| Literature DB >> 35757626 |
Yichi Zhang1, Wei Deng1, Ayesha Afzal2, Ran Tao3.
Abstract
This paper assesses data from 16 emerging economies between 2000-and 2020 to assess the relationship between business cycles and healthcare expenditure alongside other control variables. Using the Gaussian mixture model, this study analyses the relationship between healthcare spending and business cycles, urbanization, population age, environmental quality, and the gender ratio. The paper finds that there exists a counter-cyclical relationship between economic booms/recessions and healthcare expenditure such that spending decreases during booms and goes up during recessions. The study also finds evidence that environmental quality plays a vital role in influencing healthcare expenditure.Entities:
Keywords: business cycles; economic intervention; economic stabilization; emerging national economies; health inequalities; patient safety
Mesh:
Year: 2022 PMID: 35757626 PMCID: PMC9226544 DOI: 10.3389/fpubh.2022.936004
Source DB: PubMed Journal: Front Public Health ISSN: 2296-2565
List of countries.
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|---|---|---|---|---|---|
| Brazil | BRICS | Columbia | CIVETS | Bangladesh | Next 11 |
| Russia | BRICS | Indonesia | CIVETS | Iran | Next 11 |
| India | BRICS | Vietnam | CIVETS | Mexico | Next 11 |
| China | BRICS | Egypt | CIVETS | Nigeria | Next 11 |
| South Africa | BRICS | Turkey | CIVETS | Pakistan | Next 11 |
| South Korea | CIVETS | Philippines | Next 11 |
Description of variables.
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|---|---|---|---|
| Dependent | Current health expenditure per capita (current US$) | HE1 | World Development Indicators |
| Current health expenditure (% of GDP) | HE2 | World Development Indicators | |
| Independent | Real GDP growth rate (%) | BC | IMF Economic Outlook Report |
| Control | Urban population (% of total population) | Urb | United Nations Population Division. |
| Population ages 65 and above (% of the total population) | Age | United Nations Population Division. | |
| Population, male (% of the total population) | Gen | United Nations Population Division. | |
| CO2 emissions (metric tons per capita) | EQ | Climate Watch. 2020. GHG Emissions. |
Summary statistics.
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|---|---|---|---|---|---|
| BC | 357 | 4.47 | 3.44 | −9.60 | 14.60 |
| HE1 | 320 | 245.19 | 240.44 | 8.36 | 1,031.58 |
| HE2 | 320 | 4.86 | 1.86 | 1.85 | 9.59 |
| Urb | 357 | 55.04 | 18.18 | 23.59 | 87.07 |
| Age | 357 | 6.24 | 2.51 | 2.74 | 15.51 |
| EQ | 323 | 3.19 | 2.95 | 0.17 | 11.64 |
| Gen | 357 | 49.94 | 1.28 | 46.33 | 52.03 |
Unit-root test.
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|---|---|---|
| BC | 4.3961 | Stationary |
| HE1 | 0.83 | Stationary |
| HE2 | −2.4537 | Non-stationary |
| Urb | −4.9078 | Non-stationary |
| Age | 9.0411 | Stationary |
| EQ | −0.7925 | Stationary |
| Gen | −4.8195 | Non-stationary |
Source: Author's calculations.
p < 0.05,
p < 0.1.
Robust GMM first differences panel modeling.
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|---|---|---|
| L.HE1 | 1.055 | |
| L.HE2 | 0.686 | |
| BC | −6.411 | −0.038 |
| Urb | 1.591 (1.764) | −0.014 (0.013) |
| Age | 0.827 (1.06) | 0.069 (0.054) |
| EQ | 20.62 | 0.179 |
| Gen | −75.59 | 0.056 (0.245) |
| Constant | −36.41 | −1.323 |
|
| 16 | 16 |
| Observations | 256 | 256 |
Standard errors in parenthesis.
p < 0.01,
p < 0.1.
Granger causality, HE1.
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|---|---|---|
| HE1-BC | 2.889 | Unidirectional |
| BC-HE1 | 0.043 | |
| HE1-Urb | 0.022 | Unidirectional |
| Urb-HE1 | 2.244 | |
| HE1-Age | 0.402 | Unidirectional |
| Age-HE1 | 3.884 | |
| HE1-EQ | 0.182 | Unidirectional |
| EQ-HE1 | 0.002 | |
| HE1-Gen | 0.04 | No Granger Causality |
| Gen-HE1 | 1.026 |
p < 0.01,
p < 0.05.
Granger causality, HE2.
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|---|---|---|
| HE2-BC | 0.978 | Unidirectional |
| BC-HE2 | 1.884 | |
| HE2-Urb | 1.598 | Unidirectional |
| Urb-HE2 | 4.463 | |
| HE2-Age | 0.293 | No Granger Causality |
| Age-HE2 | 0.495 | |
| HE2-EQ | 1.826 | Unidirectional |
| EQ-HE2 | 2.656 | |
| HE2-Gen | 1.917 | No Granger Causality |
| Gen-HE2 | 0.304 |
p < 0.01,
p < 0.05.