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Chapter I: Environmental and Regulatory Concerns at the Shooting ...

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BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> Rangesowners/oper<strong>at</strong>ors to develop a BMP programth<strong>at</strong> contains elements discussed l<strong>at</strong>er in thismanual. Contact <strong>the</strong> NRA <strong>and</strong> NSSF foradditional guidance m<strong>at</strong>erials available on leadmanagement practices.By implementing appropri<strong>at</strong>e lead management<strong>at</strong> outdoor shooting ranges, range owners <strong>and</strong>oper<strong>at</strong>ors can reduce <strong>the</strong> environmental <strong>and</strong>health risks associ<strong>at</strong>ed with lead deposition,meet legal requirements <strong>and</strong> realize quantifiablebenefits.1.1 Lead Contamin<strong>at</strong>ion’s Impacton Human Health <strong>and</strong>EnvironmentExposure RoutesHistorically, <strong>the</strong> three major sources for humanexposure to lead are lead-based paint, lead indust <strong>and</strong> soil <strong>and</strong> lead in drinking w<strong>at</strong>er.Typically, human exposure occurs throughingestion, which is <strong>the</strong> consumption of lead orlead-contamin<strong>at</strong>ed m<strong>at</strong>erials, or by inhal<strong>at</strong>ion.The main human exposure to lead associ<strong>at</strong>edwith shooting ranges is through leadcontamin<strong>at</strong>edsoil. However, o<strong>the</strong>r p<strong>at</strong>hways arediscussed below, along with lead’s detrimentaleffects on humans <strong>and</strong> animals.Lead can be introduced into <strong>the</strong> environment <strong>at</strong>shooting ranges in one or more of <strong>the</strong> followingways. Each of <strong>the</strong>se p<strong>at</strong>hways is site-specific<strong>and</strong> may or may not occur <strong>at</strong> each individualrange:• Lead oxidizes when exposed to air <strong>and</strong>dissolves when exposed to acidic w<strong>at</strong>er orsoil.• Lead bullets, bullet particles, or dissolvedlead can be moved by storm w<strong>at</strong>er runoff.• Dissolved lead can migr<strong>at</strong>e through soils togroundw<strong>at</strong>er.Lead oxidizes when exposed to air <strong>and</strong>dissolves when exposed to acidic w<strong>at</strong>er or soilWhen lead is exposed to acidic w<strong>at</strong>er <strong>and</strong>/orsoil, it breaks down by we<strong>at</strong>hering into leadoxides, carbon<strong>at</strong>es, <strong>and</strong> o<strong>the</strong>r solublecompounds. With each rainfall, <strong>the</strong>secompounds may be dissolved, <strong>and</strong> <strong>the</strong> lead maymove in solution in <strong>the</strong> storm runoff w<strong>at</strong>ers.Decreases in w<strong>at</strong>er acidity (i.e., increases in itspH) will cause dissolved lead to precipit<strong>at</strong>e out ofsolution. Lead concentr<strong>at</strong>ions in solution arereduced by this precipit<strong>at</strong>ion. At pHs above 7.5,very little lead remains in solution. Increasedtime of contact between lead <strong>and</strong> acidic w<strong>at</strong>ergenerally results in an increase in <strong>the</strong> amount ofdissolved lead in <strong>the</strong> storm runoff w<strong>at</strong>er. The fivefactors which most influence <strong>the</strong> dissolving oflead in w<strong>at</strong>er are summarized below:Annual Precipit<strong>at</strong>ion R<strong>at</strong>e - The higher <strong>the</strong>annual precipit<strong>at</strong>ion r<strong>at</strong>e, <strong>the</strong> faster <strong>the</strong> leadwe<strong>at</strong>hers. Also, during prolonged rains, <strong>the</strong>contact time between w<strong>at</strong>er <strong>and</strong> lead isincreased. In general, <strong>the</strong> higher <strong>the</strong>precipit<strong>at</strong>ion r<strong>at</strong>e, <strong>the</strong> higher <strong>the</strong> potential risk oflead migr<strong>at</strong>ion off-site in solution.pH of Rain <strong>and</strong> Surface W<strong>at</strong>er - The acidity of<strong>the</strong> rainw<strong>at</strong>er decreases as basic (alkaline)minerals in <strong>the</strong> soil are dissolved. If sufficientminerals such as calcium, magnesium, <strong>and</strong> ironare present in local soils, <strong>the</strong>n <strong>the</strong> lead mayquickly precipit<strong>at</strong>e out of solution entirely as<strong>the</strong>se o<strong>the</strong>r minerals are dissolved. The pH ofshallow surface w<strong>at</strong>er is an indic<strong>at</strong>or of <strong>the</strong>presence or absence of basic minerals in <strong>the</strong>local soil <strong>and</strong> in gravel within <strong>the</strong> stream bedsthrough which <strong>the</strong> w<strong>at</strong>er has moved. The w<strong>at</strong>erin deeper streams <strong>and</strong> lakes is more likely to becomposed of acidic rainw<strong>at</strong>er th<strong>at</strong> is notneutralized.Contact Time - The contact time betweenacidic surface w<strong>at</strong>er <strong>and</strong> lead is a factor in <strong>the</strong>amount of lead th<strong>at</strong> is dissolved. For example,lead shot deposited directly into a lake has alonger contact time <strong>the</strong>n lead shot deposited inupl<strong>and</strong> areas.Soil Cover - Organic m<strong>at</strong>erial will absorb lead<strong>and</strong> remove it from a w<strong>at</strong>er solution. The thicker<strong>the</strong> organic leaf <strong>and</strong> pe<strong>at</strong> cover on <strong>the</strong> soil, <strong>the</strong>lower <strong>the</strong> lead content in solution in w<strong>at</strong>er leaving<strong>the</strong> shot area. Organic m<strong>at</strong>erial has a strong<strong>Chapter</strong> I - Page I-2


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> Rangesability to extract lead out of solution in w<strong>at</strong>er.pH of Groundw<strong>at</strong>er - During periods of norainfall, <strong>the</strong> w<strong>at</strong>er flowing within most streamscomes from groundw<strong>at</strong>er discharging into <strong>the</strong>stream channel. Therefore, <strong>the</strong> acidity of <strong>the</strong>groundw<strong>at</strong>er affects <strong>the</strong> acidity of <strong>the</strong> surfacew<strong>at</strong>er, <strong>and</strong> hence, affects <strong>the</strong> solubility of anylead particles carried into <strong>the</strong> stream duringstorm runoff.Lead bullets, bullet particles or dissolved leadcan be moved by storm w<strong>at</strong>er runoffThe ability of w<strong>at</strong>er to transport lead is influencedby two factors: velocity of <strong>the</strong> w<strong>at</strong>er <strong>and</strong> weightor size of <strong>the</strong> lead fragment. W<strong>at</strong>er’s capacity tocarry small particles is proportional to <strong>the</strong> squareof <strong>the</strong> w<strong>at</strong>er’s velocity. Clear w<strong>at</strong>er moving <strong>at</strong> avelocity of 100 feet per minute can carry a leadparticle 10,000 times heavier than w<strong>at</strong>er moving<strong>at</strong> a velocity of 10 feet per minute. Muddy w<strong>at</strong>ercan carry even larger particles. The five factorsth<strong>at</strong> most influence velocity of runoff aredescribed below:Rainfall Intensity - The gre<strong>at</strong>er <strong>the</strong> volume ofrainfall during a short period of time, <strong>the</strong> faster<strong>the</strong> velocity cre<strong>at</strong>ed to carry <strong>the</strong> rainfall off-site.The higher <strong>the</strong> annual rainfall, <strong>the</strong> gre<strong>at</strong>er <strong>the</strong>number of periods of heavy rainfall.Topographic Slope - Generally, <strong>the</strong> steeper <strong>the</strong>topographic slope, <strong>the</strong> faster <strong>the</strong> velocity ofstormw<strong>at</strong>er runoff.Soil Type - More rainfall will soak into s<strong>and</strong>ysoils <strong>the</strong>n into clay soils. Hence, for a givenrainfall intensity, <strong>the</strong> volume of runoff will begre<strong>at</strong>er from areas underlain by clays or o<strong>the</strong>rlow permeable soils than from permeable s<strong>and</strong>ysoil.Velocity - Velocity tends to decrease as streamwidth increases. Merging streams, eddycurrents, <strong>and</strong> curves in streams are o<strong>the</strong>r factorsth<strong>at</strong> may reduce <strong>the</strong> velocity. Generally, <strong>the</strong>shorter <strong>the</strong> distance from <strong>the</strong> lead deposit to <strong>the</strong>property line, <strong>the</strong> more likely it is th<strong>at</strong> <strong>the</strong> leadfragments in suspension will be transported offsite.Veget<strong>at</strong>ive Cover <strong>and</strong> Man-made Structures -Structures such as dams <strong>and</strong> dikes reduce <strong>the</strong>w<strong>at</strong>er’s velocity <strong>and</strong> gre<strong>at</strong>ly reduce <strong>the</strong> size <strong>and</strong>weight of <strong>the</strong> lead particles <strong>the</strong> w<strong>at</strong>er can carry.Since lead particles are heavy compared to <strong>the</strong>o<strong>the</strong>r suspended particles of similar size, <strong>the</strong>yare more likely to be deposited under <strong>the</strong>influence of anything th<strong>at</strong> reduces velocity of <strong>the</strong>storm runoff. Grass <strong>and</strong> o<strong>the</strong>r veget<strong>at</strong>ionreduce runoff velocity <strong>and</strong> act as a filter toremove suspended solids from <strong>the</strong> w<strong>at</strong>er.Dissolved lead can migr<strong>at</strong>e through soils togroundw<strong>at</strong>erAcidic rainw<strong>at</strong>er may dissolve we<strong>at</strong>hered leadcompounds. A portion of <strong>the</strong> lead may betransported in solution in groundw<strong>at</strong>er bene<strong>at</strong>hl<strong>and</strong> surfaces. Groundw<strong>at</strong>er may transport leadin solution from <strong>the</strong> higher topographic areas to<strong>the</strong> lower areas such as valleys, where it isdischarged <strong>and</strong> becomes part of <strong>the</strong> surfacew<strong>at</strong>er flow. If <strong>the</strong> w<strong>at</strong>er flowing undergroundpasses through rocks containing calcium,magnesium, iron, or o<strong>the</strong>r minerals more soluble<strong>the</strong>n lead, or through minerals th<strong>at</strong> raise <strong>the</strong> pHof <strong>the</strong> w<strong>at</strong>er, <strong>the</strong>n <strong>the</strong> lead in solution may bereplaced (removed) from <strong>the</strong> solution by <strong>the</strong>seo<strong>the</strong>r metals. However, if <strong>the</strong> soil is a cleansilica s<strong>and</strong> <strong>and</strong> gravel, fractured granite, orsimilar type m<strong>at</strong>erial, <strong>the</strong>n <strong>the</strong> lead may movelong distances in solution. The factors mostlikely to affect <strong>the</strong> amount of lead carried by <strong>the</strong>groundw<strong>at</strong>er in solution are discussed below:Annual Precipit<strong>at</strong>ion - Generally, highprecipit<strong>at</strong>ion r<strong>at</strong>es result in heavy dew, morefrequent rainfall, numerous streams, shallowdepth to groundw<strong>at</strong>er, shorter distance of travel,<strong>and</strong> more rapid r<strong>at</strong>es of groundw<strong>at</strong>er flow. Also,<strong>the</strong> gre<strong>at</strong>er volumes of rainfall over geologic timeprobably have reduced <strong>the</strong> amount of calcium<strong>and</strong> o<strong>the</strong>r soluble basic minerals th<strong>at</strong> could raise<strong>the</strong> w<strong>at</strong>er pH <strong>and</strong> cause lead to precipit<strong>at</strong>e(settle) out of solution from <strong>the</strong> groundw<strong>at</strong>er.Soil Types - Clays have a high ionic leadbonding capacity <strong>and</strong> more surface area towhich <strong>the</strong> lead can bond. Also, groundw<strong>at</strong>ermovement in clay is very slow, which increases<strong>the</strong> contact time for lead to bond to <strong>the</strong> clay.<strong>Chapter</strong> I - Page I-3


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> RangesLow permeability reduces <strong>the</strong> amount ofhistorical leaching <strong>and</strong> increases <strong>the</strong> probabilityof <strong>the</strong> presence of basic (+pH increasing)minerals th<strong>at</strong> can precipit<strong>at</strong>e out of solution ingroundw<strong>at</strong>er or cause <strong>the</strong> lead to bond to <strong>the</strong>clay. All of <strong>the</strong> basic calcium <strong>and</strong> rel<strong>at</strong>edminerals generally will have been removed from<strong>the</strong> clean silica s<strong>and</strong> <strong>and</strong> gravel soils, so <strong>the</strong>lead in solution in groundw<strong>at</strong>er in <strong>the</strong>se typesoils can move long distances (miles) through<strong>the</strong> ground rel<strong>at</strong>ively unchanged.Soil Chemistry - The more basic minerals likecalcium <strong>and</strong> magnesium th<strong>at</strong> are present in soilsalong <strong>the</strong> p<strong>at</strong>hways through which <strong>the</strong>groundw<strong>at</strong>er moves, <strong>the</strong> gre<strong>at</strong>er <strong>the</strong> leadprecipit<strong>at</strong>ion (removal) r<strong>at</strong>e. Lead should movein solution only a short distance (a few feet)through a s<strong>and</strong> composed of calcium shellfragments, but could move in solution longdistances (miles) through clean quartz s<strong>and</strong>.Depth to Groundw<strong>at</strong>er - In areas ofgroundw<strong>at</strong>er discharge such as river flood plains<strong>and</strong> most fl<strong>at</strong> areas, <strong>the</strong> groundw<strong>at</strong>er surface isoften a few feet below <strong>the</strong> surface. Remember,<strong>the</strong> shorter <strong>the</strong> distance traveled, <strong>the</strong> gre<strong>at</strong>er <strong>the</strong>risk th<strong>at</strong> <strong>the</strong> lead will migr<strong>at</strong>e into <strong>the</strong>environment. Shallow depth to groundw<strong>at</strong>er isindic<strong>at</strong>ive of higher risk for lead to reach <strong>the</strong>w<strong>at</strong>er.pH of Groundw<strong>at</strong>er - Although o<strong>the</strong>r factorsinfluence solubility of lead in w<strong>at</strong>er, a good rule ofthumb is th<strong>at</strong> lead will precipit<strong>at</strong>e out of solutionwhen <strong>the</strong> pH or alkalinity of w<strong>at</strong>er is gre<strong>at</strong>er <strong>the</strong>nabout 7.5. But, lead dissolved in acidgroundw<strong>at</strong>er may travel many miles withoutchange.Health Effects of Lead Exposure on RangesLead poisoning is a serious health risk. Athigher concentr<strong>at</strong>ions, it is dangerous to peopleof all ages, leading to convulsions, coma <strong>and</strong>even de<strong>at</strong>h. At even very low concentr<strong>at</strong>ions, itis dangerous to infants <strong>and</strong> young children,damaging <strong>the</strong> developing brain <strong>and</strong> resulting inboth learning <strong>and</strong> behavioral problems. Figure 1-1 describes <strong>the</strong> effects of exposure to lead onchildren <strong>and</strong> adults.Federal, st<strong>at</strong>e <strong>and</strong> local actions, including banson lead in gasoline, paint, solder <strong>and</strong> many o<strong>the</strong>rlead-containing products, have resulted insignificant reductions in average blood-leadlevels. Despite <strong>the</strong>se advances, <strong>the</strong> number oflead-poisoned children remains alarmingly high.Children living in older homes may be exposedto lead in peeling paint or paint dust. Childrencan also come in contact with lead in soil <strong>and</strong>with lead dust carried home on <strong>the</strong> clothing ofparents.On ranges, inhal<strong>at</strong>ion is one p<strong>at</strong>hway for leadexposure since shooters are exposed to leaddust during <strong>the</strong> firing of <strong>the</strong>ir guns. Becausewind is unlikely to move heavy lead particlesvery far, airborne dust is generally considered apotential thre<strong>at</strong> only when <strong>the</strong>re are significantstructures th<strong>at</strong> block air flow on <strong>the</strong> firing line.Under such conditions, <strong>the</strong> hygiene <strong>and</strong> o<strong>the</strong>rpractices proposed by <strong>the</strong> NRA for indoorshooting ranges in <strong>the</strong>ir “Source Book” areapplicable to outdoor ranges.Range workers may also be exposed to leaddust while performing routine maintenanceoper<strong>at</strong>ions, such as raking or cleaning out bullettraps. Owners/oper<strong>at</strong>ors may want to protect<strong>the</strong>se workers by requiring <strong>the</strong>m to wear <strong>the</strong>proper protective equipment or dampening <strong>the</strong>soil prior to work.Ano<strong>the</strong>r exposure route for lead <strong>at</strong> outdoorranges is ingestion by direct contact with lead orlead particles. For example, lead particlesgener<strong>at</strong>ed by <strong>the</strong> discharge of a firearm cancollect on <strong>the</strong> h<strong>and</strong>s of a shooter. Theseparticles can be ingested if a shooter e<strong>at</strong>s orsmokes prior to washing his/her h<strong>and</strong>s aftershooting. The rel<strong>at</strong>ive risk of lead exposure topeople in a well managed facility is low.Detrimental effects due to elev<strong>at</strong>ed lead levelscan also be found in animals. Excessiveexposure to lead, primarily from ingestion, cancause increased mortality r<strong>at</strong>es in c<strong>at</strong>tle, sheep<strong>and</strong> w<strong>at</strong>erfowl. For example, w<strong>at</strong>erfowl <strong>and</strong>o<strong>the</strong>r birds can ingest <strong>the</strong> shot, mistaking it forfood or grit. W<strong>at</strong>erfowl, in particular, are highlysusceptible to lead ingestion. This is a concern<strong>at</strong> ranges where shooting occurs into or over<strong>Chapter</strong> I - Page I-4


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> RangesEffects on <strong>the</strong> Human Body from Excessive Exposure to LeadIf not detected early, children with rel<strong>at</strong>ively low levels of lead (as low as 10microgram/deciliter for children) in <strong>the</strong>ir bodies can suffer from:- damage to <strong>the</strong> brain <strong>and</strong> nervous system,- behavior <strong>and</strong> learning problems (such as hyperactivity <strong>and</strong> aggressiveness),- slowed growth,- hearing problems,- headaches, <strong>and</strong>- impairment of vision <strong>and</strong> motor skills.Adults can suffer from:- difficulties during pregnancy,- reproductive problems in both men <strong>and</strong> women (such as low birth- weight, birth defects <strong>and</strong> decreased fertility),- high blood pressure,- digestive problems,- neurological disorders,- memory <strong>and</strong> concentr<strong>at</strong>ion problems, Brain or Nerve Damage- muscle <strong>and</strong> joint pain, <strong>and</strong>- kidney dysfunction.Hearing ProblemsSlowed GrowthDigestive ProblemsLead affects <strong>the</strong>body in many waysReproductive Problems(Adults)Figure 1-1: Effects on <strong>the</strong> Human Body from Excessive Exposure to Lead<strong>Chapter</strong> I - Page I-5


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> Rangesw<strong>at</strong>er. Many of <strong>the</strong> legal <strong>and</strong> government actionsth<strong>at</strong> have been brought against ranges arebased on elev<strong>at</strong>ed levels of lead, <strong>and</strong> increasedmortality in w<strong>at</strong>erfowl. For example, in one case,an upl<strong>and</strong> area of a range became a temporarypond after a thunderstorm. W<strong>at</strong>erfowl used <strong>the</strong>pond to feed <strong>and</strong> shortly <strong>the</strong>reafter, <strong>the</strong>re was aw<strong>at</strong>erfowl die-off (increase in bird mortality),apparently from lead ingestion.1.2 Legal Requirements & CourtRulingsTo d<strong>at</strong>e, most litig<strong>at</strong>ion concerns are <strong>at</strong> shotgunranges where <strong>the</strong> shotfall zone impacts w<strong>at</strong>er orwetl<strong>and</strong> areas. The potential environmental <strong>and</strong>human health risks are gre<strong>at</strong>er <strong>at</strong> <strong>the</strong>se ranges.However, all ranges, including those not loc<strong>at</strong>ednear w<strong>at</strong>er bodies, may be subject to legal <strong>and</strong>government action if proper range managementprograms are not implemented. Range owners/oper<strong>at</strong>ors should expect gre<strong>at</strong>er scrutiny asranges become more visible to regul<strong>at</strong>ors,environmental groups <strong>and</strong> <strong>the</strong> general public.Citizen groups have been <strong>the</strong> driving forcebehind most legal actions taken against outdoorranges. These groups have sued range owners/oper<strong>at</strong>ors under federal environmental laws. Twoof EPA’s most comprehensive environmentallaws, <strong>the</strong> Resource Conserv<strong>at</strong>ion <strong>and</strong> RecoveryAct (RCRA) <strong>and</strong> <strong>the</strong> Clean W<strong>at</strong>er Act (CWA),specifically provide citizens with <strong>the</strong> right to suein cases in which <strong>the</strong> environment <strong>and</strong> humanhealth are thre<strong>at</strong>ened. These citizen suits havebeen highly effective in changing <strong>the</strong> way rangesoper<strong>at</strong>e, even when out-of-court settlementshave been reached. The decisions of <strong>the</strong> UnitedSt<strong>at</strong>es Court of Appeals for <strong>the</strong> Second Circuit inRemington Arms <strong>and</strong> New York Athletic Club seta legal precedent in <strong>the</strong> applic<strong>at</strong>ion of RCRA<strong>and</strong>/or <strong>the</strong> CWA to outdoor ranges. Leadmanagement programs <strong>at</strong> outdoor ranges mustcomply with both laws. Actions have also beentaken under <strong>the</strong> Comprehensive <strong>Environmental</strong>Response, Compens<strong>at</strong>ion <strong>and</strong> Liability Act(CERCLA) commonly know as Superfund.St<strong>at</strong>e <strong>and</strong> local st<strong>at</strong>utes <strong>and</strong> regul<strong>at</strong>ions mayalso apply. To ensure environmental laws arebeing followed, range owners/oper<strong>at</strong>ors mustunderst<strong>and</strong> <strong>the</strong> legal issues <strong>and</strong> requirements.1.2.1 Resource Conserv<strong>at</strong>ion <strong>and</strong>Recovery Act (RCRA)RCRA provides <strong>the</strong> framework for <strong>the</strong> n<strong>at</strong>ion’ssolid <strong>and</strong> hazardous waste managementprogram. Under RCRA, EPA developed a“cradle-to-grave” system to ensure <strong>the</strong>protection of human health <strong>and</strong> <strong>the</strong> environmentwhen gener<strong>at</strong>ing, transporting, storing, tre<strong>at</strong>ing<strong>and</strong> disposing of hazardous waste. RCRApotentially applies to many phases of rangeoper<strong>at</strong>ion because lead bullets/shot, ifab<strong>and</strong>oned, may be a solid <strong>and</strong>/or a hazardouswaste <strong>and</strong> may present an actual or potentialimminent <strong>and</strong> substantial endangerment.Connecticut Coastal Fishermen’sAssoci<strong>at</strong>ion v. Remington Arms Company, etal.In <strong>the</strong> l<strong>at</strong>e 1980s, <strong>the</strong> Connecticut CoastalFishermen’s Associ<strong>at</strong>ion filed a lawsuit againstRemington Arms Company as <strong>the</strong> owner of <strong>the</strong>Lordship Gun Club. The Lordship Gun Club(a.k.a. Remington Gun Club) is a 30-acre site inStr<strong>at</strong>ford, Connecticut, loc<strong>at</strong>ed on <strong>the</strong> LongIsl<strong>and</strong> Sound <strong>at</strong> <strong>the</strong> mouth of <strong>the</strong> Hous<strong>at</strong>onicRiver. In <strong>the</strong> mid-1960s, <strong>the</strong> Lordship Gun Clubwas reconstructed to its final configur<strong>at</strong>ion of 12combined trap <strong>and</strong> skeet fields <strong>and</strong> oneadditional trap field. Over <strong>the</strong> years, <strong>the</strong>Lordship Gun Club became known as one of <strong>the</strong>premier shooting facilities on <strong>the</strong> East Coast.The Connecticut Coastal Fishermen’sAssoci<strong>at</strong>ion filed a lawsuit, alleging th<strong>at</strong> lead shot<strong>and</strong> clay targets are hazardous waste underRCRA. The Complaint alleged th<strong>at</strong> because <strong>the</strong>lead shot <strong>and</strong> clay targets were hazardouswastes, <strong>the</strong> gun club was a hazardous wastestorage <strong>and</strong> disposal facility subject to RCRArequirements. The plaintiff also sought civilpenalties <strong>and</strong> <strong>at</strong>torney’s fees.Remington moved for a summary judgmentdismissing <strong>the</strong> complaint, <strong>and</strong> <strong>the</strong> ConnecticutCoastal Fisherman’s Associ<strong>at</strong>ion cross-movedfor a partial summary judgment on <strong>the</strong> issue ofliability. On September 11, 1991, <strong>the</strong> UnitedSt<strong>at</strong>es District Court for <strong>the</strong> District ofConnecticut ruled on <strong>the</strong> case.<strong>Chapter</strong> I - Page I-6


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> RangesRegarding <strong>the</strong> plaintiff’s claims under RCRA, <strong>the</strong>District Court ruled in favor of <strong>the</strong> ConnecticutCoastal Fishermen’s Associ<strong>at</strong>ion, holding th<strong>at</strong><strong>the</strong> lead shot <strong>and</strong> clay targets were “discardedm<strong>at</strong>erials” <strong>and</strong> were “solid waste;” <strong>the</strong>refore, <strong>the</strong>m<strong>at</strong>erials were subject to regul<strong>at</strong>ion underRCRA. The court fur<strong>the</strong>r st<strong>at</strong>ed th<strong>at</strong> <strong>the</strong>discharged lead shot was a “hazardous waste,”but declined to rule on whe<strong>the</strong>r <strong>the</strong> clay targetfragments were also hazardous waste.Remington petitioned <strong>the</strong> United St<strong>at</strong>es Court ofAppeals for <strong>the</strong> Second Circuit Court to review<strong>the</strong> lower court’s ruling.On June 11, 1992, both parties presented oralarguments before <strong>the</strong> court. Subsequent to oralarguments, <strong>the</strong> appell<strong>at</strong>e court requested th<strong>at</strong>EPA file an amicus brief “addressing whe<strong>the</strong>rlead shot <strong>and</strong> clay target debris deposited onl<strong>and</strong> <strong>and</strong> in <strong>the</strong> w<strong>at</strong>er in <strong>the</strong> normal course oftrap <strong>and</strong> skeet shooting is ‘discarded m<strong>at</strong>erial’...so as to constitute ‘solid waste’ under RCRA.”On March 29, 1993, <strong>the</strong> United St<strong>at</strong>es Court ofAppeals for <strong>the</strong> Second Circuit reached itsdecision. With respect to RCRA, <strong>the</strong> court bothreversed <strong>and</strong> affirmed <strong>the</strong> lower court’s opinionin part.Briefly, <strong>the</strong> decision affects currently oper<strong>at</strong>ing<strong>and</strong> future gun clubs, <strong>and</strong> <strong>the</strong> following keypoints are of primary concern:1. With respect to RCRA, <strong>the</strong> court agreedwith EPA’s amicus brief, which had argued th<strong>at</strong><strong>the</strong> gun clubs are not subject to RCRA’sregul<strong>at</strong>ory (as opposed to st<strong>at</strong>utory)requirements. In o<strong>the</strong>r words, gun clubs are notviewed as facilities th<strong>at</strong> manage hazardouswastes subject to RCRA regul<strong>at</strong>ions <strong>and</strong>, assuch, do not require RCRA permits.2. Ano<strong>the</strong>r argument in <strong>the</strong> EPA’s amicusbrief with which <strong>the</strong> court agreed was <strong>the</strong> viewth<strong>at</strong> <strong>the</strong> RCRA st<strong>at</strong>ute allows citizen suits to bebrought if a gun club’s shooting activities posean “imminent <strong>and</strong> substantial endangerment tohealth or <strong>the</strong> environment.” Although gun clubsare not subject to RCRA regul<strong>at</strong>ions, EPA orany st<strong>at</strong>e, municipality, or citizen group can takelegal action under <strong>the</strong> st<strong>at</strong>utory provisions ofRCRA against gun clubs for actual or potentialenvironmental damage occurring during, or evenafter, <strong>the</strong> oper<strong>at</strong>ion of <strong>the</strong> club. Under RCRA,<strong>the</strong> plaintiff would be eligible to recover its legalfees as well.3. The court concluded th<strong>at</strong> lead shot <strong>and</strong>clay targets meet <strong>the</strong> st<strong>at</strong>utory definition of solidwaste because <strong>the</strong>se m<strong>at</strong>erials were “discarded(i.e. ab<strong>and</strong>oned)” <strong>and</strong> “left to accumul<strong>at</strong>e longafter <strong>the</strong>y have served <strong>the</strong>ir intended purpose.”Fur<strong>the</strong>r, <strong>the</strong> court concluded th<strong>at</strong> based upontoxicity testing <strong>and</strong> evidence of leadcontamin<strong>at</strong>ion, <strong>the</strong> lead shot was a hazardouswaste subject to RCRA.The important point to consider here is th<strong>at</strong> iflead shot <strong>and</strong> clay target debris are discarded(i.e. ab<strong>and</strong>oned), <strong>the</strong>se m<strong>at</strong>erials are considereda solid waste as defined in <strong>the</strong> st<strong>at</strong>ute <strong>and</strong> <strong>the</strong>facility may be subject to imminent hazardgovernmental or citizen suits.If, on <strong>the</strong> o<strong>the</strong>r h<strong>and</strong>, <strong>the</strong> discharged lead shot isrecovered or reclaimed on a regular basis, nost<strong>at</strong>utory solid waste (or hazardous waste)would be present <strong>and</strong> imminent hazard suitswould be avoided.Thus, <strong>the</strong> Remington Arms case is an importantlegal precedent. Even though regul<strong>at</strong>ions havenot been issued regarding gun club oper<strong>at</strong>ion<strong>and</strong> environmental protection, gun clubs are still<strong>at</strong> risk of legal action.Gun clubs where <strong>the</strong>re is shooting into w<strong>at</strong>er,wetl<strong>and</strong>s, rivers, creeks, <strong>and</strong> o<strong>the</strong>r sensitiveenvironments have <strong>the</strong> highest degree oflitig<strong>at</strong>ion risk. Conversely, gun clubs th<strong>at</strong> have<strong>the</strong> lowest risk of environmental litig<strong>at</strong>ion orgovernment action are those clubs th<strong>at</strong> do notshoot into w<strong>at</strong>er or wetl<strong>and</strong>s <strong>and</strong> which have anactive program to recover lead.The following describes how RCRA may applyto outdoor shooting ranges.How is Lead Shot Regul<strong>at</strong>ed UnderRCRA?Lead shot is not considered a hazardous waste<strong>Chapter</strong> I - Page I-7


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> Rangessubject to RCRA <strong>at</strong> <strong>the</strong> time it is dischargedfrom a firearm because it is used for its intendedpurpose. As such, shooting lead shot (orbullets) is not regul<strong>at</strong>ed nor is a RCRA permitrequired to oper<strong>at</strong>e a shooting range. However,spent lead shot (or bullets), left in <strong>the</strong>environment, is subject to <strong>the</strong> broader definitionof solid waste written by Congress <strong>and</strong> used insections 7002 <strong>and</strong> 7003 of <strong>the</strong> RCRA st<strong>at</strong>ute.With reference to reclaiming <strong>and</strong> recycling leadshot, <strong>the</strong> following points should serve asguidance in underst<strong>and</strong>ing RCRA <strong>and</strong> how itapplies to your range. (A more detaileddiscussion of <strong>the</strong> underlying RCRA rulesapplicable to lead shot removal <strong>at</strong> ranges isincluded in Appendix D)• Removal contractors or reclaimers shouldapply st<strong>and</strong>ard best managementpractices, mentioned in this manual, tosepar<strong>at</strong>e <strong>the</strong> lead from soil. The soil, if<strong>the</strong>n placed back on <strong>the</strong> range, is exemptfrom RCRA. However, if <strong>the</strong> soil is to beremoved off-site, <strong>the</strong>n it would requiretesting to determine if it is a RCRAhazardous waste.• Lead, if recycled or reused, is considereda scrap metal <strong>and</strong> is, <strong>the</strong>refore, excludedfrom RCRA.• Collected lead shot <strong>and</strong> bullets are excludedfrom RCRA regul<strong>at</strong>ion, <strong>and</strong> need not have amanifest, nor does a range need to obtain aRCRA gener<strong>at</strong>or number (i.e., <strong>the</strong> range isnot a hazardous waste “gener<strong>at</strong>or”), providedth<strong>at</strong> <strong>the</strong> lead is recycled or re-used. Thereclaimer does not need to be a RCRAtransporter. However, it is recommendedth<strong>at</strong> ranges retain records of shipments oflead to <strong>the</strong> receiving facilities in order todemonstr<strong>at</strong>e th<strong>at</strong> <strong>the</strong> lead was recycled.Records should also be kept whenever<strong>the</strong> lead is reused (as in reloading). Therange should be aware th<strong>at</strong> it ultim<strong>at</strong>elymay be responsible for <strong>the</strong> lead sent forreclam<strong>at</strong>ion. Therefore, only reputablereclaimers should be utilized.allow EPA, st<strong>at</strong>es or citizens to use civillawsuits, to compel cleanup of or o<strong>the</strong>r actionfor “solid waste” (e.g., spent lead shot) posingactual or potential imminent <strong>and</strong> substantialendangerment. Such actions can be soughtwhe<strong>the</strong>r <strong>the</strong> range is in oper<strong>at</strong>ion or closed,<strong>and</strong> is based solely on a determin<strong>at</strong>ion th<strong>at</strong>harm is being posed or may be posed by <strong>the</strong>range to public health <strong>and</strong>/or <strong>the</strong> environment.Since <strong>the</strong> risk of lead migr<strong>at</strong>ing increases withtime, making ranges th<strong>at</strong> have not removedlead more likely c<strong>and</strong>id<strong>at</strong>es for governmentaction or citizen lawsuits under RCRA Section7002 <strong>and</strong> 7003, ranges are advised tomaintain a schedule of regular lead removal.• With time, lead in soil can become lessdesirable to reclaimers <strong>and</strong> smelters, <strong>the</strong>rebypotentially reducing or elimin<strong>at</strong>ing financialreturns from lead removal. Moreover, suchsoil may be subject to more expensivetre<strong>at</strong>ment to separ<strong>at</strong>e <strong>the</strong> lead for recycling.• Lead removal will allow <strong>the</strong> range to: avoidcontamin<strong>at</strong>ion of <strong>the</strong> site <strong>and</strong> potential impactsto human health <strong>and</strong> <strong>the</strong> environment; reduceliability with regard to potential governmentagency or citizen suit action; <strong>and</strong>, possibly,benefit economically from <strong>the</strong> recycling oflead. Additional guidance on reclaiming leadis provided in o<strong>the</strong>r parts of this manual.• The above RCRA discussion applies to bothoper<strong>at</strong>ing <strong>and</strong> non-oper<strong>at</strong>ing ranges. Theapplic<strong>at</strong>ion of BMPs contained in this manualduring <strong>the</strong> life of <strong>the</strong> range is, of course, highlyrecommended. However, such applic<strong>at</strong>ionmay not preclude <strong>the</strong> need for remedi<strong>at</strong>ion asappropri<strong>at</strong>e, <strong>and</strong> as required by individualst<strong>at</strong>es’ regul<strong>at</strong>ions when a range ispermanently closed <strong>and</strong> or ab<strong>and</strong>oned or <strong>the</strong>l<strong>and</strong> use changes <strong>and</strong> may result in potentialexposure to soil containing lead. Generalintroductory guidance for remedi<strong>at</strong>ion can befound <strong>at</strong> www.epa.gov/epaoswer/osw orwww.epa.gov/superfund. Look under <strong>the</strong>sections “Cleanup” or “Resources,” or use <strong>the</strong>Search function.• Sections 7002 <strong>and</strong> 7003 of <strong>the</strong> RCRA st<strong>at</strong>ute<strong>Chapter</strong> I - Page I-8


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> Ranges1.2.2 - Clean W<strong>at</strong>er ActThe goal of <strong>the</strong> Clean W<strong>at</strong>er Act (CWA) is to“restore <strong>and</strong> maintain <strong>the</strong> chemical, physical,<strong>and</strong> biological integrity of <strong>the</strong> N<strong>at</strong>ion’s w<strong>at</strong>ers.”The most common alleg<strong>at</strong>ion against ranges by<strong>the</strong> EPA <strong>and</strong> citizen groups, is th<strong>at</strong> <strong>the</strong>y viol<strong>at</strong>e<strong>the</strong> CWA if <strong>the</strong>y do not have permits th<strong>at</strong> allowspent ammunition to be discharged into w<strong>at</strong>er.The CWA prohibits “<strong>the</strong> discharge of anypollutant by any person” into <strong>the</strong> w<strong>at</strong>ers of <strong>the</strong>United St<strong>at</strong>es without a N<strong>at</strong>ional PollutionDischarge <strong>and</strong> Elimin<strong>at</strong>ion System (NPDES)permit. There have been two court cases th<strong>at</strong>have applied <strong>the</strong> provisions of <strong>the</strong> CWA tocivilian shooting ranges. To underst<strong>and</strong> how <strong>the</strong>CWA can apply to shooting ranges, a summaryof <strong>the</strong> cases follows. Also see Table 1-1.To underst<strong>and</strong> <strong>the</strong> applic<strong>at</strong>ion of <strong>the</strong> CWA tooutdoor ranges, one must know <strong>the</strong> definitions ofkey terms <strong>and</strong> how <strong>the</strong>y have been applied toshooting activities. See Table 1-1.In <strong>the</strong> Remington Arms <strong>and</strong> <strong>the</strong> New YorkAthletic Club lawsuits, citizen groups argued th<strong>at</strong><strong>the</strong> defendants viol<strong>at</strong>ed <strong>the</strong> CWA by dischargingpollutants from point sources into <strong>the</strong> LongIsl<strong>and</strong> Sound without a NPDES permit.Applic<strong>at</strong>ion of <strong>the</strong> CWA requires <strong>the</strong> viol<strong>at</strong>ions tobe ongoing. Consequently, <strong>the</strong> court inRemington Arms dismissed <strong>the</strong> CWA chargeagainst <strong>the</strong> range because it had ceasedoper<strong>at</strong>ing before <strong>the</strong> lawsuit was filed.However, in <strong>the</strong> New York Athletic Club case,<strong>the</strong> club was still in oper<strong>at</strong>ion during <strong>the</strong> time oflitig<strong>at</strong>ion, but had switched to steel shot. EPA’sopinion on this case also addressed <strong>the</strong> CWAviol<strong>at</strong>ion. EPA argued th<strong>at</strong> certain trap/skeetranges can convey pollutants, via point sources,to w<strong>at</strong>er in viol<strong>at</strong>ion of <strong>the</strong> CWA if a NPDESpermit is not obtained. Although some shootingorganiz<strong>at</strong>ions have disagreed with <strong>the</strong> EPAposition, <strong>the</strong> United St<strong>at</strong>es District Court for <strong>the</strong>Sou<strong>the</strong>rn District of New York specifically foundth<strong>at</strong>:• The mechanized target throwers, <strong>the</strong>concrete shooting pl<strong>at</strong>forms, <strong>and</strong> <strong>the</strong>shooting range itself are considered pointsources as defined by <strong>the</strong> CWA;• Expended shot <strong>and</strong> target debris, includingnon-toxic shot, such as steel shot, left inw<strong>at</strong>er are pollutants as defined by <strong>the</strong> CWA.Although <strong>the</strong> New York district court’s decision in<strong>the</strong> New York Athletic Club case is notcontrolling in any o<strong>the</strong>r district, range owners<strong>and</strong> oper<strong>at</strong>ors of outdoor ranges th<strong>at</strong> shoot overor into wetl<strong>and</strong>s or o<strong>the</strong>r navigable w<strong>at</strong>ers of <strong>the</strong>United St<strong>at</strong>es should be aware of it.Based on <strong>the</strong> court’s decision in <strong>the</strong> New YorkAthletic Club case, any range whose shot,bullets or target debris enter <strong>the</strong> “w<strong>at</strong>ers of <strong>the</strong>United St<strong>at</strong>es” could be subject to permittingrequirements as well as governmental or citizensuits. “W<strong>at</strong>ers of <strong>the</strong> United St<strong>at</strong>es” or“navigable w<strong>at</strong>ers of <strong>the</strong> United St<strong>at</strong>es” arew<strong>at</strong>ers of <strong>the</strong> United St<strong>at</strong>es, including territorialseas th<strong>at</strong> include any body of w<strong>at</strong>er th<strong>at</strong> has anyconnection to, or impact on, interst<strong>at</strong>e w<strong>at</strong>ers orcommerce. The w<strong>at</strong>ers may include lakes,ponds, rivers, streams, wetl<strong>and</strong>s, or even gutsth<strong>at</strong> are frequently dry, which may not beobvious to range owners/oper<strong>at</strong>ors. Theseranges may be required to remedi<strong>at</strong>econtamin<strong>at</strong>ed sediments <strong>and</strong> soils, which couldbe both difficult <strong>and</strong> expensive, <strong>and</strong> to ceaseoper<strong>at</strong>ions over w<strong>at</strong>ers <strong>and</strong> wetl<strong>and</strong>s. It isstrongly recommended th<strong>at</strong> <strong>the</strong>se rangeschange <strong>the</strong> direction of shooting, to avoidshooting over or into wetl<strong>and</strong>s or o<strong>the</strong>rnavigable w<strong>at</strong>ers of <strong>the</strong> United St<strong>at</strong>es, <strong>and</strong>initi<strong>at</strong>e lead removal <strong>and</strong> recycling activities.In addition, <strong>the</strong>se ranges can cause asubstantial impact on wildlife <strong>and</strong> wetl<strong>and</strong>s,which range owners/oper<strong>at</strong>ors may be requiredto restore under o<strong>the</strong>r federal laws (e.g.,CERCLA, discussed below). Lead shotentering a w<strong>at</strong>er body substantially increases<strong>the</strong> potential risk of contamin<strong>at</strong>ing surface <strong>and</strong>groundw<strong>at</strong>er which, in turn, thre<strong>at</strong>ens humanhealth <strong>and</strong> <strong>the</strong> environment. Finally, as NewYork Athletic Club, Remington Arms <strong>and</strong> similarcases show, neighbors have <strong>the</strong> most leveragewhen range activity affects wetl<strong>and</strong>s <strong>and</strong>w<strong>at</strong>erways.For ranges loc<strong>at</strong>ed away from coastal areas or<strong>Chapter</strong> I - Page I-9


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> RangesTable 1-1: Applic<strong>at</strong>ion of Key Terms to New York Athletic Club<strong>Chapter</strong> I - Page I-10


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> Rangeswhose oper<strong>at</strong>ing areas are situ<strong>at</strong>ed wholly overl<strong>and</strong>, compliance with <strong>the</strong> CWA can be achievedby obtaining a NPDES permit for piped orchanneled runoff from <strong>the</strong> range into w<strong>at</strong>er 1 .<strong>Shooting</strong> ranges impacting wetl<strong>and</strong> areas maybe subject to o<strong>the</strong>r regul<strong>at</strong>ions found in Section404 of <strong>the</strong> CWA. This section is <strong>the</strong> principalfederal regul<strong>at</strong>ory program protecting <strong>the</strong>N<strong>at</strong>ion’s remaining wetl<strong>and</strong> resources. Anyplans for range owners/oper<strong>at</strong>ors to dredge <strong>and</strong>/or fill wetl<strong>and</strong>s will come under close scrutiny by<strong>the</strong> federal, st<strong>at</strong>e <strong>and</strong> local governments <strong>and</strong>citizen groups. Range owners/oper<strong>at</strong>ors mustcomply with <strong>the</strong> CWA when range design,redesign, construction, reclam<strong>at</strong>ion orremedi<strong>at</strong>ion occurs in wetl<strong>and</strong> areas.1.2.3 Comprehensive <strong>Environmental</strong>Response, Compens<strong>at</strong>ion, <strong>and</strong>Liability Act (CERCLA)The Comprehensive <strong>Environmental</strong> Response,Compens<strong>at</strong>ion, <strong>and</strong> Liability Act (CERCLA),imposes liability on past <strong>and</strong> present owners oroper<strong>at</strong>ors of properties where a release of ahazardous substance into <strong>the</strong> environmentexists. CERCLA is typically used when a party,ei<strong>the</strong>r <strong>the</strong> government or priv<strong>at</strong>e party, hascleaned up someone else’s contamin<strong>at</strong>ion, <strong>and</strong>seeks reimbursement from past owners/oper<strong>at</strong>ors or disposers (potentially responsibleparties or PRPs). Under CERCLA, lead isconsidered a hazardous substance.EPA has <strong>the</strong> authority to order a PRP to clean upa site or conduct <strong>the</strong> cleanup <strong>and</strong> recover itscosts from <strong>the</strong> PRP under CERCLA.Responsible parties may be held liable for allcleanup costs, which can be substantial. UnderCERCLA, shooting ranges may be liable forgovernment costs incurred during <strong>the</strong> cleanupof ranges, n<strong>at</strong>ural resources damages, <strong>and</strong>health assessments <strong>and</strong>/or health effectsstudies. The following two examples illustr<strong>at</strong>ehow shooting ranges (including one oper<strong>at</strong>ed by<strong>the</strong> federal government) can be affected byCERCLA.1The term “l<strong>and</strong>” in this instance refers specifically to terrainrecognized as “non-wetl<strong>and</strong>” areas.Sou<strong>the</strong>rn Lakes Trap <strong>and</strong> Skeet Club Site,Lake Geneva, Wisconsin, et al.In 1992, <strong>the</strong> US Fish <strong>and</strong> Wildlife Service(USFWS) began an investig<strong>at</strong>ion to determine<strong>the</strong> cause of de<strong>at</strong>h of over 200 Canada geese.The geese died as a result of acute leadpoisoning after ingesting lead shot, whichresearch indic<strong>at</strong>ed came from <strong>the</strong> Sou<strong>the</strong>rnLakes Trap <strong>and</strong> Skeet Club. The USFWS, in itsrole as N<strong>at</strong>ural Resource Trustee, took action torecover <strong>the</strong> cost of damage to <strong>the</strong> n<strong>at</strong>uralresources (i.e., migr<strong>at</strong>ory geese) underCERCLA. In addition, EPA pursued a separ<strong>at</strong>eaction under <strong>the</strong> Agency’s CERCLA responseauthority. The club had leased <strong>the</strong> property from<strong>the</strong> property owners to oper<strong>at</strong>e a shooting range.Shortly after EPA sent out <strong>the</strong> notice of potentialliability to <strong>the</strong> current <strong>and</strong> former owners <strong>and</strong>oper<strong>at</strong>ors of <strong>the</strong> club site, <strong>the</strong> club closedpermanently.In 1994, EPA issued an Administr<strong>at</strong>ive Order onConsent (AOC) against one current <strong>and</strong> oneformer owner of <strong>the</strong> property where <strong>the</strong> nowclosed Sou<strong>the</strong>rn Lakes Trap <strong>and</strong> Skeet Club wasloc<strong>at</strong>ed. The AOC required <strong>the</strong> owners toperform a site assessment, which included anevalu<strong>at</strong>ion of <strong>the</strong> costs to restore <strong>the</strong> wetl<strong>and</strong>s.In 1998, EPA completed activities to clean up <strong>the</strong>site <strong>and</strong> restore some of <strong>the</strong> n<strong>at</strong>ural resources<strong>and</strong> wetl<strong>and</strong>s. In a negoti<strong>at</strong>ed settlement, EPArecovered $1 million of <strong>the</strong> cost of <strong>the</strong> cleanup.Walter L. Kamb v. United St<strong>at</strong>es Coast Guard,et al.In ano<strong>the</strong>r CERCLA action, Mr. Kamb (courtappointed property guardian) sued <strong>the</strong> U.S.Coast Guard, California Highway P<strong>at</strong>rol, City ofFort Bragg, <strong>and</strong> <strong>the</strong> County of Mendocino (<strong>the</strong>defendants) for recovery of cleanup costs underCERCLA. Mr. Kamb had been appointed by <strong>the</strong>Mendocino County Superior Court to sell <strong>the</strong>property on behalf of <strong>the</strong> property owners. Theproperty was formerly used by defendants as arifle, pistol <strong>and</strong> trap range. Soil analysisindic<strong>at</strong>ed <strong>the</strong> presence of lead in <strong>the</strong> form ofleadshot, bullets, pellets, <strong>and</strong> dust. The courtfound <strong>the</strong> defendants were “responsible parties”(liable for cleanup costs) under CERCLA. No<strong>Chapter</strong> I - Page I-11


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> Rangesapportionment of liability was made <strong>and</strong> <strong>the</strong> finaldetermin<strong>at</strong>ion of each parties’ pro r<strong>at</strong>a share of<strong>the</strong> response cost was deferred.This case shows th<strong>at</strong> range activity need notaffect a w<strong>at</strong>er body to trigger CERCLA liability.CERCLA is a powerful st<strong>at</strong>utory authority th<strong>at</strong>can gre<strong>at</strong>ly impact current <strong>and</strong> former rangeowners/oper<strong>at</strong>ors. The st<strong>at</strong>ute allows forrecovery of damages to n<strong>at</strong>ural resources, <strong>the</strong>cost of any health assessment studies <strong>and</strong> allcleanup costs. Liability may extend to pastowners <strong>and</strong> oper<strong>at</strong>ors long after a range ceasesoper<strong>at</strong>ion.1.2.4 Additional Laws <strong>and</strong> Regul<strong>at</strong>ions<strong>Shooting</strong> ranges may also be subject to st<strong>at</strong>e<strong>and</strong> local laws <strong>and</strong> regul<strong>at</strong>ions. Many st<strong>at</strong>eshave adopted <strong>the</strong>ir own environmental laws,which are based on federal laws. Specifically,<strong>the</strong>se st<strong>at</strong>es have laws <strong>and</strong> regul<strong>at</strong>ions th<strong>at</strong>mirror <strong>the</strong> CWA <strong>and</strong> RCRA program laws. EPAapprovedst<strong>at</strong>e program laws must be asstringent as <strong>the</strong> federal laws <strong>and</strong> may be morestringent. Activities <strong>at</strong> shooting ranges may alsobe subject to local laws, ordinances <strong>and</strong>regul<strong>at</strong>ions addressing issues such as noise,zoning, traffic, wetl<strong>and</strong>s <strong>and</strong> nuisance. Often,citizens or neighbors of outdoor shooting rangescan initi<strong>at</strong>e noise nuisance claims againstrange owners/oper<strong>at</strong>ors. Because many st<strong>at</strong>eshave passed legisl<strong>at</strong>ion protecting ranges fromnoise nuisance lawsuits, <strong>the</strong>se may turn intoclaims of environmental viol<strong>at</strong>ions under <strong>the</strong>laws discussed above due to <strong>the</strong> presence oflead <strong>and</strong> o<strong>the</strong>r products <strong>at</strong> ranges.1.3 Benefits of MinimizingLead’s <strong>Environmental</strong> ImpactAll ranges will benefit from proactivelyimplementing successful BMP’s. Even ifrange activities currently do not cause adversepublic health <strong>and</strong> environmental impacts, bydeveloping <strong>and</strong> promoting active leadmanagement programs, ranges will benefit in <strong>the</strong>following ways:• Through a sound lead managementprogram, shooting sports enthusiasts canreduce <strong>the</strong> potential of lead exposure <strong>and</strong>contamin<strong>at</strong>ion to humans, animals <strong>and</strong> <strong>the</strong>environment.• A lead management program will result inimproved public rel<strong>at</strong>ions for <strong>the</strong> range<strong>and</strong> <strong>the</strong> shooting sports. Ranges canpromote <strong>and</strong> publicize <strong>the</strong>ir successful BMPprograms to improve <strong>the</strong>ir public image.Since many of <strong>the</strong> legal <strong>and</strong> governmentalactions begin with or are due to citizengroups, an active lead management programmay improve <strong>the</strong> public image of <strong>the</strong> rangewith <strong>the</strong>se citizen groups.• The removal of spent lead from <strong>the</strong> rangepresents a clean, well maintained facility,which will increase customer s<strong>at</strong>isfaction.• Lead is a recyclable <strong>and</strong> finite resource <strong>and</strong>can be recovered from <strong>the</strong> active portion ofranges <strong>and</strong> sold to lead reclaimers.Frequently, reclaimers do not charge rangeowners/oper<strong>at</strong>ors to recover lead fromranges, <strong>and</strong> owners <strong>and</strong> oper<strong>at</strong>ors mayreceive a percentage of <strong>the</strong> profit from <strong>the</strong>sale of reclaimed lead. This factor drivesrecycling efforts <strong>at</strong> many ranges.• By reducing or elimin<strong>at</strong>ing a potentialsource of lead migr<strong>at</strong>ion in soil, surfacew<strong>at</strong>er <strong>and</strong> groundw<strong>at</strong>er, range owners/oper<strong>at</strong>ors may avoid costly <strong>and</strong> lengthyfuture remedi<strong>at</strong>ion activities.• Finally, implementing a BMP program forlead may elimin<strong>at</strong>e or gre<strong>at</strong>ly reduce <strong>the</strong>risk of citizen lawsuits <strong>and</strong> <strong>the</strong> legal costsassoci<strong>at</strong>ed with <strong>the</strong>se lawsuits. Throughmanagement <strong>and</strong> removal practices, leadmay no longer represent a thre<strong>at</strong> upon whichcitizen lawsuits are based.Range owners/oper<strong>at</strong>ors may question whe<strong>the</strong>r<strong>the</strong> benefits of a regular <strong>and</strong> timely BMP programoutweigh <strong>the</strong> efforts of implementing <strong>and</strong>maintaining a program. The questions may ariseespecially for ranges <strong>at</strong> which shooting activitiesinvolve w<strong>at</strong>erways, since n<strong>at</strong>ional <strong>at</strong>tention hasfocused on ranges loc<strong>at</strong>ed adjacent to w<strong>at</strong>er(e.g., Remington Arms <strong>and</strong> <strong>the</strong> New York Athletic<strong>Chapter</strong> I - Page I-12


BMP for Lead <strong>at</strong> Outdoor <strong>Shooting</strong> RangesClub). However, all outdoor ranges may besubject to legal actions under RCRA <strong>and</strong>CERCLA authority. All of <strong>the</strong> benefits foradopting best management practices areavailable <strong>and</strong> worthwhile for every range owner<strong>and</strong> oper<strong>at</strong>or.The following sections provide inform<strong>at</strong>ion th<strong>at</strong>will assist <strong>the</strong> range owner or oper<strong>at</strong>or inimplementing a BMP program for recovery <strong>and</strong>recycling of lead shots <strong>and</strong> bullets.<strong>Chapter</strong> I - Page I-13


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