Keskkonnaminister määrus terviktekst avaldamine avaldatud 2016-12-27 RT I 2016-12-29 51 129122016051 2017-01-01 81 RT I 2020-12-18+02:00 2020 15 118122020015 2021-01-01+02:00 2023-07-13+03:00 1 2020-12-14 maarus_1_10.02.2010.xsd 118122020015 12 2023-07-10 Maret Mauer 1037349 Määruse raamskeem XML struktuuri koostamiseks Lõhnaaine esinemise hindamise kord, hindamisele esitatavad nõuded ja lõhnaaine esinemise häiringutasemed 2020-12-13 RT I 2020-12-18 2 118122020002 2021-01-01 Määrus kehtestatakse § 68 lõike 1 alusel. 1 Määruse reguleerimisala Käesoleva määrusega sätestatakse: 1 lõhnaaine esinemise hindamiseks kasutatavate mõõtmiste ja arvutuslike meetodite loetelu; 2 lõhnaaine esinemise hindamise kord; 3 lõhnaaine esinemise hindamisele esitatavad nõuded; 4 hindamismeetoditele vastavad lõhnaaine esinemise häiringutasemed ja nende kohaldamise kord. 2 Lõhnaaine esinemise hindamiseks kasutatavad meetodid 1 Õhukvaliteedi vastavust lõhnaaine esinemise häiringutasemetele hinnatakse referentsmeetodiga. 2 Referentsmeetodite nõuete täitmisel on soovitatav kasutada järgmisi meetodeid eraldi või omavahel kombineerituna: 1 standard EVS-EN 13725 „Õhukvaliteet. Lõhnaainete kontsentratsiooni määramine dünaamilise olfaktomeetria abil” või muu samaväärne rahvusvaheline või Euroopa standardiorganisatsiooni standard; 2 standardi EVS 888 „Lõhnaainete määramine välisõhus välimõõtmiste teel” rastermeetod või muu samaväärne rahvusvaheline või Euroopa standardiorganisatsiooni standard; 3 standard EVS 886-1 „Lõhnaainete hajumine atmosfääris. Osa 1: Põhialused” või muu samaväärne rahvusvaheline või Euroopa standardiorganisatsiooni standard. 3 Käesoleva paragrahvi lõike 2 punktides 1 ja 2 nimetatud meetodid peavad olema akrediteeritud mõõteseaduse kohaselt. 4 Lõhnaaine esinemise kohta indikatiivse hinnangu saamiseks võib lisaks referentsmeetoditele kasutada ka järgmisi meetodeid: 1 standardi EVS 888 „Lõhnaainete määramine välisõhus välimõõtmiste teel” hajumissuuna meetod või mõni muu samaväärne rahvusvaheline või Euroopa standardiorganisatsiooni standard; 2 standard EVS 887-1 „Lõhnade mõju ja selle hindamine. Osa 1: Lõhnahäiringu psühhomeetriline hindamine. Küsimustikud” või muu samaväärne rahvusvaheline või Euroopa standardiorganisatsiooni standard; 3 standard EVS 887-2 „Lõhnade mõju ja selle hindamine. Osa 2: Häirivate omaduste väljaselgitamine küsitluste teel” või muu samaväärne rahvusvaheline või Euroopa standardiorganisatsiooni standard; 4 elektroonilised sensorid lõhnaainete hindamiseks. 5 Käesoleva paragrahvi lõike 4 punktis 1 nimetatud standardi kasutamise korral on lõhnaaine esinemise kohta indikatiivse hinnangu saamiseks vajalik minimaalne mõõtmispäevade arv vähemalt 15% vaadeldava perioodi ööpäevade koguarvust. 3 Lõhnaaine hetkelise heitkoguse arvutuslik hindamine 1 Lõhnaaine hetkelise heitkoguse arvutuslikku hindamist kasutatakse lõhnaaine modelleerimise puhul järgmiselt: 1 loomakasvatussektori korral arvutatakse lõhnaaine hetkeline heitkogus järgmise valemiga:   Q = qi × LÜ, kus Q on lõhnaaine hetkeline heitkogus (OU/s); qi – vastava valdkonna eriheide, mis on esitatud käesoleva määruse lisas; LÜ – vastava käitise loomühikud; 2 pindallikate korral arvutatakse lõhnaaine hetkeline heitkogus järgmise valemiga:   Q = qi × S, kus Q on lõhnaaine hetkeline heitkogus (OU/s); qi – vastava valdkonna eriheide, mis on esitatud käesoleva määruse lisas; S – pindallika pindala (m²); 3 käitise spetsiifiline lõhnaaine hetkeline heitkogus (OU/s) arvutatakse järgmise valemiga:   Q = c × V_R,20, kus Q on lõhnaaine hetkeline heitkogus (OU/s); c – lõhnaaine kontsentratsioon väljuvates gaasides (OU/m³) käesoleva määruse lisa või akrediteeritud labori määratu kohaselt; V_R,20 – ventilatsiooni või emissioonigaaside mahtkulu (m³/s); 4 standardi EVS-EN 13725 (2005) kohaselt arvutatakse mahtkiirus standardtingimustel (20 ºC ja 101,3 kPa) niiske gaasi jaoks standardi ISO 10780 järgi järgmise valemiga:   V_R,20 = V_s × (273 + 20) / (273 + t) × p_s / 101,3, kus V_R,20 on mahtkiirus standardtingimustel; V_s – mahtkiirus m³/s;24.04.2017 10:53 p_s – absoluutne rõhk korstnas; t – gaaside temperatuur ºC. 2 Käesoleva määruse lisas esitatud lõhnaühikud on indikatiivsed ning käitistel on õigus oma eriheiteid täpsustada, kasutades selleks käesoleva määrusega kooskõlas olevat standardiseeritud metoodikat. 4 Lõhnaaine esinemise hindamise kord 1 Keskkonnaamet võib lõhnaaine esinemise häiringutaseme ületamise kahtluse korral kokku kutsuda eksperdirühma. RT I 2020-12-18 2 118122020002 2021-01-01 2 Eksperdirühma ei kutsuta kokku järgmistel juhtudel: 1 heiteallikas ei saa tegevuse iseloomu tõttu lõhnaainet levitada; 2 tuvastatakse õhukvaliteedi piirväärtuse ületamine või muu keskkonnakaitseloa nõuete rikkumine, mis eeldatavalt põhjustas õhukvaliteedi piirväärtuse ületamise kahtluse; 3 lõhnaaine väljutamine on seotud muu keskkonnakaitseloa nõuete rikkumisega; 4 lõhnaaine häiringutaseme ületamise kahtlus on põhjustatud sõnniku laotamisest tekkinud lõhnaaine esinemisest; 5 piirkonnas, kus kahtlustatakse lõhnaaine esinemise häiringutaseme ületamist, ei ole püsivat asustust; 6 heiteallika valdaja on koostanud lõhnaaine esinemise vähendamise kava, mis on heaks kiidetud ning Keskkonnaamet on veendunud, et kavas ette nähtud meetmed on piisavad. RT I 2020-12-18 2 118122020002 2021-01-01 3 Keskkonnaamet võib enne eksperdirühma kokkukutsumise otsuse tegemist esitada heiteallika valdajale ettepaneku koostada vabatahtlikult lõhnaaine esinemise vähendamise kava. RT I 2020-12-18 2 118122020002 2021-01-01 4 Eksperdirühma kokkukutsumise otsuses märgitakse: 1 lõhnaaine esinemise hindamise meetodi nimetus; 2 lõhnaaine esinemise hindamisel kasutatava standardi nimetus; 3 lõhnaaine esinemist hindava eksperdirühma liik; 4 lõhnaaine esinemise hindamise orienteeriv tähtaeg. 5 Eksperdirühma kokkukutsumise otsus saadetakse kaebuse esitajale ja heiteallika valdajale. RT I 2020-12-18 2 118122020002 2021-01-01 5 Lõhnaaine esinemise hindamisele esitatavad nõuded 1 Lõhnaaine esinemise hindamisel tagatakse kasutatavat hindamismeetodit kirjeldava standardi kõigi nõuete täitmine. 2 Standardi EVS 888 meetodeid kasutava eksperdirühma liige peab läbima n-butanooli tundlikkuse testimise standardi EVS-EN 13725 kohaselt. 3 Standardite EVS 888 või EVS-EN 13725 alusel lõhnaaine esinemise hindamisega tegeleva eksperdirühma liige ei tohi olla teenistus- või töösuhetes hinnatava heiteallika valdajaga ning peab olema oma hinnangutes erapooletu. 4 Lõhnaaine esinemise hindamiseks standardi EVS-EN 13725 meetodeid kasutava eksperdirühma liige peab vastama nimetatud standardis eksperdirühma liikmele esitatud nõuetele. 5 Lõhnaaine esinemise hindamiseks standardi EVS 887-1 või EVS 887-2 meetodeid kasutava eksperdirühma liige peab juhinduma ICC/ESOMARi „Turundus- ja ühiskonnauuringute läbiviimise rahvusvaheliste reeglite” (ICC/ESOMAR International Code of Marketing and Social Research Practice) nõuetest. 6 Lõhnaaine esinemise hindamise referentsmeetoditele vastavad lõhnaaine esinemise häiringutasemed ja nende kohaldamise kord 1 Lõhnaaine esinemise häiringutase on aasta lõhnatundide osakaal kogu aasta tundidest, millest alates loetakse lõhnaaine esinemine oluliseks keskkonnahäiringuks. 2 Standardit EVS 886-1 või standardi EVS 888 rastermeetodit kasutades on lõhnaaine esinemise häiringutase vastuvõtja juures 15% aasta lõhnatundidest. 3 Standardit EVS 886-1 kasutades loetakse üheks lõhnatunniks tunnikeskmise lõhnaaine kontsentratsiooni 0,25 OU/m³ ületamist. 4 Standardi EVS 888 rastermeetodit kasutades loetakse üheks lõhnatunniks ühe hindamisruudu ühes mõõtepunktis ühekordse hindamise käigus saadud positiivsete mõõtmistulemuste 51% osakaal. 7 Lõhnaaine esinemise hindamistulemuste hinnang 1 Lõhnaaine esinemise hindamistulemuse hinnang sisaldab vähemalt järgmist: 1 viide eksperdirühma kokkukutsumise aluseks olnud asjaoludele; 2 heiteallikate iseloomustus, sh heiteallikate paiknemise kirjeldus ja mõõtepunktide asukohad; 3 piirkonna meteoroloogiliste tingimuste lühikirjeldus, sh valdavad tuulesuunad; 4 lõhnaaine esinemise hindamiseks kasutatud meetod ning kinnitus, et eksperdirühma tegevus vastab käesolevas määruses sätestatud nõuetele ning tõendid selle kohta on vajaduse korral taasesitatavad; 5 lõhnaaine esinemise hindamistulemused, sh vastavus lõhnaaine esinemise häiringutasemele juhul, kui kasutati referentsmeetodit; 6 eksperdirühma lõhnaaine esinemise hindamise tulemus. 2 Keskkonnaamet saadab lõhnaaine esinemise hindamistulemuste hinnangu Keskkonnaministeeriumile, kaebuse esitajale ja heiteallika valdajale. RT I 2020-12-18 2 118122020002 2021-01-01 8 Määruse jõustumine Käesolev määrus jõustub 2017. aasta 1. jaanuaril. 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