KR101497504B1 - Identification of odor-causing components occurred from odor sources - Google Patents
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Abstract
본 발명은 냄새발생원에 대한 냄새유발 원인성분 규명방법에 관한 것으로, 보다 상세하게는 냄새발생원에서 발생되는 냄새물질을 비닐백에 채취하는 샘플채취 단계; 직접 관능법을 이용하여 냄새물질 종류를 확인하는 관능평가 단계; 냄새물질 종류별로 기기분석을 통해 검출성분을 확인하는 기기분석 단계; 검출성분에 대한 최소감지값을 확인하는 최소감지법 평가 단계; 및 냄새 물질로 선정된 물질만을 대상으로 샘플에서 확인된 농도와 동일한 관능평가용 샘플가스를 제조하고, 상기 제도된 가스를 샘플과의 비교 관능평가를 통해 냄새질 동일성을 평가하는 재현성 평가 단계를 포함하는 냄새발생원에 대한 냄새유발 원인성분 규명방법에 관한 것이다.The present invention relates to a method for identifying a cause component of an odor causing an odor, and more particularly, to a method for identifying a cause component of an odor causing odor, A sensory evaluation step of confirming the type of odorous substance using a direct sensory method; A device analyzing step of confirming the detected components by analyzing the devices according to the types of odorous substances; A minimum sensing method evaluation step of confirming a minimum sensing value for the detected component; And a reproducibility evaluation step of preparing a sample gas for sensory evaluation equal to the concentration confirmed in the sample only for the substance selected as the smell substance and evaluating the odor identity through comparative sensory evaluation of the structured gas with the sample And to a method for identifying the cause component of the odor from the odor source.
Description
본 발명은 냄새발생원에서 발생되는 성분들중 실제 냄새에 영향을 미치고 있는 냄새유발 원인성분 선정을 위한 보다 정확하고 용이하게 판별하기 위한 냄새평가방법에 관한 것이다.The present invention relates to an odor evaluation method for more accurately and easily discriminating an odor causing component that affects the actual odor of components generated from an odor generating source.
냄새에는 향과 같이 좋은 냄새와 하수구 냄새와 같은 불쾌한 냄새가 있다. 이러한 불쾌한 냄새를 일반적으로 악취라 한다. 우리나라의 악취방지법에서는 악취를 황화수소, 메르캅탄, 아민류 기타 자극성 있는 기체상 물질이 사람의 후각에 작용하여 불쾌감과 혐오감을 주는 냄새라고 정의하고 있다.Smells have unpleasant smells such as incense and smell like sewer. These unpleasant smells are generally called stinks. In Korea 's Anti - Odor Law, odor is defined as the smell of hydrogen sulfide, mercaptans, amines, and other irritating gaseous substances acting on the human' s smell, giving it discomfort and disgust.
냄새물질은 대기오염물질의 한 종류이며 휘발성 유기화합물(VOC)과 비슷한 특성을 갖고 있으므로 비슷하게 취급되는 경향도 있지만, 냄새는 불쾌감을 유발한다는 점이 다른 대기오염물질과의 가장 큰 차이점이다. Odorous substances are a kind of air pollutants and they are similar to volatile organic compounds (VOCs) and tend to be treated similarly, but the biggest difference is that odor causes discomfort.
현재, 우리나라의 악취방지법에 의한 지정악취물질은 총 22종 즉, 암모니아, 메틸머캅탄, 황화수소, 다이메틸설파이드, 다이메틸다이설파이드, 트라이메틸아민, 아세트알데하이드, 스타이렌, 프로피온알데하이드, 뷰티르알데하이드, n-발레르알데하이드, i-발레르알데하이드, 톨루엔, 자일렌, 메틸에틸케톤, 메틸아이소뷰티르케톤, 뷰티르아세테이트, 프로피온산, n-뷰티르산, n-발레르산, i-발레르산, i-뷰티르알코올로 관리되고 있다.At present, the designated odor substances according to the Korean Society of Odor Control Law are total 22 kinds, namely, ammonia, methyl mercaptan, hydrogen sulfide, dimethyl sulfide, dimethyl disulfide, trimethylamine, acetaldehyde, styrene, propionaldehyde, , n-valeric aldehyde, i-valeraldehyde, toluene, xylene, methyl ethyl ketone, methyl isobutyrate ketone, butylacetate, propionic acid, n-butyric acid, n- It is managed by le alcohol.
한편, 냄새물질은 육안식별이 불가능하여, 인간의 후각에 의존적인 정신적ㅇ 생리학적 스트레스를 유발하는 감각성 오염물질이다. 냄새발생원 역시 매우 다양하며 대부분 단일물질보다는 여러 화합물의 복합적 성질에 의해 발생한다. 또한 기상상태, 인간의 감각 등 여러 요인에 의해 영향을 받으므로 객관적인 측정 및 평가가 매우 어려운 오염물질이기도 하다. 따라서 냄새발생원에서 발생되는 냄새 물질의 냄새 재현성을 통해 냄새발생원에서 발생되는 냄새물질의 객관적인 측정 및 평가가 요구된다.On the other hand, odorous substances are sensory pollutants that cause mental and physiological stress that is not visually identifiable and dependent on human olfactory sense. Odorogenic sources are also very diverse and are mostly caused by the complex nature of several compounds rather than a single substance. It is also a pollutant that is very difficult to objectively measure and evaluate because it is influenced by various factors such as weather conditions and human senses. Therefore, it is necessary to objectively measure and evaluate the odorous substances generated from the odor source through the reproducibility of odor substances generated from the odor source.
이에, 본 발명의 목적은 냄새발생원별 실제 직접적인 영향을 주는 원인성분을 보다 정확하고 용이하게 판별하기 위한평가방법에 관한 것으로서, 냄새발생원에서 발생하는 냄새유발 원인성분 무엇인지를 정확히 규명하여 냄새저감 방안을 위한 기초자료로 활용하여 환경오염 및 제품의 품질향상을 도모하기 위한 것이다.Accordingly, it is an object of the present invention to provide an evaluation method for more accurately and easily discriminating causal elements that have a direct and direct effect on each odor generation source, and it is an object of the present invention to provide an evaluation method for odor reduction by accurately identifying what constitutes an odor- To improve environmental pollution and product quality.
상기 목적을 달성하기 위하여, 본 발명은 냄새발생원에서 발생되는 가스를 직접 관능법을 이용하여 냄새물질 종류를 확인하는 관능평가 단계; 냄새발생원에서 발생되는 가스를 비닐백에 채취한 후 냄새종류별 흡착 및 흡수, 또는 냄새발생원에서 발생되고 있는 가스를 직접 냄새종류별로 흡착 및 흡수하는 가스샘플 전처리 단계; 냄새물질 종류별로 기기분석을 통해 검출성분을 확인하는 기기분석 단계; 검출성분에 대한 최소감지값을 확인하는 최소감지법 평가 단계; 냄새 물질로 선정된 물질만을 대상으로 샘플에서 확인된 농도와 동일한 표준가스를 제조하고, 상기 표준가스를 샘플가스와 비교 관능평가를 통해 냄새질에 대한 동일성 여부를 판단하는 냄새재현성 평가 단계를 포함하는 냄새발생원에 대한 냄새유발 원인물질 선정 과정에 대한 평가방법을 제공한다.In order to achieve the above object, the present invention provides a sensory evaluation method, comprising: a sensory evaluation step of identifying a kind of odorous substance using a direct sensory method; A gas sample preprocessing step of collecting the gas generated from the odor generating source into a plastic bag and then adsorbing and absorbing the odor type or adsorbing and absorbing the gas generated from the odor source directly according to the type of odor; A device analyzing step of confirming the detected components by analyzing the devices according to the types of odorous substances; A minimum sensing method evaluation step of confirming a minimum sensing value for the detected component; A smell reproducibility evaluation step of preparing a standard gas which is the same as the concentration determined in the sample only for the substance selected as the smell substance and judging whether or not the standard gas is identical to the smell through the comparative sensory evaluation with the sample gas Provides an evaluation method for the odor causing agent selection process.
상기 비닐백은 폴리에스테르로 이루어진 비닐백일 수 있다.The vinyl bag may be a vinyl bag made of polyester.
상기 관능평가는 판정자 선정 단계; 원샘플 평가 단계; 무취 공기 제조 단계; 샘플 가스 제조 단계; 샘플 관능 평가 단계; 및 결과 산출 단계를 포함할 수 있다.Wherein the sensory evaluation includes a judge selecting step; A circle sample evaluation step; An odorless air production step; A sample gas production step; Sample sensory evaluation stage; And a result calculating step.
상기 기기분석에 사용된 장비는 가스크로마토그래프로 분리관 오븐의 온도 승온조작이 가능하고, 분리관 유량을 조정하여 일정하게 할 수 있다.The equipment used for the above equipment analysis can be temperature controlled by a gas chromatograph and temperature of the oven can be adjusted by adjusting the flow rate of the pipe.
상기 최소감지법 평가는 기기분석을 통해 검출된 성분을 대상으로 단일물질의 시약을 가스제조용 유리병에 주입하고 기화시켜 제조하는 1차 가스 제조 단계; 상기 1차 가스를 무취가스가 들어있는 다수의 백 중 어느 한 곳에만 일정량 주입하고 희석하는 관능평가용 샘플 제조 단계; 다수의 판정원이 냄새를 맡아 감지농도가 가장 낮고, 가장 높은 결과가 나올 때까지 평가하는 샘플 관능 평가 단계; 및 감지한계 농도가 가장 낮고, 가장 높은 판정원을 제외한 나머지 판정원을 대상으로 결과를 확인하는 최소감지값 확인 단계를 포함할 수 있다. 단 검출성분의 시약이 가스로 된 성분일 경우 1차 가스 제조 단계를 생략하여 바로 무취가스가 들어있는 백에 희석을 해서 관능평가용 샘플을 제조할 수 있다.The minimum sensing method evaluation is a primary gas manufacturing step in which a reagent of a single substance is injected into a glass bottle for gas production and vaporized to a component detected through a device analysis; Preparing a sample for sensory evaluation in which a predetermined amount of the primary gas is injected and diluted only in one of a plurality of bags containing odorless gas; A sample sensory evaluation step in which a plurality of judges smell to evaluate the lowest sensed concentration until the highest result is obtained; And a minimum sensing value confirming step of confirming a result of the determination source having the lowest detection concentration and excluding the highest determination source. If the reagent of the detection component is a gaseous component, a sample for sensory evaluation can be prepared by omitting the primary gas production step and immediately diluting it in a bag containing an odorless gas.
상기 냄새재현성 평가는 기기분석을 이용한 검출성분별 정량분석과 최소감지값 확인을 통한 냄새발생 원인성분을 추적하는 냄새발생원인 추적 단계; 실제 냄새발생원인을 확인하고, 검출성분별 농도를 이용한 관능액을 제조하는 관능액 제조 단계; 상기 관능액 일정량을 냄새발생 원인에서 발생된 농도와 유사한 범위로 샘플가스를 제조하는 샘플가스 제조 단계; 및 실제 냄새발생원인과 제조한 샘플가스를 관능으로 비교하여 실제 냄새 원인 성분을 제시하는 냄새 원인 성분 규명 단계를 포함한다.The odor reproducibility evaluation step includes a quantitative analysis for each detected component using instrumental analysis and a cause tracking step for tracking the cause of odor generation by confirming the minimum sensed value; A sensory fluid manufacturing step of identifying the cause of the actual odor generation and producing a sensory fluid using the concentration of each sensing component; A sample gas production step of producing a sample gas in a range of the predetermined amount of the sensory solution in a range similar to the concentration generated in the cause of odor generation; And a step of identifying the causative component of the odor causing physical odor causing component by comparing the cause of the actual odor with the produced sample gas sensually.
본 발명에 따른 냄새발생원에 대한 냄새유발 원인성분 규명방법은 실질적 냄새유발 원인성분을 보다 정확하고 용이하게 판별하기 위한 평가방법으로서, 특히 냄새발생원에서 발생되는 냄새의 종류에 따라 냄새저감 방안 수립과, 이에 따른 제품 효율성 향상을 도모함으로써 하여 환경오염도 방지할 수 있다.According to the present invention, there is provided a method for identifying a causative element causing odor in an odor generating source, comprising the steps of establishing an odor reduction method according to the type of odor generated in the odor generating source, Thereby improving the product efficiency, thereby preventing environmental pollution.
도 1은 관능 평가 단계를 나타낸 것이고,
도 2는 최소감지법 평가 단계를 나타낸 것이고,
도 3은 재현성 평가 단계를 나타난 것이다. Figure 1 shows the sensory evaluation step,
FIG. 2 shows a minimum sensing method evaluation step,
3 shows the reproducibility evaluation step.
이하, 본 발명에 따른 냄새 재현성 평가방법을 세부공정에 따라 보다 상세하게 설명한다. Hereinafter, the odor reproducibility evaluation method according to the present invention will be described in detail with reference to the detailed process.
1. 샘플채취 단계1. Sampling step
냄새발생원 제품과 원료에서 발생되는 성분을 채취하기 위해 냄새나 VOC가 없는 폴리에스테르로 만들어진 비닐백을 사용한다. 평가에 사용될 수 있는 백은 여러 가지 냄새 성분과의 반응이 극히 적어야 한다. 본 발명에 사용된 샘플채취용 백은 두께가 38미크론에 불과하지만 잘 찢어지지 않으며, 샘플이 강산이나 강염기가 아닌 경우 열화되지 않고, 또한 냄새를 구성하는 여러 가지 가스, 유기용제 증기, 질소, 산소, 이산화탄소 등 모든 기체에 대해 우수한 가스차단성을 갖는다. To pick up the odor origins and ingredients from the raw materials, use a plastic bag made of polyester with no odor or VOC. The bag that can be used for the evaluation should have very little reaction with various odor components. The sample collecting bag used in the present invention has a thickness of only 38 microns but does not tear easily and does not deteriorate when the sample is not a strong acid or a strong base. Further, various gases constituting the odor, organic solvent vapor, nitrogen, oxygen , Carbon dioxide, and the like.
2. 관능 평가 단계2. Sensory Evaluation Step
기체상태의 물질이 사람의 후각을 자극하여 불쾌감과 혐오감을 주는 냄새세기 및 냄새질을 측정하기 위해 적용되는 방법으로서, 전체적인 진행 과정을 도 1에 나타내었다. 기기분석법에 비해 짧은 시간에 평가할 수 있는 장점이 있지만, 냄새 시험에 참가하는 판정자별 냄새 종류에 따라 민감성이 다르고 동일한 상태의 유지관리가 어렵기 때문에 동일한 샘플에 대한 결과의 오차가 클 수 있는 단점이 있다.The overall process is shown in FIG. 1, which is a method applied to measure odor intensity and odor quality, in which a gaseous substance stimulates the nose of a person to give offensive and repulsive effects. Although there is an advantage that it can be evaluated in a short time compared with the instrumental analysis method, the sensitivity of the result to the same sample may be large because the sensitivity is different depending on the type of odor of each odorant participating in the odor test, have.
3. 기기 분석 단계3. Instrument Analysis Phase
평가 항목의 선정은 우리나라 악취방지법에서 규제하고 있는 22가지 지정악취 물질을 근거로 암모니아, 아민류, 황화합물류, 알데하이드류, 휘발성 유기화합물, 저급 지방산을 대상으로 검출성분을 확인한다. 각 성분별 평가방법을 하기 표 1에 나타내었다.The selection of the evaluation items is based on the 22 designated odor substances regulated by Korea's Anti-Odor Control Act, and identifies the detected components of ammonia, amines, sulfur compounds, aldehydes, volatile organic compounds, and lower fatty acids. The evaluation methods for each component are shown in Table 1 below.
1) 암모니아1) Ammonia
암모니아 분석은 분석용 샘플용액에 페놀-펜타시아노 니트로실 철(Ⅲ)산나트륨용액 5㎖와 차아염소산 나트륨용액 5㎖를 가하고 25 ∼ 30℃의 수욕조에서 1시간 방치 후 암모늄이온과 반응시켜 생성되는 인도페놀류의 흡광도를 측정하여 암모니아를 정량하는 방법인 인도페놀법을 이용하여 청색으로 발색시킨 후 UV/vis (CARY-50, USA)를 이용하여 640nm 파장에서 분석한다. 암모니아 분석에는 UV/vis 분광분석기(spectrophotometer)를 사용한다.Ammonia analysis was performed by adding 5 ml of phenol-pentacyano nitrosyl iron (III) sodium salt solution and 5 ml of sodium hypochlorite solution to the sample solution for analysis, allowing to stand in a water bath at 25 to 30 ° C for 1 hour and then reacting with ammonium ion The absorbance of the resulting indanthrene phenols is measured and blue color is developed using the indophenol method, which is a method of quantifying ammonia, and then analyzed at a wavelength of 640 nm using UV / vis (CARY-50, USA). A UV / vis spectrophotometer is used for ammonia analysis.
2) 트라이메틸아민2) Trimethylamine
트라이메틸아민 분석은 분석용 샘플용액을 넣은 바이알에 50% KOH 5㎖를 가하고 전처리 장비인 SPME auto sampler(MH01-00B)를 이용하여 5분 교반 후 바이알 상층부 기체층으로 트라이메틸아민이 용출되면 SPME 흡착(15분) 후 이를 가스크로마토그래피(GC/MSD)로 주입하여 분석한다. 트라이메틸아민 분석에는 GC/MSD를 사용한다.Trimethylamine analysis was performed by adding 5 ml of 50% KOH to the vial containing the sample solution for analysis. After 5 minutes of stirring using the SPME auto sampler (MH01-00B) as a pretreatment device, trimethylamine was eluted into the upper layer of the vial, After adsorption (15 min), it is analyzed by gas chromatography (GC / MSD). GC / MSD is used for the trimethylamine analysis.
3) 황화합물3) Sulfur compounds
황화합물은 펌프 내장형의 진공흡인상자(Model1062, 영화과학)와 Tedlar bag(5ℓ, 10ℓ, JAPAN)을 이용하여 측정한다. 황화합물 측정에 사용한 Tedlar bag은 측정 전 고순도 질소(99.999 %)로 3회 이상 세척하였으며, 현장샘플로 1회 이상 채우고 배기한 후 샘플을 채취한다. 샘플채취가 완료된 백은 상온(15 ∼ 25℃)의 유지와 직사광선을 피하여 보관 및 운반하며, 분석은 24시간 이내에 실시한다. Sulfur compounds are measured using a vacuum suction box (Model 1062, Film Science) and a Tedlar bag (5 L, 10 L, JAPAN) with built-in pump. The Tedlar bag used in the measurement of sulfur compounds was washed with high purity nitrogen (99.999%) three or more times before the measurement. Fill the sample bag with at least one sample, exhaust the sample, and collect the sample. After collection of samples, bags should be kept at room temperature (15 ~ 25 ℃) and kept away from direct sunlight. Analysis should be done within 24 hours.
황화합물에 선택성이 좋은 불꽃광도검출기(PFPD)가 설치된 GC(CP3800, Varian, U.S.A)를 사용하여 분석한다. 황화합물의 분석에는 GC/PFPD를 사용한다.Analyze with a GC (CP3800, Varian, U.S.A) equipped with a selective flame photometric detector (PFPD) for sulfur compounds. GC / PFPD is used for the analysis of sulfur compounds.
4) 알데하이드4) Aldehyde
알데하이드류는 카보닐화합물과 2,4-DNPH(Dinitrophenylhydrazine)와의 반응에 의해 생성되는 DNPH 유도체를 분석하는 방법으로 측정 시 알데하이드류 뿐만 아니라 케톤과도 반응하여 안정한 유도체를 형성하는 2,4-DNPH 유도체화 방법을 이용하였다. The aldehydes are 2,4-DNPH derivatives that react with carbonyl compounds and 2,4-DNPH (Dinitrophenylhydrazine) to produce DNPH derivatives, which react with not only aldehydes but also ketones to form stable derivatives. .
카보닐화합물과 2,4-DNPH와의 유도체화 반응을 통해 카보닐화합물은 안정한 2,4-DNPH hydrazone 유도체 형태로 전환되고 H2O를 부산물로 생성하게 된다. 알데하이드류 샘플채취 매체는 폴리프로필렌 튜브에 고순도로 정제된 2,4-DNPH가 코팅되어 있는 2,4-DNPH 카트리지와 알데하이드류 측정 시 방해물질로 작용하는 오존을 제거하기 위하여 2,4-DNPH 카트리지 전단부에 KI가 채워져 있는 오존 스크러버를 이용한다.Through derivatization of the carbonyl compound with 2,4-DNPH, the carbonyl compound is converted to a stable 2,4-DNPH hydrazone derivative form and H 2 O is produced as a by-product. The 2,4-DNPH cartridge coated with 2,4-DNPH purified in a high-purity polypropylene tube and the 2,4-DNPH cartridge to remove ozone, which acts as an obstacle in the measurement of aldehydes, Use an ozone scrubber filled with KI at the front end.
측정이 완료된 샘플은 내·외부가 알루미늄으로 코팅되어 있는 용기에 개별 포장하여 용매추출 전까지 4℃ 이하에서 냉장보관 하며, 아세토니트릴 2.5㎖를 사용하여 매우 느린 속도(1㎖/min)로 추출한다. 알데하이드류의 분석에는 액체크로마토그래피(HPLC)를 사용한다.After the measurement is completed, the sample is individually packaged in a container coated with aluminum. The sample is refrigerated at 4 ° C or lower before solvent extraction. Extract at very slow rate (1 ml / min) using 2.5 ml of acetonitrile. For analysis of aldehydes, liquid chromatography (HPLC) is used.
5) 휘발성 유기화합물(Volatile Organic Compounds, VOCs)5) Volatile Organic Compounds (VOCs)
휘발성유기화합물 중 냄새물질로 관리되고 있는 스타이렌(Styrene), 톨루엔(Toluene), 자일렌(Xylene), 메틸에틸케톤(MEK), 메틸아이소뷰티르케톤(MIBK), 뷰티르아세테이트(Butyl acetate), 아이소뷰틸알코올(i-Butyl alcohol) 등 7개 물질은 Tenax-TA 흡착제가 200㎎ 이상 충진되어 있는 Tenax-TA 흡착튜브(Supelco, U.S.A)를 이용하여 측정한다. Toluene, xylene, methyl ethyl ketone (MEK), methyl isobutyrate ketone (MIBK), butylacetate (Butyl acetate), which are managed as odor substances in volatile organic compounds, , And isobutyl alcohol (i-butyl alcohol) are measured using a Tenax-TA adsorption tube (Supelco, USA) filled with 200 mg or more of Tenax-TA adsorbent.
측정이 끝난 Tenax-TA 흡착튜브는 4℃ 이하에서 냉장보관 하며, GC/MSMS(3800GC /1200L, Varian, U.S.A)로 분석한다. VOCs 분석에는 GC/MS를 사용한다.The Tenax-TA adsorption tubes are stored at 4 ° C or lower and analyzed by GC / MSMS (3800 GC / 1200 L, Varian, U.S.A). GC / MS is used for VOCs analysis.
6) 유기산6) Organic acid
유기산 분석은 분석용 샘플용액을 넣은 바이알에 NaCl 2.3g 넣은 후 2% 황산 1㎖를 가하고 충분히 섞은 후 전처리 장비인 SPME auto sampler(MH01-00B)를 이용하여 교반(90℃, 20분) 후 바이알 상층부 기체층으로 유기산이 용출되면 SPME 흡착(15분) 후 이를 가스크로마토그래피(GC/MSD)로 주입하여 분석한다. 유기산 분석에는 GC/MSD를 사용한다.For the analysis of organic acids, 2.3 g of NaCl was added to the vial containing analytical sample solution, and 1 ml of 2% sulfuric acid was added. After thorough mixing, the mixture was stirred (90 ° C., 20 minutes) using SPME auto sampler (MH01-00B) When the organic acid is eluted into the upper layer of the gas layer, it is adsorbed by SPME (15 minutes) and analyzed by gas chromatography (GC / MSD). GC / MSD is used for organic acid analysis.
4. 최소감지법 평가 단계4. Minimum Sensing Method Evaluation Step
기기분석을 통해 배출구별 검출성분을 평가하고, 이들 성분에 대해 판정자가 감지할 수 있는 최소감지값을 확인하여 실제 냄새에 직접적인 영향을 주는 성분을 선정한다. 이때, 전체적인 진행 과정을 도 2에 나타내었다.By analyzing the equipment, the emission discrimination component is evaluated, and the component that directly affects the actual odor is selected by confirming the minimum sensed value that can be sensed by the judge for these components. At this time, the overall process is shown in FIG.
5. 재현성 평가 단계5. Reproducibility Evaluation Step
선정한 성분이 실제 냄새물질이 맞는지에 대한 신뢰성을 확보하기 위해 도 3와 같은 냄새 재현성 평가법을 적용한다. 즉, 냄새예상물질로 선정한 성분을 샘플에서 검출된 농도와 동일한 농도로 표준가스를 제조하고, 이를 샘플냄새와 비교하여 냄새종류가 유사한지를 평가하는 방법이다. 이를 통해 기기분석에서 검출된 성분들 중에서 실제 냄새유발 원인성분만을 제시하게 된다.The odor reproducibility evaluation method as shown in Fig. 3 is applied in order to ensure the reliability of whether the selected components are true odor substances. That is, a standard gas is prepared at a concentration equal to the concentration detected in the sample, and the odor is compared with the sample odor to evaluate whether or not the odor types are similar. Thus, only the actual odor inducing components among the components detected in the device analysis are presented.
최종적으로 이들 결과물을 근거로 가장 효율적인 냄새 저감방안을 확보하기 위한 기초자료로 활용할 수 있다.
Finally, based on these results, it can be used as the basic data for securing the most effective smell reducing method.
이상과 같이, 본 발명은 비록 한정된 실시예에 의해 설명되었으나, 본 발명은 이것에 의해 한정되지 않으며 본 발명이 속하는 기술 분야에서 통상의 지식을 가진 자에 의해 본 발명의 기술 사상과 아래에 기재될 청구범위의 균등 범위 내에서 다양한 수정 및 변형이 가능함은 물론이다. While the present invention has been described in connection with certain exemplary embodiments, it is to be understood that the invention is not limited to the disclosed embodiments, but, on the contrary, It is to be understood that various changes and modifications may be made without departing from the scope of the appended claims.
Claims (5)
상기 최소감지법 평가는 표준용액을 표준샘플병에 주입하고 기화시켜 1차 가스를 제조하는 1차 고농도 가스 제조 단계; 상기 1차 고농도가스를 무취가스가 들어있는 다수의 백 중 어느 한 곳에만 일정량 주입하고 희석하는 관능평가용 샘플가스 제조 단계; 다수의 판정원이 냄새를 맡아 감지농도가 가장 낮고, 가장 높은 결과가 나올 때까지 평가하는 샘플 관능 평가 단계; 및 감지한계 농도가 가장 낮고, 가장 높은 판정원을 제외한 나머지 판정원을 대상으로 결과를 확인하는 최소감지값 확인 단계를 포함하는 것을 특징으로 하는 냄새발생원에 대한 냄새유발 원인성분 규명방법.A sample collecting step of collecting the odor substance generated in the odor generating source in a plastic bag; A sensory evaluation step of confirming the type of odorous substance using a direct sensory method; A device analyzing step of confirming the detected components by analyzing the devices according to the types of odorous substances; A minimum sensing method evaluation step of confirming a minimum sensing value for the detected component; And a reproducibility evaluation step of preparing a standard gas which is the same as the concentration identified in the sample only for the substance selected as the odorous substance and evaluating the smell identity through comparative sensory evaluation of the standard gas with the sample,
The minimum sensing method includes a first high concentration gas production step of injecting a standard solution into a standard sample bottle and vaporizing the same to produce a primary gas; A step of preparing a sample gas for sensory evaluation in which the primary high concentration gas is injected and diluted in a certain amount only in one of a plurality of bags containing odorless gas; A sample sensory evaluation step in which a plurality of judges smell to evaluate the lowest sensed concentration until the highest result is obtained; And a minimum sensed value confirming step of confirming the result of the judgment on the other judgment sources except for the highest judgment source, which has the lowest detection concentration, and identifying the cause component of the odor causing substance to the odor generating source.
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