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Home My WebLink About1987-11-25 Water Quality Report► minnesota department of health 717t.«.(Mawar**t. p.o. box 9441 minnoopoUt S5440 (6121623-SOOO November 25, 1987 Mr. unilam Farley 350 South BroMD Road Long Lake, Minneso ad ^ U—5M! Dear Mr. Farley: Enclosed are the results of analyses conducted on water samples collected from your well. The well was sampled as part of a monitoring program establish^ by the Metropolitan Landfill Abatement Act. The water samples have been analyzed for the presence of 54 volatile organic chemicals and seven Indicator parameters. Volatile organic chemicals were not detected In the samples. The concentra tions of the Indicator parameters were within the range of background water quality. He have enclosed a copy of the analysis report, and a water quality Informa tion summary. Should you wish additional Information, please contact Ron Thompson at 612/623-5264. Sincerely yours. c r. Sister Mary Madonna Ashton Commissioner of Health JMMA:RDT:cad Enclosures cc: Gordon Meyer, Minnesota Pollution Control Agency Senator Gen Olson Representative John Burger Mark Andrew, Chair, Hennepin County Board of Commissioners Hennepin County Board of Health / James Grabek, Mayor, City of Orono^'' an equal opportunity amployar - HINNESOTA DEPARTMENT OF HEALTH GROUND-WATER Form SSU-3 ITORING - VOC SAMPLE/ANALYSIS REPOff Rev. 9-« =^==^^^=^=^^^=s=s=^==sssasE:s s. sMvu liNMNiiriai Field Nell iMiNn rial I |&|9^|~7| (2d-l»r. clock) 01 0 Collectdd kf 1 Meter Sjrstea Rene (Public Syitp)____ ft«»er Met LmA uq 'UA Fav^l FeciIIty Addretf i. A (St., Rte. or P.O. ^vAU VaVctAiA VtVHfA City end Zip Code Lt>>\An^ (-dVV» SS'^SA_____ Se^njuJypd (clMCb t^ooe) Q-iTMtrteted Meter Q T Treeted Meter - Treetewnt Type. Q 0 Other Leb ludpet IA<I)4IN 1^1 bl I cI(MI SeepIMp Point Oeicripyon -QeiAfPr".r^vf jX\a csf V\ou^'e AfMljOLT* Type (chick u'one) 0T Iflitlel Seeple Q 0 Other Q C Check Seeple Leb Seiple Nuiter OeU Received Oete Confirmed Il7 0l^l5^l7 Field Oleek \hld^|qig 2.7> Split Seaple? Q »ei n N 0 0 Oete Raelyied Oete Reported r>.S w i w 0 TT t. KMRIKTU m COKOmUTIflO IMFOUTIflll i^OC'f OittcMT Q Iff 13^0 co4t vgc iCttOllt tthyl fthtr 6«nity»t tolutfif CUMAt iHMyltfif tttrihydrofvrin Mtth/1 tihyl kctont atthy1 Isobytyl kttont ethyl btnitnt o-xyltnt p*xylene chloroatthane vinyl chlerlde chloreethtne d Uhl erodi f1 yoroat thine broaoaethine dUh I oref 1 uoroat then# atihyltnt chloride illylchlerlde 1.1-dUhleretthine cl !• 1 »2*dUh!eroethy1ene le2-d1chieroethine lolol*trlch1eretthine hfoaedl chi ereaethene 2 0 l-dUh1 ore* 1-propene 1 f l*df chlore* l*propene lolp2*tr1ch1ereethylent Result (ue/l) % ^ «■ a D L (eoT quwTiruoj teoT oiieeTimDi (JSTJIMXirtQ]. U2Tj|l!QlFiaL £BTJNQl£ial la? JtfRUf'Qi Anelyieo Reouetted Code ^ Result (uo/ll□ m □ [] □ I] □ [] B[| □ [] □ []□ C3 P□ [] □ I] □ [] VOC chlorodibroaoatthine cl$-l,3-d1chloro- 1-propene 2-ch1oreethylv1nyl ether Q [] ____ 1.1.1.2- tetrach1oroethine Q [ ] l.l.2,2*tetrichloroethane Q [j pentachloroethtne 1.1.2- trUhlorotrl- fluoreethane 1 eZ-dUhlorobenitne trichiorofluoroaethane 1 • 1-dUh1oroethy1ene trans-lo2- dichloroeth/ltne chlorofora dibroaoaethane carbon tetrachloride dUhloroacetoni tri 1e 1.2*d1ch1oropropane trans*l»3*d1ch1oro* l*propene Io3*d1ch1oropropane l»lp2-tr1ch1oroethane 1.2*d1broaoethane broaofora 1•2 0 3* tr1 ch1 oropropane R § San Result (ag/1 unless Paraaeter otherwise noted) nltrate^nltrite nitrogen <L O . ^ Q •aaonia nitrogen _ _ _ JQ chloride *«>'•»• ____L id. Iron _______L 3Z tetrachloroethylene Q c ]_ _ _ _ _•_ _ chlorobenxene Q Q ] 1•3-d1chlorobenxene F 1 _ _ _ _ _ _ _ _ _ _ _._ _ _ _ _ 1•4-dlchlorobenxene C I 1nn , . □□_ _ _ _._ _ Analyses Result (ag/1 unless Reouested Code Parameter otherwise noted) □□□ specific conductance pH A.2.O._ _umho/cn. MINNESOTA DEPARTMENT OF HEALTH WATER QUALITY PARAMETERS VOLATILE ORGANIC CMEHICALS (VOC's) arc a large group of low boiling point, carbon-containing, predomi nantly manmade substances. VOC's are contained in a wide variety of industrial, commercial, and resi dential products including: cleaners, degreasers, paints, solvents, inks, and petroleum distillates. VOC's do not normally occur in groundwater. Their presence usually signifies contamination from improper use, storage, disposal, spillage or leakage cf solvents or petroleum products. VOC's vary widely in their toxicity and drinking water concentration standards. NITRATE ANO NITRITE NITROGEN is used as one of the principal indicators of water quality. Nitrate is the stable foiTn 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 than 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. AfiNMIA, a compound of nitrogen and hydrogen, is generally found in low concentrations in groundwater due to oxidation to nitrate and adsorption to soil pa*‘ticles. High concentrations of aanonia may represent oxygen depleted water or rapid introduction of ammonia 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 (recofimended guideline) for public water supplies is 2S0 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 groundwater is naturally occurring sulphates of gypsum or anhydrite. Background concentrations of sulphate in Minnesota groundwaters range from O.S mg/1 to 1300 rog/1 with a mean of 72 mg/1. The secondary drinking water standard for public water supplies is 2S0 mg/1. IRON is a commonly found constituent in groundwaters, primarily derived from weathering of soil and rocks. High concentrations can be due to corrosive water or leaching of wastes. Background concen trations in Minnesota groundwaters range f/om 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 CONOUCTANCE is a measure of the ability of water to conduct an electric current. This ability depends on the presence, concentration, and chemical state tC Wastewater and leachate typically have high concentrations of dissolved material (ions) and high specific conductance. Back ground specific conductance in Minnesota groundwaters rangi*’ SO to 2S00 micromhos per centimeter (umho/cm) with a mean of 630 iimho/cm. Specific conductance is often us?d to estimate total dissolved solids (TOS) by multiplying specific conductance by .6. The secondary drinking water standard for public water supplies is SOO mg/1 TOS. pH is a measure of the hydrogen ion activity of water. pH less than 7 represents 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 413 wells and springs sampled throughout Minnesota in the Minnesota Pollution Control Agency's Ground Walir Quality Monitoring Program. MHI) 710 tM 19R6