingredients 2[5] INGLEBY PROHIBITED PESTICIDES MAY 2018 Active ingredient Type Fungicides (continued) Phenylmercury acetate Fungicide/Herbicide Phenylmercuric oleate [PMO] Fungicide Prochloraz Fungicide Procymidone Fungicide Propineb Fungicide Pyrazophos Fungicide Pyrifenox Fungicide Tecnazene Fungicide Tricyclazole Fungicide Tridemorph Fungicide Vinclozolin Fungicide Zineb Fungicide Herbicides 2,4,5-T Herbicide Acifluorfen Herbicide Alachlor Herbicide Arsenic
    [Show full text]
  • 12 Chemical Fact Sheets
    1212 ChemicalChemical factfact sheetssheets A conceptual framework for Introduction implementing the Guidelines (Chapter 1) (Chapter 2) he background docudocu-- ments referred to in FRAMEWORK FOR SAFE DRINKING-WATER SUPPORTING Tments referred to in INFORMATION thisthis chapterchapter (as the princi-princi- Health-based targets Public health context Microbial aspects pal reference for each fact (Chapter 3) and health outcome (Chapters 7 and 11) sheet) may be found on Water safety plans Chemical aspects (Chapter 4) (Chapters 8 and 12) thethe Water, Sanitation, HyHy-- System Management and Radiological Monitoring giene and Health web site assessment communication aspects at http://www.who.int/ (Chapter 9) Acceptability Surveillance water_sanitation_health/ aspects (Chapter 5) dwq/chemicals/en/indewater-quality/guidelines/x. (Chapter 10) htmlchemicals/en/. A complete. A complete list of rlist eferences of references cited citedin this in Application of the Guidelines in specic circumstances chapter,this chapter, including including the (Chapter 6) background documents Climate change, Emergencies, Rainwater harvesting, Desalination forfor each cchemical, hemical, is pro-pro- systems, Travellers, Planes and vided in Annex 22.. ships, etc. 12.1 Chemical contaminants in drinking-water Acrylamide Residual acrylamideacrylamide monomermonomer occursoccurs inin polyacrylamidepolyacrylamide coagulantscoagulants used used in in thethe treattreat-- ment of drinking-water. In general, thethe maximummaximum authorizedauthorized dosedose ofof polymerpolymer isis 11 mg/l. mg/l. At a monomer content of 0.05%, this corresponds to a maximum theoretical concen-- trationtration ofof 0.5 µg/l of the monomer in water.water. Practical concentrations maymay bebe lowerlower byby aa factor factor of 2–3. This applies applies to to thethe anionic anionic and and non-ionic non-ionic polyacrylamides, polyacrylamides, but but residual residual levelslevels fromfrom cationic polyacrylamides maymay bebe higher.higher.
    [Show full text]
  • Highly Specific Nanobody Against Herbicide 2,4
    Science of the Total Environment 753 (2021) 141950 Contents lists available at ScienceDirect Science of the Total Environment journal homepage: www.elsevier.com/locate/scitotenv Highly specific nanobody against herbicide 2,4-dichlorophenoxyacetic acid for monitoring of its contamination in environmental water Zhen-Feng Li a,e, Jie-Xian Dong a,e, Natalia Vasylieva a, Yong-Liang Cui b, De-Bin Wan a, Xiu-De Hua c, Jing-Qian Huo d, Dong-Chen Yang d, Shirley J. Gee a, Bruce D. Hammock a,⁎ a Department of Entomology and UCD Comprehensive Cancer Center, University of California, Davis, California 95616, United States b Ministry of Agriculture, Citrus Research Institute, Southwest University, Chongqing 400712, PR China. c College of Plant Protection, Nanjing Agricultural University, Nanjing 210095, PR China d College of Plant Protection, Agricultural University of Hebei, Baoding 071001, PR China e Guangzhou Nabo Antibody Technology Co. Ltd, Guangzhou 510530, PR China HIGHLIGHTS GRAPHICAL ABSTRACT • Reliable step-wise workflow for anti- hapten nanobody discovery was pre- sented. • Highly specific and sensitive nanobody against 2,4-D was obtained by opti- mized isolation procedure. • A sensitive one-step FLEIA for 2,4-D was developed based on nanobody-AP fu- sion protein. • The assay showed to be useful and ap- plicable for monitoring 2,4-D pollution in environmental water. article info abstract Article history: 2,4-dichlorophenoxyacetic acid (2,4-D), a widely used herbicide, is a small organic chemical pollutant in the en- Received 15 July 2020 vironment. To develop a nanobody-based immunoassay for monitoring trace levels of 2,4-D, a step-wise strategy Received in revised form 22 August 2020 for the generation of nanobodies highly specific against this small chemical was employed.
    [Show full text]
  • Recommended Classification of Pesticides by Hazard and Guidelines to Classification 2019 Theinternational Programme on Chemical Safety (IPCS) Was Established in 1980
    The WHO Recommended Classi cation of Pesticides by Hazard and Guidelines to Classi cation 2019 cation Hazard of Pesticides by and Guidelines to Classi The WHO Recommended Classi The WHO Recommended Classi cation of Pesticides by Hazard and Guidelines to Classi cation 2019 The WHO Recommended Classification of Pesticides by Hazard and Guidelines to Classification 2019 TheInternational Programme on Chemical Safety (IPCS) was established in 1980. The overall objectives of the IPCS are to establish the scientific basis for assessment of the risk to human health and the environment from exposure to chemicals, through international peer review processes, as a prerequisite for the promotion of chemical safety, and to provide technical assistance in strengthening national capacities for the sound management of chemicals. This publication was developed in the IOMC context. The contents do not necessarily reflect the views or stated policies of individual IOMC Participating Organizations. The Inter-Organization Programme for the Sound Management of Chemicals (IOMC) was established in 1995 following recommendations made by the 1992 UN Conference on Environment and Development to strengthen cooperation and increase international coordination in the field of chemical safety. The Participating Organizations are: FAO, ILO, UNDP, UNEP, UNIDO, UNITAR, WHO, World Bank and OECD. The purpose of the IOMC is to promote coordination of the policies and activities pursued by the Participating Organizations, jointly or separately, to achieve the sound management of chemicals in relation to human health and the environment. WHO recommended classification of pesticides by hazard and guidelines to classification, 2019 edition ISBN 978-92-4-000566-2 (electronic version) ISBN 978-92-4-000567-9 (print version) ISSN 1684-1042 © World Health Organization 2020 Some rights reserved.
    [Show full text]
  • Studies on Rubber Vine (Cryptostegia Grandiflora): III Basal Bark Application of Phenoxyalkanoic Acid Herbicides
    6 Australian Weeds Dec. 1981 Studies on rubber vine (Cryptostegia grandiflora): furfuryl ester; picloram as the acid. and triclopyr as the ethyleneglycol but yl et her III Basal bark application of phenoxyalkanoic acid (EGBE) ester (as Doweo 233. M 4021 ). herbicides Trial I The eight herbicide esters and one oil -soluble acid formulation listed G. J. Harvey in Table I all di ssolved in diesel distillate Department of Land s, Sherwood, Oueensland 4075 at 5% and 2% a.e. concentrations with and without 1% dibutyJ phthalate. were applied in 10-microlitre droplets to the basal 2.5 cm of stem of 1600 rubber vine seedlings. Four diese l distillate controls. al so with and without 1% dibutyl phthal­ ate. were included . The experimental design was a ran­ Summary Materials and methods domi zed block design with 40 treatme nt s (8 herbicid es x 2 conce ntrations + 4 Rubber vine (Cryptostegia gralldif/ora) Rubber vi ne seedli ngs were grown in a diesel distillate controls x 2 factors. with is a serious weed of grazing lands in glasshouse in individual nursery seedling and without 1% dib utyl phthalate). fi ve north Queensland. A research pro­ tubes (7 cm hi gh x 4.5 em diameter) replicates and ten plants per pl ol. Treat­ gramme aimed at improving existing using commercial potting mixes. Freshly­ ment s were assessed four months after recommendations for chemical con­ collected rubber vine seed has a germi­ application, by whi ch time those plants trol of rubber vine was commenced in nation rate greater than 95%.
    [Show full text]
  • Are Your Weed-Control Products Damaging Nearby Vineyards?
    OREGON STATE UNIVERSITY EXTENSION SERVICE Are Your Weed-control Products Damaging Nearby Vineyards? Michael Kennedy and Patty Skinkis Grapes are becoming an increasingly important crop in Oregon. There are more than 22,000 acres of vineyard planted in the state, from the Willamette Valley south to Medford and Ashland, along the Columbia Gorge, and into the Milton-Freewater area. There is also a small but growing interest in counties of Central Oregon. The farm gate value (the price of grapes when sold by the farm) is nearly $130 million annually, making grape production a significant agricultural commodity in the state. Over the past decade, grape growers have become increasingly concerned that herbicides used by homeowners will drift into their vineyards and damage their vines. Photo: Michael Kennedy, © Oregon State University Herbicides can cause significant damage to Figure 1. Herbicide products that contain active ingredients grapevines. Grapevine growth can be stunted and fruit known to cause damage to grapevines can be found at hardware stores, garden centers and other retailers. They may be effective yields lost due to certain active ingredients found in at controlling weeds in your home garden or landscape but weed-killer products. With the Oregon grape industry should be used with caution, particularly around vineyards, or growing rapidly near urban boundaries throughout the avoided all together. The photo above features four products that contain herbicides that can damage grapevines. state, herbicides used in home gardens and residential and urban landscapes can cause serious damage to local vineyards. drift can occur whenever the vine is green and growing (March through October).
    [Show full text]
  • The Safety of the Herbicides 2, 4-D and 2, 4
    Forestry Commission ARCHIVE © Crown copyright 1977 First published 1977 ISBN 0 11 710149 4 THE SAFETY OF THE HERBICIDES 2,4-D AND 2,4,5-T D. J. TURNER, B.Sc., Ph. D. Agricultural Research Council Weed Research Organization LONDON: HER MAJESTY’S STATIONERY OFFICE CONTENTS 4 INTRODUCTION 5 The historical background 5 2.4-D and 2,4,5-T as herbicides 5 2.4-D and 2,4,5-T as defoliants 7 The side effects of the defoliation programme 9 The present situation 9 Civil uses of defoliants 10 THE PROPERTIES, MANUFACTURE, MODE OF ACTION AND 10 USES OF 2,4-D and 2,4,5-T Chemical and physical properties 10 The manufacture of 2,4-D and 2,4,5-T 14 Formulation ingredients 14 The mode of action of the herbicides 14 The choice of 2,4-D and 2,4,5-T formulations 16 The practical use of 2,4-D and 2,4,5-T for woody plant control 18 Overall foliage sprays Dormant shoot sprays Basal bark sprays Cut-bark and cut-stump treatments 19 THE EFFECTS OF 2,4-D AND 2,4,5-T ON DOMESTIC LIVESTOCK 20 AND ON MAN Acute effects of 2,4-D and 2,4,5-T on animals 21 Chronic (subacute) effects of 2,4-D and 2,4,5-T on animals 22 The effects of 2,4-D and 2,4,5-T on humans 22 2.4-D and 2,4,5-T in animal products 23 2.4-D and 2,4,5-T residues in crops and fruit 23 Indirect effects of 2,4-D and 2,4,5-T on farm livestock 24 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) 24 Teratogenic effects of 2,4-D and 2,4,5-T 26 THE EFFECTS OF 2,4-D AND 2,4,5-T ON OTHER LAND ORGANISMS 27 AND THE PERSISTENCE OF THESE COMPOUNDS IN TERRESTRIAL ENVIRONMENTS The effects of 2,4-D and 2,4,5-T on higher plants 28
    [Show full text]
  • NEWS 02 2020 ENG.Qxp Layout 1
    Polymers and fluorescence Balance of power 360° drinking water analysis trilogy Fluorescence spectroscopy LCMS-8060NX: performance of industrial base polymers and robustness without Automatic, simultaneous and compromising sensitivity rapid analysis of pesticides and speed CONTENT APPLICATION »Plug und Play« disease screening solution? – The MALDI-8020 in screening for Sickle Cell Disease 4 Customized software solutions for any measurement – Macro programming for Shimadzu UV-Vis and FTIR 8 Ensuring steroid-free food supplements – Identification of steroids in pharmaceuticals and food supplements with LCMS-8045 11 MSn analysis of nonderivatized and Mtpp-derivatized peptides – Two recent studies applying LCMS-IT-TOF instruments 18 Polymers and fluorescence – Part 2: How much fluorescence does a polymer show during quality control? 26 PRODUCTS The balance of power – LCMS-8060NX balances enhanced performance and robustness 7 360° drinking water analysis: Episode 2 – Automatic, simul- taneous and rapid analysis of pesticides in drinking water by online SPE and UHPLC-MS/MS 14 Versatile testing tool for the automotive industry – Enrico Davoli with the PESI-MS system (research-use only [RUO] instrument) New HMV-G3 Series 17 No more headaches! A guide to choosing the perfect C18 column 22 Validated method for monoclonal antibody drugs – Assessment of the nSMOL methodology in Global solution through the validation of bevacizumab in human serum 24 global collaboration LATEST NEWS Global solution through global collaboration – Shimadzu Cancer diagnosis:
    [Show full text]
  • NQA-54.0003 – Pesticide Residue Analysis by Electrospray LC-MS/MS
    Technical Datasheet Analysis Name: Pesticide Residue Analysis by Electrospray LC-MS/MS Method Number: NQA-54.0003 Scope of Application: This method is not suitable to determine black pepper, clove, cumin seed, ginger extract, ginger powder, rosemary, ground rosemary, white pepper, peppercorn, nutmeg, and oleoresin Description: QuEChERS is an extraction method for the analysis of pesticide residues in a large variety of food products. The extracts obtained by this procedure are analyzed by Electrospray ionization LC-MS/MS Sample Weight 50 g Required: Method Reference: Determination of pesticide residues using GC-MS and/or LC- MS/MS following acetonitrile extraction/partitioning and cleanup by dispersive SPE-QuEChERS-method. EN 15662, November 2008. FDA Pesticide Analytical Manual Volume I. Guidance document on analytical quality control and validation procedures for pesticide residues analysis in food and feed. SANTE/11945/2015. Analytical Platform: LC/MS/MS Special Information: QL may vary based on matrix effects Some pesticides may be reported as "Not Determinable" if interferences or matrix effects prevent detection/quantitation TDS-NQA-54.0003-1 1/5/2021 Analyte Reported Alias Unit of Limit of Reproducibility Measure Quantification mg/kg ≤20% 2,4,5-T 0.01 - 0.1 2,4,5-TP Silvex, Fenoprop mg/kg 0.01 - 0.1 ≤20% 2,4-D mg/kg 0.01 - 0.1 ≤20% 2,4-DB mg/kg 0.01 - 0.1 ≤20% Abamectin mg/kg 0.01 - 0.1 ≤20% Acephate mg/kg 0.01 - 0.1 ≤20% Acequinocyl mg/kg 0.01 - 0.1 ≤20% Acetamiprid mg/kg 0.01 - 0.1 ≤20% Acibenzolar-S- mg/kg ≤20% 0.01 - 0.1 methyl
    [Show full text]