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Home My WebLink About1987-11-25 Water Quality ReportMINNESOTA DEPARTMENT OF HEALTH WATER QUALITY PARAMETERS VOLATILE ORGAKIC CHEMICALS (YOC*s) are a large group of low boiling point, carbon-containing, predomi nantly manTK»de substances. V0C*s are contained in a wide variety of industrial, coffiTK?rcial, and resi dential products including: cleaners, degreasers, paints, solvents, inks, and petroleum distillates. VOC's do not nonn.rlly occur in groundwater. Their presence usually signifies contamination from improper use, storage, disposal, spillage or leakage of solvents or puroleum products. VOC’s vary widely in their toxicity and drinking water concentration standards. NITRATE AND NITRITE NITROGEN is used as one of the principal indicators of water quality. Nitrate is the stable form of nitrogen in oxygenated groundwater. Nitrite presents a particular health threat to infants. Sources of nitrogen include: municipal and industrial wastes, landfill leachate, animal and human wastes, nitrogen fertilizers, decomposition of organic matter and dissolution of nitrogen- containing soil and rocks. Background concentrations* in Minnesota groundwaters range from less ihan 0.4 milligrams per liter (mg/1) to 140 mg/1 with a mean of 2.7 mg/1. A primary drinking water standard of 10 mg/1 has been established for public water supplies. AlflONIA, a compound of nitrogen and hydrogen, is generally found in low concentrations in groundwater due to oxidation to nitrate and adsorption to soil particles. High concentrations of ammonia may represent oxygen depleted water or rapid introduction of aimonia fertilizers, animal or human wastes, or leaching of solid wastes. CHLORIDE is one of the major inorganic anions in water. Chloride is very soluble and will move through groundwater with little attenuation. The presence of chloride in groundwater may be due to natural salts in soils or rocks, or leaching of chemical fertilizers, solid wastes or highway deicing salts. Background chloride concentrations in Minnesota groundwaters range from 0.3 mg/1 to 490 mg/1, with a mean of 19.2 mg/1. The secondary drinking water standard (reconmended guideline) for public water supplies is 250 mg/1. SULPHATE occurs almost universally in groundwater. Rainfall may contain 10 mg/1 or more sulphate. Household wastes, including detergents, may add 10 mg/1 or more sulphate to sewage. The usual source in 9’^oundwater is naturally occurring sulphates of gypsum or anhydrite. Background concentrations cf sulphate in Minnesota groundwaters range from 0.5 mg/1 to 1300 mg/1 with a mean of 72 mg/1. The secondary drinking water standard for public water supplies is 250 mg/1. IRON is a commonly found constituent in groundwaters, primarily derived from weathering of soil and rocks. High cc..centrations can be due to corrosive water or leaching of wastes. Background concen trations in Minnesota groundwaters range from less than 0.03 mg/1 to 46 mg/1 with a mean of 1.3 mg/1. The secondary drinking water standard for public water supplies is 0.3 mg/1. SPECIFIC CONDUCTANCE Is a measure of the ability of wat«»r to conduct an electric current. This ability depends on the presence, concentration, and chemical state of ions. Wastewater and leachate typically have high concentrations of dissolved icaterial (ions) and therefore high specific conductance. Back ground specific conductance in Minnesota groundwaters ranges from 50 to 2500 micromhos per centimeter (umho/cm) with a mean of 630 pmho/cm. Specific conductance is often used to estimate total dissolved solids (TDS) by multiplying specific conductance by .6. The secondary drinking water standard for public water supplies is 500 mg/1 TDS. pH is a measure of the hydrogen ion activity of water. pH less than 7 represent; acid conditions, pH greater than 7 represents alkaline or basic conditions. Background pH levels in Minnesota ground- waters range from 5.9 to 9.4 with a mean of 7.5. The secondary drinking water standard for public water supplies Is 6.5 to 8.5. •Background concentrations represent water quality values from 410 wells and springs sampled throughout Minnesota in the Minnesota Pollution Control Agency’s Ground Water Quality Monuonng Piogram. Mill) 710 IM I9R6 HINNESOTA DEPARTMENT OF HEALTH GROUND-HATER MONITORING - VOC SAMPLE/ANALYSIS REPORT Form SSU-3 Rev. 9-85 S. SAirtC IMFOMTIOH SlU I.D. Ntater Collection (kte 1 <2 9, N N 0 0 1 T Field Well nmt^r Jim (24-hr. clock) Uli las ColIccUd by \ \ArsUi pStCiA Water Systen Name (Public Systeai) Omer Wane TVvnv Mc I L OLv^xA ^ FacHIty Address r- 11 \ (St., Rte. or P.O. B ok ) /SO I^VC vj^lA l/c5q r\ City and Zip Code Vfy_______S S. S<T Sailpl^Type (check i^one) Q-i^ntreated Mater Q T Treated Mater - Treatment Type, Q 0 Other_______________________ SanpHng Point Description PsaTSlop. ravAf<^ S^oj\\a Analysis Type (check w^one) Initial Sample (□ 0 Other______________ Split Sample? f~) C Check Sample □ Yes Q-^Mo^ Lab Budget Niflber Lab Sample Number Date Received Date Confirmed iMNl^Jol cM I 7 O e|q 6. 0 1 ^s. 7 M M 0 0 f / M N 0 0 Y T Field Blank Number Date Analyzed ) bbNqis. OaU Refiorted M M 1 0 0 Y 1 r 1 o H j M 0 0 ^ ^ I. PAMICTEt AMO CONCCNTRATIOII INFORMATION Q^^alysls Requested - Volatile Hydrocarbon - Code 465 YOC's Detected? Q Yes pfNo Code acetone ethyl ether benzene toluene cumne m-*ylene tetrahydrofuran methyl ethyl ketone methyl Isobutyl ketone ethyl benzene o-*ylene p-xylene chloroaie thane vinyl chloride chloroethane d 1 ch 1 orod 1 f 1 uo rome'.hane broanmethane d1ch1orof1uoromethane methylene chloride allylchlorlde 1.1- dlchloroethane c1s-l,2*d1chloroethylene l,2*d1chloroethane 1.1.1- tr1chloroethane bromod1ch10romethane 2,3-d1chloro-i-propene 1.1- d1chloro-l-propene I,I,2-trichloroethylene ° s □ [] □ C]□ m□ o □□□□□□□□□□□□□□□□□□□□□□ Result (ug/l) []_________ C3_______□____ []_________□____ C]_________ C]________□____ C] [WOT QOMTIFICDl Cl [SOT OUMTIFICD] □ isoTjuMmttoi Cl [WOT OUanTIFltD] ci [WTjJUfmTJTICOl Cl rWT QUMTiriCDl Cl________□ ____□_____□_____ Cl_______ Cl_______ Cl_______ []_________ []_________m_____ Code VOC chlorodibromomethane Cl cls-l,3-d1chloro- l-propene Q 2-chloroethylviny! ether 1.1.1.2- tetrachloroethane CD 1.1.2.2- tetrachloroethane CD pentachloroethane CD 1.1.2- trlchlorotrl- fluoroethane CD 1.2- dlchlorobenzene CD trichiorofluoromethane CD 1.1- d1chloroethylene CD trans-1,2- dlchloroethylene CD chloroform CD dibromomethane Q carbon tetrachloride Q dichloroacetonitrile CD 1.2- d1chloropropane CD trans-l,3-dichloro- l-propene CD 1.3- dlchloropropane CD 1.1.2- trichloroethane CD 1.2- dlbromoethane CD bromoform Q 1.2.3- tr1chloropropane CD 1.1.2.2- tetrachloroethylene CD chlorobenzene CD 1.3- d1 chlorobenzene CD 1.4- d1chlorobenzene fD Result (uq/1) Analyses Requested □□□□□ Code Parameter Result (mg/l unless otherwise noted) i2-*=±Q.nltrate^nltrlte nitrogen <[ ammonia nitrogen _____ ^ chloride _ _ _ _ _ _C sulfate ~ZZ±-S Analyses Requested □ □□□ Code Parameter specific conductance pH Result (mg/1 unless otherwise noteo) .:z:zQ-_ _umno/c«.