| Literature DB >> 35015762 |
Nerea Almeda1, Carlos R Garcia-Alonso2, Mencia R Gutierrez-Colosia1, Jose A Salinas-Perez2, Alvaro Iruin-Sanz3, Luis Salvador-Carulla4.
Abstract
Major efforts worldwide have been made to provide balanced Mental Health (MH) care. Any integrated MH ecosystem includes hospital and community-based care, highlighting the role of outpatient care in reducing relapses and readmissions. This study aimed (i) to identify potential expert-based causal relationships between inpatient and outpatient care variables, (ii) to assess them by using statistical procedures, and finally (iii) to assess the potential impact of a specific policy enhancing the MH care balance on real ecosystem performance. Causal relationships (Bayesian network) between inpatient and outpatient care variables were defined by expert knowledge and confirmed by using multivariate linear regression (generalized least squares). Based on the Bayesian network and regression results, a decision support system that combines data envelopment analysis, Monte Carlo simulation and fuzzy inference was used to assess the potential impact of the designed policy. As expected, there were strong statistical relationships between outpatient and inpatient care variables, which preliminarily confirmed their potential and a priori causal nature. The global impact of the proposed policy on the ecosystem was positive in terms of efficiency assessment, stability and entropy. To the best of our knowledge, this is the first study that formalized expert-based causal relationships between inpatient and outpatient care variables. These relationships, structured by a Bayesian network, can be used for designing evidence-informed policies trying to balance MH care provision. By integrating causal models and statistical analysis, decision support systems are useful tools to support evidence-informed planning and decision making, as they allow us to predict the potential impact of specific policies on the ecosystem prior to its real application, reducing the risk and considering the population's needs and scientific findings.Entities:
Mesh:
Year: 2022 PMID: 35015762 PMCID: PMC8752022 DOI: 10.1371/journal.pone.0261621
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
Fig 1Sequence of the decisional consequences (causality) in the ecosystem and variables involved.
Basic statistics for original data.
| Population (inhabitants) | Frequentation (visits) | Length of stay (days) | Discharges (users) | Readmissions (users) | Outpatient services per 100,000 | Psychiatrists per 100,000 | Psychologists per 100,000 | Nurses per 100,000 | Total number of professionals per 100,000 | |
|---|---|---|---|---|---|---|---|---|---|---|
| Average | 49,279.62 | 14,030.85 | 1,112.69 | 75.23 | 6.23 | 2.44 | 5.93 | 2.11 | 3.93 | 13.89 |
| Standard deviation | 20,942.74 | 7,414.42 | 620.42 | 43.32 | 3.92 | 1.23 | 1.29 | 1.24 | 0.90 | 2.65 |
| Variation coefficient (%) | 42.50 | 52.84 | 55.76 | 57.59 | 62.90 | 50.15 | 21.76 | 58.92 | 22.87 | 19.06 |
| Minimum | 21,593 | 5,532 | 392 | 28 | 1 | 1.25 | 4.31 | 0 | 2.47 | 10.91 |
| Maximum | 78,400 | 27,205 | 2.058 | 147 | 15 | 4.53 | 9.06 | 4.08 | 5.51 | 21.11 |
Fig 2Final evidence-informed Bayesian network based on expert knowledge and data.
Fig 3Relationship between Freq and Pop×TNProff (significance level 0.05).
Confidence intervals in dashed lines.
Input-oriented results, variation pre-post (%) in brackets.
In bold, the catchment areas directly involved with the decisional process.
| Areas | Relative technical efficiency (RTE) on average | Probability of having an RTE score greater than 0.75 | RTE error | Stability of the ecosystem | Shannon’s entropy (%) | |||||
|---|---|---|---|---|---|---|---|---|---|---|
| Pre | Post | Pre | Post | Pre | Post | Pre | Post | Pre | Post | |
| Global (Gipuzkoa MH ecosystem) | 0.83 | 0.86 | 0.76 | 0.80 | 0.0016 | 0.0019 | 23.46 | 29.20 | 76.69 | 71.18 |
| Alto Deba-Arrasate | 0.82 | 0.80 | 0.69 | 0.60 | 0.0068 | 0.0100 | 28.71 | 22.93 | 66.07 | 74.20 |
| Amara | 0.82 | 0.86 | 0.63 | 0.77 | 0.0042 | 0.0050 | 29.71 | 36.12 | 65.91 | 64.01 |
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| Beasain | 0.89 | 0.87 | 0.90 | 0.84 | 0.0021 | 0.0034 | 40.97 | 40.02 | 58.53 | 67.89 |
| Eguia | 0.74 | 0.83 | 0.51 | 0.74 | 0.0063 | 0.0031 | 27.98 | 28.33 | 78.42 | 66.24 |
| Eibar | 0.77 | 0.78 | 0.66 | 0.64 | 0.0042 | 0.0035 | 19.23 | 30.89 | 78.26 | 73.29 |
| Irun | 0.73 | 0.78 | 0.54 | 0.63 | 0.0078 | 0.0049 | 26.22 | 29.38 | 79.20 | 71.97 |
| Ondarreta | 0.81 | 0.83 | 0.64 | 0.56 | 0.0056 | 0.0069 | 30.90 | 29.97 | 74.22 | 57.82 |
| Renteria | 0.82 | 0.85 | 0.73 | 0.80 | 0.0049 | 0.0070 | 32.24 | 36.93 | 72.13 | 63.92 |
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| Zarautz | 0.86 | 0.88 | 0.83 | 0.81 | 0.0026 | 0.0028 | 37.05 | 44.25 | 68.42 | 64.28 |
| Zumarraga | 0.86 | 0.90 | 0.87 | 0.75 | 0.0035 | 0.0046 | 28.43 | 39.09 | 64.22 | 62.80 |
(1) RTE∈[0, 1] (0: DMU completely inefficient, 1: DMU completely efficient); 500 experiments.
(2) Pre: Pre-Intervention.
(3) Post: Post-Intervention.
(4) Stability∈[0. 100] (0: minimum stability–small data changes can result in very large RTE changes; 100 maximum stability–data changes do not modify RTE).
(5) Shannon´s entropy is calculated as a percentage of the feasible maximum estimated by the frequency analysis. Entropy∈[0, 100] (0: minimum–the ecosystem has a very homogeneous management, 100: maximum–the ecosystem has a very heterogeneous management).
(6) Fifteen scenarios (meaningful variable combinations (500 experiments each); 13 catchment areas.
(7) The results have been rounded to the most appropriate number of decimal places.
Output-oriented results, variation pre-post (%) in brackets.
In bold, the catchment areas directly involved with the decisional process.
| Areas | Relative technical efficiency (RTE) on average | Probability of having an RTE score greater than 0.75 | RTE error | Stability of the ecosystem | Shannon’s entropy (%) | |||||
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| Pre | Post | Pre | Post | Pre | Post | Pre | Post | Pre | Post | |
| Global (Gipuzkoa MH ecosystem) | 0.83 | 0.83 | 0.77 | 0.77 | 0.0014 | 0.0010 | 13.89 | 13.81 | 73.94 | 73.96 |
| Alto Deba-Arrasate | 0.80 | 0.80 | 0.61 | 0.63 | 0.0036 | 0.0069 | 12.17 | 12.14 | 77.27 | 77.65 |
| Amara | 0.84 | 0.84 | 0.78 | 0.78 | 0.0046 | 0.0032 | 17.48 | 17.58 | 71.06 | 70.46 |
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| Beasain | 0.90 | 0.89 | 0.88 | 0.85 | 0.0031 | 0.0021 | 19.38 | 18.85 | 59.94 | 63.29 |
| Eguia | 0.79 | 0.79 | 0.74 | 0.73 | 0.0082 | 0.0054 | 8.03 | 8.03 | 65.44 | 64.84 |
| Eibar | 0.77 | 0.76 | 0.55 | 0.54 | 0.0053 | 0.0043 | 11.05 | 11.14 | 68.52 | 67.69 |
| Irun | 0.76 | 0.76 | 0.58 | 0.56 | 0.0105 | 0.0116 | 9.34 | 9.34 | 77.95 | 76.78 |
| Ondarreta | 0.76 | 0.75 | 0.56 | 0.52 | 0.0087 | 0.0032 | 9.00 | 9.00 | 74.02 | 73.84 |
| Renteria | 0.84 | 0.83 | 0.72 | 0.71 | 0.0128 | 0.0091 | 13.51 | 13.51 | 63.04 | 64.24 |
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| Zarautz | 0.85 | 0.86 | 0.76 | 0.76 | 0.0059 | 0.0020 | 16.22 | 16.26 | 69.19 | 68.81 |
| Zumarraga | 0.87 | 0.86 | 0.66 | 0.64 | 0.0086 | 0.0079 | 15.65 | 14.10 | 68.23 | 67.09 |
(1) RTE∈[0, 1] (0: DMU completely inefficient, 1: DMU completely efficient); 500 experiments.
(2) Pre: Pre-Intervention.
(3) Post: Post-Intervention.
(4) Stability∈[0. 100] (0: minimum stability–small data changes can result in very large RTE changes; 100 maximum stability–data changes do not modify RTE).
(5) Shannon´s entropy is calculated as a percentage of the feasible maximum estimated by the frequency analysis. Entropy∈[0, 100] (0: minimum–the ecosystem has a very homogeneous management, 100: maximum–the ecosystem has a very heterogeneous management).
(6) Fifteen scenarios (meaningful variable combinations, 500 experiments each); 13 catchment areas.
(7) The results have been rounded to the most appropriate number of decimal places.