RISS 학술연구정보서비스

검색

인기 검색어

    다국어 입력

    http://chineseinput.net/에서 pinyin(병음)방식으로 중국어를 변환할 수 있습니다.

    변환된 중국어를 복사하여 사용하시면 됩니다.

    예시)
    • 中文 을 입력하시려면 zhongwen을 입력하시고 space를누르시면됩니다.
    • 北京 을 입력하시려면 beijing을 입력하시고 space를 누르시면 됩니다.
    닫기

    폴리에틸렌 미세플라스틱과 중금속의 복합독성 및 독성 상호작용 평가 = Evaluation of Combined Toxicity and Toxic Interactions between Polyethylene Microplastics and Heavy Metals

    한글로보기

    https://www.riss.kr/link?id=T17548940

    • 0

      상세조회
    • 0

      다운로드
    서지정보 열기
    • 내보내기
    • 내책장담기
    • 공유하기
      • URL 복사
    • 오류접수
    인용문이 복사되었습니다.

    부가정보

    다국어 초록 (Multilingual Abstract) kakao i 다국어 번역

    Microplastics and heavy metals frequently coexist in aquatic environments, and their combined toxicity may be altered by environmental weathering of plastic particles. This study evaluated the combined toxicity and toxicity interaction patterns of non-weathered polyethylene microplastics (NPE) and UV-weathered polyethylene microplastics (UVPE) with Cr (VI), Cd (II), Hg (II), and a mixed-metal system using sulfur-oxidizing bacteria (SOB). Toxic responses were assessed using electrical conductivity (EC)-based functional inhibition, independent action (IA) based interaction analysis, response surface methodology (RSM), and superoxide dismutase (SOD) inhibition as an oxidative stress-related endpoint. Surface characterization using SEM and ATR-FTIR showed that UV treatment induced clear morphological and chemical changes in polyethylene microplastics, including increased surface roughness, cracks, surface delamination, and an increase in the carbonyl index. These results confirmed that the applied UV treatment produced detectable weathering-related alterations in particle properties. RSM analysis demonstrated that the effects of weathering differed depending on the metal type. Under Cr (VI) exposure, the inhibition surface shifted upward after weathering, and the high-inhibition region expanded toward lower and intermediate concentration ranges. In the Cd (II) system, inhibition responses remained largely linear, whereas the interaction response under UVPE showed a significant quadratic
    pattern, indicating that weathering changed the overall interaction structure. In the Hg (II) system, UVPE substantially increased EC inhibition, while IA-based interaction patterns differed between NPE and UVPE. In the mixed-metal system, antagonism was dominant under both NPE and UVPE conditions, although the magnitude and spatial distribution of interaction were modified by weathering. SOD inhibition showed a significant positive correlation with EC inhibition across all treatments, and this relationship was more distinct in the UVPE group. However, the explanatory power was limited, indicating that SOD alone did not fully explain EC-based functional inhibition. Overall, this study demonstrates that UV weathered polyethylene microplastics can alter not only the magnitude of combined toxicity but also the direction and spatial distribution of toxicity interactions with heavy metals in an SOB-based test system. These findings suggest that weathered microplastics should be considered dynamic factors in combined ecological risk assessment.
    번역하기

    Microplastics and heavy metals frequently coexist in aquatic environments, and their combined toxicity may be altered by environmental weathering of plastic particles. This study evaluated the combined toxicity and toxicity interaction patterns of non...

    Microplastics and heavy metals frequently coexist in aquatic environments, and their combined toxicity may be altered by environmental weathering of plastic particles. This study evaluated the combined toxicity and toxicity interaction patterns of non-weathered polyethylene microplastics (NPE) and UV-weathered polyethylene microplastics (UVPE) with Cr (VI), Cd (II), Hg (II), and a mixed-metal system using sulfur-oxidizing bacteria (SOB). Toxic responses were assessed using electrical conductivity (EC)-based functional inhibition, independent action (IA) based interaction analysis, response surface methodology (RSM), and superoxide dismutase (SOD) inhibition as an oxidative stress-related endpoint. Surface characterization using SEM and ATR-FTIR showed that UV treatment induced clear morphological and chemical changes in polyethylene microplastics, including increased surface roughness, cracks, surface delamination, and an increase in the carbonyl index. These results confirmed that the applied UV treatment produced detectable weathering-related alterations in particle properties. RSM analysis demonstrated that the effects of weathering differed depending on the metal type. Under Cr (VI) exposure, the inhibition surface shifted upward after weathering, and the high-inhibition region expanded toward lower and intermediate concentration ranges. In the Cd (II) system, inhibition responses remained largely linear, whereas the interaction response under UVPE showed a significant quadratic
    pattern, indicating that weathering changed the overall interaction structure. In the Hg (II) system, UVPE substantially increased EC inhibition, while IA-based interaction patterns differed between NPE and UVPE. In the mixed-metal system, antagonism was dominant under both NPE and UVPE conditions, although the magnitude and spatial distribution of interaction were modified by weathering. SOD inhibition showed a significant positive correlation with EC inhibition across all treatments, and this relationship was more distinct in the UVPE group. However, the explanatory power was limited, indicating that SOD alone did not fully explain EC-based functional inhibition. Overall, this study demonstrates that UV weathered polyethylene microplastics can alter not only the magnitude of combined toxicity but also the direction and spatial distribution of toxicity interactions with heavy metals in an SOB-based test system. These findings suggest that weathered microplastics should be considered dynamic factors in combined ecological risk assessment.

    더보기

    목차 (Table of Contents)

    • Ⅰ. 서 론 1
    • Ⅱ. 연 구 사 6
    • III. 재료 및 방법 29
    • 3.1재료 29
    • 3.1.1 미세플라스틱 및 중금속 시약 29
    • Ⅰ. 서 론 1
    • Ⅱ. 연 구 사 6
    • III. 재료 및 방법 29
    • 3.1재료 29
    • 3.1.1 미세플라스틱 및 중금속 시약 29
    • 3.1.2 중금속 stock solution 제조 30
    • 3.1.3 SOB 배양 및 시험계 구성 30
    • 3.2시험 방법 33
    • 3.2.1 미세플라스틱 UV 풍화 처리 33
    • 3.2.2 미세플라스틱 표면 특성 분석 35
    • 3.2.3 단일 독성 시험 37
    • 3.2.4 복합 독성 시험 38
    • 3.2.5 산화스트레스 지표(SOD) 측정 42
    • 3.3 분석 방법 44
    • 3.3.1 단일 독성 Dose-response fitting 및 EC50 산정 44
    • 3.3.2 복합 독성의 상호작용 평가 44
    • 3.3.3 반응표면 적합 및 시각화 46
    • 3.3.4 통계분석 47
    • Ⅳ. 결과 및 고찰 48
    • 4.1 미세플라스틱의 표면 변화 분석 48
    • 4.2개별 독성 측정 결과 53
    • 4.3 복합 독성 측정 결과(Inhibition, Interaction) 60
    • 4.3.1 Cr(VI) 61
    • 4.3.2 Cd(II) 70
    • 4.3.3 Hg(II) 78
    • 4.3.4 Mixture 88
    • 4.4 SOD 측정 결과 97
    • Ⅴ. 결 론 107
    • 참 고 문 헌 111
    더보기

    분석정보

    View

    상세정보조회

    0

    Usage

    원문다운로드

    0

    대출신청

    0

    복사신청

    0

    EDDS신청

    0

    동일 주제 내 활용도 TOP

    더보기

    주제

    연도별 연구동향

    연도별 활용동향

    연관논문

    연구자 네트워크맵

    공동연구자 (7)

    유사연구자 (20) 활용도상위20명

    이 자료와 함께 이용한 RISS 자료

    나만을 위한 추천자료

    해외이동버튼