쉐도잉 연습: IASNR 2022 Conference Presentation - 영상으로 영어 말하기 배우기

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Hi, my name is Chad McGuire, and this is my presentation on an analysis of sulfur emission reductions in the United States between 1990
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and 2014 using a disproportionality framework.
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In terms of an overview, uh, There is a regulatory natural experiment in sulfur emissions in the United States that we can look at,
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and it began in 1990 when the United States federal government passed the Clean Air Act amendments of 1990.
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And the regulatory mechanism that creates this natural experiment is the cap and trade program.
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Cap and trade has been used in a number of ways.
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globally by different governments, but here in the United States in particular, cap and trade was the main mechanism that was used in the 1990 Clean Air Act amendments.
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And as a matter of using that cap and trade framework, we can review reductions over time.
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between high and low socioeconomic status communities.
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So using the cap and trade scenario, we can look at the effect of cap and trade.
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in terms of its
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proportionality or disproportionality between communities and what that means quite simply is
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that as we see the cap
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and trade play itself out over time since 1990 we can
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look at areas where emission levels of certain particular sulfur as an example of a pollutant
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that has an impact on human well -being we can look at those the numbers of the proportions
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of sulfur emissions over time since 1990
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and we can see relatively speaking where they diminished
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and where they might not have diminished as quickly in certain communities so we can look for evidence of disproportionality so
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Operational characteristics are we can look for, for example, for the socio -economic status communities, higher unemployment, lower educational attainment,
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higher consumption of means tested public services and offering greater demographic diversity.
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These characteristics are the things
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that we would look at to determine low socio -economic status communities
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when we're looking at the relative changes in sulfur emissions from the cap and trade program between different geographic regions.
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And disproportionality itself, we can operationally or operationally defined as evidence of distributional effects of environmental policies.
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So where we see some change, some variance in reductions, let's call that, reductions of sulfur emissions over time.
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So for cap and trade in particular, the cap, we can look at as a government mandate and then the trade market forces.
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So we have the opportunity for distributional effects because the cap part is a government mandate.
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That's a requirement.
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So we cap total amounts of emissions, but then the trade can allow us to see how those changes,
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those reductions as the cap reduces total emissions, where there might be changes in one area versus another.
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You might actually see increases in some areas where you see substantial reductions in others.
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And then you'd look at what those areas look like, what that community looks like, and whether or not it shows signs of,
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as we've defined operationally here, low socioeconomic status.
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Michael Shachm: And so, as a matter of overall CAP is reduced government function, but what is the distribution of emissions and trading phase over time between socio economic status communities.
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- Yeah.
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For the purposes of the study, in particular.
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located in Massachusetts and so looked at Massachusetts communities instead of a nationwide
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because there's too much variance say between states it's too difficult
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so we looked at communities at the county level
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and then specific communities largest emitters within counties so we compared those counties
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and the communities within those counties
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and Massachusetts as a way to try to determine disproportionality the big questions what factors may be influencing the observance or
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What factors might be influencing it?
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What policy implications arise from this analysis?
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And in terms of the research focus framework questions that we have derived from previous work, Collins, Munos, and Zsa Zsa in particular,
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whether the producer disproportionality are present across the study area.
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So do we find disproportionality at all between these Massachusetts communities, these let's call them county level communities.
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And if disproportionality are found, what is the demographic makeup of those communities, and are they consistent?
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So if we do find disproportionality between communities, How do those communities look from a demographic standpoint?
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In terms of data and results, so here we have a table that we derived from looking at the different sulfur emissions,
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and these are the years in which we can find changes
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and new updates in terms of the United States Environmental Protection Agency national emissions inventory.
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So these are the years that we can find between 1990 and 2014 where we're given these specific particular changes.
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What we find is that in Massachusetts, if you look, you can see that in 1990, these are in the millions, so it's 2 .33 million.
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And we see a reduction down to 3544 metric tons, which is significant.
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So we see an overall significant reduction.
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The cap and trade program was very effective in reducing between 1990 and 2014 the amount of sulfur overall in Massachusetts. than others.
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And so we can look at those counties
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and make a determination of the levels of reduction from these periods of time from 1990 to 1996,
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from 1996, 1997, so on and so forth, and look at how those reductions.
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We can see there were substantial overall reductions between 1990 and 2014,
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but the question is, what does the path look like between these years where the measurements were made, and what does the path look like in relationship to that?
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relating these counties to what we have identified as Bristol County
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as our low socioeconomic status community these are the five counties within Massachusetts
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that have the largest relatively large levels we excluded Suffolk County for various reasons
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but it was basically done within between 1990 and 1996 but
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which had the largest levels and we can see distribution patterns
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and compare them honestly between each other of these five counties over the period of time
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The reason Bristol County is chosen as our low socioeconomic status or the community, the relative community with disproportionality is because relative to the other,
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counties as you can see here in the scatter plots you
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can see the other counties bristol county shows relative to its amount of emissions here the tons of sulfur emissions
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and we can look at a certain demographics that we're able to get which includes population unemployment rate percent below poverty
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and percent of high school graduate or higher.
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We see the Bristol County basically contains these demographic indicators in terms of overall poverty level,
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overall percentage relative to the other counties.
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Bristol County has higher emissions, relative to the other counties, and it tends to be,
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it tends to have higher unemployment rates and lower education rates, the things that you would indicate to be a low socioeconomic status community in relationship to these other areas.
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So that's why Bristol County ends up being our county of choice.
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And so when we sort of look at these distribution patterns over time of those years that we discussed,
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1990, 96, 97, so these years where the EPA inventory looked at the sulfur emissions, we can see we have substantial reductions,
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relatively speaking, and including Bristol County, which I think, excuse me, which we can see here in the yellow Bristol County's reductions.
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here.
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So effectively what's happening is that the burden, if you think about it this way, as you're reducing sulfur emissions, if you're not doing technological advances,
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if you're not going to put in expensive scrubbers to remove the sulfur, you're probably going to start shutting down and transitioning from coal to other methods of generating electricity,
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where most of the sulfur emissions come from is the burning of coal.
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And so what's happening is the other counties that That's Bristol County.
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They're either shutting down or they're reducing pretty substantially within about a decade or so,
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and Bristol County is taking the sort of brunt of that.
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So if there's a need for still generating electricity using coal, relatively speaking, a cheap version for the state.
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writ large that you're going to see Bristol County.
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The evidence shows that Bristol County did not have the same rates in between these years in particular, the same rates of reductions.
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And you can see that
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if you look at Massachusetts here in the green relative to Massachusetts reductions relative to Bristol County, its reductions.
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You see again, there's this burden
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that Bristol County seems to be taking on relative to the
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rest of the state in terms of maintaining a certain level of emissions.
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What that means effectively if we look at this is that the cap and trade can be effective at pollution reduction.
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It certainly was in Massachusetts.
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It was nationally, you know, in terms of reducing emissions significantly sulfur, which carries all kinds of important implications,
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but cap sets mandatory target.
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which is important because you can lower the cap every year, every period of time.
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And then the trade allows for important market incentives and choice.
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So it allows for a lot of room in terms of how generators, those that burn sulfur, coal, that contain sulfur, how they're going to meet that objective.
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But the process is far from equal.
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And that's what the evidence shows us in this study.
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So the evidence is the burden of reduction tends to fall disproportionately on marginalized communities.
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In our case, Bristol County bore most of the burden of reducing.
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It same reduction, the same levels of reduction as the other communities.
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And so that's an important point for the trade portion, at least, because it's not equal amongst communities.
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And so we must understand this reality when we're thinking about policy design and implementation.
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We must look beyond the ultimate goals and see how the process of obtaining those goals, what happens along the way.
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And that's really important to think about from a policy standpoint when we thinking about the role of environmental policies.
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That's all.
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I hope you enjoyed.
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Thank you very much.
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Thank you.

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이 C1 수준 말하기 레슨은 영상 “IASNR 2022 Conference Presentation”을(를) 바탕으로 합니다. 가장 자주 반복되는 단어는 다음과 같습니다: reduction, emission, cap, communities, county. 이 영상에는 섀도잉할 문장 117개와 단어 1669개가 있습니다. 말하는 구간의 길이는 11:06입니다. 화자는 분당 약 150단어로, 일상 대화에 가까운 자연스러운 속도로 말합니다. 단어의 83%가 영어에서 가장 많이 쓰이는 3,000단어에 속합니다. 나머지는 연습 전에 미리 확인해 두세요.

이 영상의 핵심 어휘

영상에서 가장 어려운 단어 12개를 발음, 뜻과 함께 정리했습니다.

단어발음뜻
sulfur 명사/ˈsʌl.fə/황, 석유황
mandate 명사/ˈmændeɪ̯t/위임, 권한
characteristic 명사/ˌkæɹ(ə)ktəˈɹɪstɪk/특성, 특징
attainment 명사/əˈteɪnmənt/성과, 성취
pollutant 명사/pəˈl(j)uːtənt/오염물질
scatter 동사/ˈskætɚ/흩어지다, 흩다
indicator 명사/ˈɪn.dɪˌkeɪ.tə(ɹ)/인디케이터, 지시약
arise 동사/əˈɹaɪz/일어나다
generator 명사/ˈdʒɛnəɹeɪtə(ɹ)/발전기
geographic 형용사/d͡ʒiəˈɡɹæfɪk/지리학의
measurement 명사/ˈmɛʒ.ə.mənt/측정
technological 형용사/ˌtɛk.nəˈlɑ.dʒɪ.kəl/기술

이 영상의 문법

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문형영상 속 표현
현재완료 have/has + 과거분사 — 과거의 일이 지금도 관련이 있을 때has been · we've defined · have derived
수동태 be + 과거분사 — 누가 하는지보다 무슨 일이 일어나는지에 초점is reduced · are found · were made

주의할 발음

화자는 you're, we're, they're 같은 축약형과 약화된 형태를 14번 사용합니다. 들리는 대로 짧게 발음하세요.

  • “sh”와 “zh” 소리: emission /ɪˈmɪʃ.ən/, diminish /dɪˈmɪnɪʃ/, distributional /ˌdɪs.tɹəˈbjuː.ʃə.nəl/, implication /ˌɪmpləˈkeɪʃən/, disproportionately /ˈdɪs.pɹəˌpɔɹ.ʃən.ət.li/
  • 긴 단어 — 강세 위치에 주의: demographic /ˌdɛm.əˈɡɹæf.ɪk/, distributional /ˌdɪs.tɹəˈbjuː.ʃə.nəl/, implication /ˌɪmpləˈkeɪʃən/, characteristic /ˌkæɹ(ə)ktəˈɹɪstɪk/, disproportionately /ˈdɪs.pɹəˌpɔɹ.ʃən.ət.li/

한국어 화자가 어려워하는 소리:

  • /f/ — ㅍ(/p/)으로 바꾸지 말고 윗니를 아랫입술에 대기: sulfur /ˈsʌl.fə/, demographic /ˌdɛm.əˈɡɹæf.ɪk/, geographic /d͡ʒiəˈɡɹæfɪk/
  • /v/ — ㅂ(/b/)과 구별하기: variance /ˈvæɹ.i.əns/, derive /dɪˈɹaɪv/, observance /əbˈzɝvəns/, incentive /ɪnˈsɛntɪv/
  • /z/ — ㅈ이 아니라 성대를 울리는 /s/: marginalize /ˈmɑɹdʒɪnəlaɪz/, observance /əbˈzɝvəns/, arise /əˈɹaɪz/

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