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An optimized artificial neural network model for the prediction of rate of hazardous chemical and healthcare waste generation at the national level

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Abstract

This paper presents a development of general regression neural network (a form of artificial neural network) models for the prediction of annual quantities of hazardous chemical and healthcare waste at the national level. Hazardous waste is being generated from many different sources and therefore it is not possible to conduct accurate predictions of the total amount of hazardous waste using traditional methodologies. Since they represent about 40% of the total hazardous waste in the European Union, chemical and healthcare waste were specifically selected for this research. Broadly available social, economic, industrial and sustainability indicators were used as input variables and the optimal sets were selected using correlation analysis and sensitivity analysis. The obtained values of coefficients of determination for the final models were 0.999 for the prediction of chemical hazardous waste and 0.975 for the prediction of healthcare and biological hazardous waste. The predicting capabilities of the models for both types of waste are high, since there were no predictions with errors greater than 25%. Also, results of this research demonstrate that the human development index can replace gross domestic product and in this context even represent a better indicator of socio-economic conditions at the national level.

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References

  1. European Parliament and the Council of the European Union (2008) Directive 2008/98/EC of the European Parliament and of the Council on waste and repealing certain directives (Waste framework). OJ L 312,22.11.2008, 3–30. doi:2008/98/EC.; 32008L0098

  2. Kang Y-Y, Jeon T-W, Kim W-I, Shin SK, Yeon J-M, Somasundaram S (2014) Correlation study of hazardous waste characteristics among various chemical processes in Republic of Korea. J Mater Cycles Waste Manag 16(3):566–575. https://doi.org/10.1007/s10163-013-0208-8

    Article  Google Scholar 

  3. Court CD, Munday M, Roberts A, Turner K (2015) Can hazardous waste supply chain “hotspots” be identified using an input-output framework? Eur J of Oper Res 241(1):177–187. https://doi.org/10.1016/j.ejor.2014.08.011

    Article  Google Scholar 

  4. Schuhmacher M, Fàbrega F, Kumar V, García F, Nadal M, Domingo JL (2014) A PBPK model to estimate PCDD/F levels in adipose tissue: Comparison with experimental values of residents near a hazardous waste incinerator. Environ Int 73:150–157. https://doi.org/10.1016/j.envint.2014.07.020

    Article  Google Scholar 

  5. Zakaria B, Abdullah R, Ramli MF, Latif PA (2012) Selection criteria using the Delphi method for siting an integrated hazardous waste disposal facility in Malaysia. J Environ Plann Manag 56(4):1–19. https://doi.org/10.1080/09640568.2012.689614

    Google Scholar 

  6. United Nations (2007) Indicators of Sustainable Development: Guidelines and Methodologies. Third Edit. United Nations publication, New York, USA. http://www.un.org/esa/sustdev/natlinfo/indicators/guidelines.pdf

  7. van Beusekom C (1999) Hazardous waste in the European Union. Statistics in focus—Environment and energy, Luxembourg: Eurostat 1–7. http://edz.bib.uni-mannheim.de/www-edz/pdf/statinf/99/CA-NQ-99-007-EN-I-EN.pdf. Accessed 22 Mar 2016

  8. European Commission Eurostat (2017) Waste statistics—statistics explained. http://ec.europa.eu/eurostat/statistics-explained/index.php/Waste_statistics. Accessed 22 Mar 2016

  9. EPA US (2012). Chemical safety for sustainability chemical, strategic research action plan 2012–2016. EPA 601/R-12/006:pp 1–64. http://www.epa.gov/sites/production/files/2014-06/documents/css-strap.pdf. Accessed 4 May 2016

  10. Rudel RA, Attfield KR, Schifano JN, Brody JG (2007) Chemicals causing mammary gland tumors in animals signal new directions for epidemiology, chemicals testing, and risk assessment for breast cancer prevention. Cancer 109(12):2635–2666. https://doi.org/10.1002/cncr.22653

    Article  Google Scholar 

  11. Komilis D, Fouki A, Papadopoulos D (2012) Hazardous medical waste generation rates of different categories of health-care facilities. Waste Manag 32(7):1434–1441. https://doi.org/10.1016/j.wasman.2012.02.015

    Article  Google Scholar 

  12. Birpinar ME, Bilgili MS, Erdoğan T (2009) Medical waste management in Turkey: a case study of Istanbul. Waste Manag 29(1):445–448. https://doi.org/10.1016/j.wasman.2008.03.015

    Article  Google Scholar 

  13. Mmereki D, Baldwin A, Li B, Liu M (2017) Healthcare waste management in Botswana: storage, collection, treatment and disposal system. J Mater Cycles Waste Manag 19(1):351–365. https://doi.org/10.1007/s10163-015-0429-0

    Article  Google Scholar 

  14. Rushbrook P, Zghondi R (2005) Better healthcare waste management: an integral component of health investment. World Health Organization, Amman http://apps.who.int/iris/bitstream/10665/119762/1/dsa515.pdf. Accessed 22. Mar 2016

  15. Shannon AL, Woolridge A (2011) Chap. 23 - Medical Waste. Elsevier Inc. https://doi.org/10.1016/B978-0-12-381475-3.10023-3

    Google Scholar 

  16. Sartaj M, Arabgol R (2015) Assessment of healthcare waste management practices and associated problems in Isfahan Province (Iran). J Mater Cycles Waste Manag 17(1):99–106. https://doi.org/10.1007/s10163-014-0230-5

    Article  Google Scholar 

  17. Elimelech E, Ayalon O, Flicstein B (2011) Hazardous waste management and weight-based indicators - The case of Haifa Metropolis. J Hazard Mater 185(2–3):626–633. https://doi.org/10.1016/j.jhazmat.2010.09.064

    Article  Google Scholar 

  18. Specht DF (1991) A general regression neural network. IEEE Trans Neural Netw 2(6):568–576. https://doi.org/10.1109/72.97934

    Article  Google Scholar 

  19. Antanasijević D, Pocajt V, Popović I, Redžić N, Ristić M (2013) The forecasting of municipal waste generation using artificial neural networks and sustainability indicators. Sustain Sci 8(1):37–46. https://doi.org/10.1007/s11625-012-0161-9

    Article  Google Scholar 

  20. Adamović V, Antanasijević D, Ristić M, Perić-Grujić A, Pocajt V (2017) Prediction of municipal solid waste generation using artificial neural network approach enhanced by structural break analysis. Environ Sci Pollut Res 24(1):299–311. https://doi.org/10.1007/s11356-016-7767-x

    Article  Google Scholar 

  21. Statistics Norway (2016) Hazardous waste, 2015. Oslo. http://www.ssb.no/en/natur-og-miljo/statistikker/spesavf/aar. Accessed 18 May 2017

  22. Gusca J, Kalnins SN, Blumberga D, Bozhko L, Khabdullina Z, Khabdullin A (2015) Assessment method of health care waste generation in Latvia and Kazakhstan. Energy Proc 72:175–179. https://doi.org/10.1016/j.egypro.2015.06.025

    Article  Google Scholar 

  23. Ben-Gal I (2005) Outlier Detection. In: Maimon O, Rockach L (eds). Data mining and knowledge discovery handbook: a complete guide for practitioners and researchers. Kluwer Academic Publishers pp 131–146. https://doi.org/10.1007/0-387-25465-x_7

  24. Liu H, Shah S, Jiang W (2004) On-line outlier detection and data cleaning. Comput Chem Eng 28(9):1635–1647. https://doi.org/10.1016/j.compchemeng.2004.01.009

    Article  Google Scholar 

  25. Beigl P, Lebersorger S, Salhofer S (2008) Modelling municipal solid waste generation: a review. Waste Manag 28(1):200–214. https://doi.org/10.1016/j.wasman.2006.12.011

    Article  Google Scholar 

  26. Sabour MR, Mohamedifard A, Kamalan H (2007) A mathematical model to predict the composition and generation of hospital wastes in Iran. Waste Manag 27(4):584–587. https://doi.org/10.1016/j.wasman.2006.05.010

    Article  Google Scholar 

  27. Jahandideh S, Jahandideh S, Asadabadi EB, Askarian M, Movahedi MM, Hosseini S et al (2009) The use of artificial neural networks and multiple linear regression to predict rate of medical waste generation. Waste Manag 29(11):2874–2879. https://doi.org/10.1016/j.wasman.2009.06.027

    Article  Google Scholar 

  28. Eleyan D, Al-Khatib I, Garfield J (2013) System dynamics model for hospital waste characterization and generation in developing countries. Waste Manag Res 31(10):986–995. https://doi.org/10.1177/0734242X13490981

    Article  Google Scholar 

  29. Al-Khatib IA, Abu Fkhidah I, Khatib JI, Kontogianni S (2016) Implementation of a multi-variable regression analysis in the assessment of the generation rate and composition of hospital solid waste for the design of a sustainable management system in developing countries. Waste Manag Res 34(3):225–234. https://doi.org/10.1177/0734242X15622813

    Article  Google Scholar 

  30. Karpušenkaitė A, Ruzgas T, Denafas G (2016) Forecasting medical waste generation using short and extra short datasets: case study of Lithuania. Waste Manag Res 34(4):378–387. https://doi.org/10.1177/0734242X16628977

    Article  Google Scholar 

  31. Granados AJ, Peterson PJ (1999) Hazardous waste indicators for national decision makers. J Environ Manage 55(4):249–263. https://doi.org/10.1006/jema.1999.0254

    Article  Google Scholar 

  32. Tripathy M (2010) Power transformer differential protection using neural network Principal Component Analysis and Radial Basis Function Neural Network. Simul Model Pract Theory 18(5):600–611. https://doi.org/10.1016/j.simpat.2010.01.003

    Article  Google Scholar 

  33. Mustapha A, Aris AZ, Juahir H, Ramli MF, Kura NU (2013) River water quality assessment using environmentric techniques: case study of Jakara River Basin. Environ Sci Pollut Res 20(8):5630–5644. https://doi.org/10.1007/s11356-013-1542-z

    Article  Google Scholar 

  34. Hamilton LC (1991) Modern data analysis: a first course in applied statistics. Technometrics 33(4):487–488

    Google Scholar 

  35. Walczak S, Cerpa N (1999) Heuristic principles for the design of artificial neural networks. Inf Softw Technol 41(2):107–117. https://doi.org/10.1016/S0950-5849(98)00116-5

    Article  Google Scholar 

  36. Gheyas IA, Smith LS (2010) A neural network-based framework for the reconstruction of incomplete data sets. Neurocomputing 73(16–18):3039–3065. https://doi.org/10.1016/j.neucom.2010.06.021

    Article  Google Scholar 

  37. Tomandl D, Schober A (2001) A modified general regression neural network (MGRNN) with new, efficient training algorithms as a robust “black box”-tool for data analysis. Neural Netw 14(8):1023–1034. https://doi.org/10.1016/S0893-6080(01)00051-X

    Article  Google Scholar 

  38. Zhou Q, Jiang H, Wang J, Zhou J (2014) A hybrid model for PM2.5 forecasting based on ensemble empirical mode decomposition and a general regression neural network. Sci Total Environ 496(1):264–274. https://doi.org/10.1016/j.scitotenv.2014.07.051

    Article  Google Scholar 

  39. Gheyas IA, Smith LS (2011) A novel neural network ensemble architecture for time series forecasting. Neurocomputing 74(18):3855–3864. https://doi.org/10.1016/j.neucom.2011.08.005

    Article  Google Scholar 

  40. Millie DF, Weckman GR, Young W, Ivey JE, Carrick HJ, Fahnenstiel GL (2012) Modeling microalgal abundance with artificial neural networks: demonstration of a heuristic “Grey-Box” to deconvolve and quantify environmental influences. Environ Model Softw 38(1):27–39. https://doi.org/10.1016/j.envsoft.2012.04.009

    Article  Google Scholar 

  41. Kisi O (2006) Generalized regression neural networks for evapotranspiration modelling. J Hydrol Sci 51(6):1092–1105. https://doi.org/10.1623/hysj.51.6.1092

    Article  Google Scholar 

  42. Palani S, Liong SY, Tkalich P (2008) An ANN application for water quality forecasting. Mar Poll Bull 56(9):1586–1597. https://doi.org/10.1016/j.marpolbul.2008.05.021

    Article  Google Scholar 

  43. Šiljić A, Antanasijević D, Perić-Grujić A, Ristić M, Pocajt V (2014) Artificial neural network modelling of biological oxygen demand in rivers at the national level with input selection based on Monte Carlo simulations. Environ Sci Pollut Res 22(6):4230–4241. https://doi.org/10.1007/s11356-014-3669-y

    Google Scholar 

  44. Yaseen ZM, El-shafie A, Jaafar O, Afan HA, Sayl KN (2015) Artificial intelligence based models for stream-flow forecasting: 2000–2015. J Hydrol 530:829–844. https://doi.org/10.1016/j.jhydrol.2015.10.038

    Article  Google Scholar 

  45. Specht DF (1990) Probabilistic neural networks. Neural Netw 3(1):109–118. https://doi.org/10.1016/0893-6080(90)90049-Q

    Article  Google Scholar 

  46. Sawant SS, Topannavar PS (2015) Introduction to probabilistic neural network—used for image classifications. Int J Adv Res Comput Sci Softw Eng 5(4):279–283

    Google Scholar 

  47. Antanasijević D, Ristić M, Perić-Grujić A, Pocajt V (2014) Forecasting GHG emissions using an optimized artificial neural network model based on correlation and principal component analysis. Int J Greenh Gas Control 20:244–253. https://doi.org/10.1016/j.ijggc.2013.11.011

    Article  Google Scholar 

  48. Sözen A, Gülseven Z, Arcaklioğlu E (2007) Forecasting based on sectoral energy consumption of GHGs in Turkey and mitigation policies. Energy Policy 35(12):6491–6505. https://doi.org/10.1016/j.enpol.2007.08.024

    Article  Google Scholar 

  49. Pahlavan R, Omid M, Akram A (2012) Energy input-output analysis and application of artificial neural networks for predicting greenhouse basil production. Energy 37(1):171–176. https://doi.org/10.1016/j.energy.2011.11.055

    Article  Google Scholar 

  50. Kialashaki A (2014) Evaluation and Forecast of Energy Consumption in Different Sectors of the United States Using Artificial Neural Networks. Theses and Dissertations. Paper 628. University of Wisconsin-Milwaukee

  51. Jacobs G, Šlaus I (2010) Indicators of economic progress: the power of measurement and human welfare. CADMUS J 1(1):53–113

    Google Scholar 

  52. Costanza R, Hart M, Posner S, Talberth J (2009) Beyond GDP: the need for new measures of progress.The Pardee papers no. 4 - January 2009. Boston University, Boston, MA, USA. https://www.bu.edu/pardee/files/documents/PP-004-GDP.pdf

  53. Dogan E, Sengorur B, Koklu R (2009) Modeling biological oxygen demand of the Melen River in Turkey using an artificial neural network technique. J Environ Manage 90(2):1229–1235. https://doi.org/10.1016/j.jenvman.2008.06.004

    Article  Google Scholar 

  54. CIWM (2014) An introductory guide to healthcare waste management in England and Wales. Northampton, UK. https://www.ciwm-journal.co.uk/downloads/Healthcare-Waste-WEB.pdf. Accessed 8 Apr 2018

  55. Insa E, Zamorano M, López R (2010) Critical review of medical waste legislation in Spain. Resour Conserv Recycl 54(12):1048–1059. https://doi.org/10.1016/j.resconrec.2010.06.005

    Article  Google Scholar 

  56. Noori R, Karbassi A, Salman Sabahi M (2010) Evaluation of PCA and Gamma test techniques on ANN operation for weekly solid waste prediction. J Environ Manage 91:767–771. https://doi.org/10.1016/j.jenvman.2009.10.007

    Article  Google Scholar 

  57. Rimaityte I, Ruzgas T, Denafas G, Racys V, Martuzevicius D (2012) Application and evaluation of forecasting methods for municipal solid waste generation in an eastern-European city. Waste Manag Res 30:89–98. https://doi.org/10.1177/0734242X10396754

    Article  Google Scholar 

  58. Eurostat (2016) Glossary: purchasing power standard (PPS)—statistics explained. http://ec.europa.eu/eurostat/statistics-explained/index.php/Glossary:Purchasing_power_standard. Accessed 20 Apr 2016

  59. NSI (2016) GDP at Market prices per inhabitant in Euro and in PPS | National statistical institute Republic of Bulgaria. http://www.nsi.bg/en/content/5226/gdp-market-prices-inhabitant-euro-and-pps. Accessed 20 Apr 2016

  60. Weisz H, Krausmann F, Amann C, Eisenmenger N, Erb KH, Hubacek K, Fisher-Kowalski (2006) The physical economy of the European Union: cross-country comparison and determinants of material consumption. Ecol Econ 58(4):676–698. https://doi.org/10.1016/j.ecolecon.2005.08.016

    Article  Google Scholar 

  61. Harttgen K, Klasen S (2012) A household-based human development index. World Dev 40(5):878–899. https://doi.org/10.1016/j.worlddev.2011.09.011

    Article  Google Scholar 

  62. UNDP (2015) Human development report 2015. Work for human development. New York http://hdr.undp.org/sites/default/files/2015_human_development_report.pdf. Accessed 5 May 2016

  63. The World Bank (2014) World Development Indicators 2014. Washington: International Bank for Reconstruction and Development/The World Bank. https://openknowledge.worldbank.org/bitstream/handle/10986/18237/9781464801631.pdf?sequence=1&isAllowed=y. Accessed 5 May 2016

  64. Saygin D, Patel M, Tam C, Gielen D (2009) Chemical and Petrochemical sector. Potential of best practice technology and other measures for improving energy efficiency. IEA Information Paper OECD/IEA, pp 1–60

  65. Eurostat (2016) Simplified energy balances - annual data http://ec.europa.eu/eurostat/web/products-datasets/-/nrg_100a. Accessed 5 May 2016

  66. OECD (2002) Proposed standard practice for surveys of research and experimental development: “Frascati Manual 2002”, the measurement of scientific and technological activities. OECD Publications, Paris

    Google Scholar 

  67. The World Bank (2016) Life expectancy at birth. http://data.worldbank.org/indicator/SP.DYN.LE00.IN. Accessed 6 May 2016

  68. Ward T (2008) Material deprivation in the EU (Chapter 5). In: Ward T, Lelkes O, Sutherland H, Tóth I G (eds) Social inclusion and income distribution in the European Union - 2008, European Commission, Tárki, Budapest. pp 114–128. http://ec.europa.eu/social/BlobServlet?docId=3991&langId=en

  69. Eurostat (2016) Inability to face unexpected financial expenses (source: SILC) - Eurostat. http://ec.europa.eu/eurostat/en/web/products-datasets/-/ILC_MDES04. Accessed 6 May 2016

  70. Eurostat (2016) SCL—International statistical classification of diseases and related health problems (ICD-10 2007). RAMON-Reference and Management of Nomenclatures. http://ec.europa.eu/eurostat/ramon/nomenclatures/index.cfm?TargetUrl=LST_NOM_DTL_LINEAR&IntCurrentPage=1&StrNom=CL_ICD10&StrLanguageCode=EN. Accessed 17 Oct 2016

  71. Renaud O, Victoria-Feser MP (2010) A robust coefficient of determination for regression. J Stat Plan Inference 140(7):1852–1862. https://doi.org/10.1016/j.jspi.2010.01.008

    Article  MathSciNet  MATH  Google Scholar 

  72. Chai T, Draxler RR (2014) Root mean square error (RMSE) or mean absolute error (MAE)? Arguments against avoiding RMSE in the literature. Geosci Model Dev 7(3):1247–1250. https://doi.org/10.5194/gmd-7-1247-2014

    Article  Google Scholar 

  73. Pao H-T, Fu H-C, Tseng C-L (2012) Forecasting of CO2 emissions, energy consumption and economic growth in China using an improved grey model. Energy 40(1):400–409. https://doi.org/10.1016/j.energy.2012.01.037

    Article  Google Scholar 

  74. Willmott CJ, Robeson SM, Matsuura K (2012) A refined index of model performance. Int J Climatol 32(13):2088–2094. https://doi.org/10.1002/joc.2419

    Article  Google Scholar 

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Acknowledgements

The authors are grateful to the Ministry of Education, Science and Technological Development of the Republic of Serbia, Project No. 172007 for financial support.

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Correspondence to Vladimir M. Adamović.

Appendices

Appendix A. Details on the selected Inputs

Gross domestic product (GDP) at market prices expressed in purchasing power standard (PPS) eliminates the differences in price levels among countries, and allows the comparison of economies significantly different in absolute size. PPS is an artificial currency unit and theoretically one PPS can buy the same amount of goods and services in each country [58, 59].

Domestic material consumption (DMC) represents the sum of the annual amount of raw material extracted from the country and the difference of all physical imports and exports [60].

Human development index (HDI) is a composite index that measures the average achievement in each specific country in three fundamental dimensions of human development: long and healthy life, knowledge and decent standard of living. The indicators used to calculate HDI are: for the health component—life expectancy at birth, for the education component—mean years of schooling (for adults) and expected years of mean schooling (for children), and for the standard of living component—the log of the purchasing power parity (PPP)—adjusted Gross National Income (GNI) [61, 62].

Value added of industry (or agriculture) refers to the contribution of industry (or agriculture) to overall GDP. Value added is the net output of a sector (e.g. industry or agriculture) adding up all outputs and subtracting intermediate inputs. Value added in industry comprises value added in mining, manufacturing, construction, electricity, water and gas. Value added in agriculture comprises value added in livestock production and cultivation of crops, but also includes value added in forestry, hunting and fishing [63].

Final energy consumption includes information about annual data on quantities of crude oil, oil products, natural gas and manufactured gases, electricity and derived heat, solid fossil fuels, renewables and wastes covering the full spectrum of the energy sector from supply through transformation to final energy consumption by chemical and petrochemical industries [64, 65]. Final energy consumption in chemical and petrochemical industries for this study is normalized and expressed as kg of oil equivalent per capita.

Total intramural expenditure on research and development is in fact gross domestic expenditure on research and development in the specific country. It aggregates the total expenditure on research and development (RD) financed by a country’s institutions including research and development performed abroad but financed by national institutions—while it excludes RD performed within a country, but funded from abroad [66]. The funding sectors are: the business enterprise sector, the government sector, public general university funds, higher education sector and private non-profit sector.

Life expectancy at birth is an indicator that represents the average number of years that a new-born could expect to live if the prevailing patterns of mortality at the time of its birth were to stay the same throughout its life [67].

Data about the inability to face unexpected financial expenses were obtained through householder surveys on the capacity to cover unexpected cost from own resources. Unexpected costs refer to amounts equal to the poverty threshold for each specific country expressed as a monthly sum [68, 69].

Death rate, crude or crude death rate indicates the number of deaths occurring during the year, per 1000 inhabitants estimated at midyear [63].

Bed days indicate the number of hospitals days per capita for all causes of diseases except V00-Y98 (External causes of morbidity and mortality) and Z38 (live born infants according to place of birth) [70].

Appendix B. The model performance metrics used in this study

The coefficient of determination represents the degree of linear correlation between the predicted and observed values. This is a measure of the ability of the model to predict an outcome in the linear regression setting [71]. Although it provides limited information, R2 is often used due to its simplicity.

If O i is the observed value, P i is the predicted value, O m and P m are the means of the observed and predicted data, and n is the number of observations then the coefficient of determination can be shown as:

$${R^2}=1 - \frac{{\sum\nolimits_{{i=1}}^{n} {{{({O_i} - {P_i})}^2}} }}{{\sum\nolimits_{{i=1}}^{n} {{{({O_i} - {O_m})}^2}} }}.$$
(7)

If there is an intercept in the linear model, R2 is equal to the square of the correlation coefficient [71]:

$${R^2}={\left( {\frac{{\sum\nolimits_{{i=1}}^{n} {({O_i} - {O_m})({P_i} - {P_m})} }}{{\sqrt {\sum\nolimits_{{i=1}}^{n} {{{({O_i} - {O_m})}^2}\sum\nolimits_{{i=1}}^{n} {{{({P_i} - {P_m})}^2}} } } }}} \right)^2}.$$
(8)

The root mean squared error (RMSE) is the square root of the mean square error (MSE) which is the average of the squares of the difference between the actual and predicted values [72]. Due to the fact that the RMSE is expressed in the units of the variables, it is much more convenient and easier to interpret than the coefficient of determination [47],

$${\text{RMSE}}=\sqrt {\frac{1}{n}\left[ {\sum\limits_{{i=1}}^{n} {{{({P_i} - {O_{_{i}}})}^2}} } \right]} .$$
(9)

The mean absolute error (MAE) is the mean value of the absolute value of the difference between the observed and predicted values:

$${\text{MAE}}=\sum\limits_{{i=1}}^{n} {\frac{{\left| {{O_i} - {P_i}} \right|}}{n}} .$$
(10)

The mean absolute percentage error (MAPE) represents a measure of the accuracy of the predicted values in relation to the measured, expressed in percentages:

$${\text{MAPE}}=\frac{{100}}{n}\sum\limits_{{i=1}}^{n} {\frac{{\left| {{O_i} - {P_i}} \right|}}{{\left| {{O_i}} \right|}}} .$$
(11)

Generally, when MAPE is less than 10%, the forecast is highly accurate, at 10–20% the forecast is good, at 20–50% the forecast is reasonable, and for more than 50%, the forecast is inaccurate [73], but the limits used for the assessment of forecast accuracy may vary for different applications.

The percentage of predictions within a factor of the observed values (FA) demonstrates the ability of the model to give accurate prediction for each test case [47],

$${\text{FA}}1.1=0.9<\frac{{{P_i}}}{{{O_i}}}<1.1,$$
(12)
$${\text{FA}}1.2=0.83<\frac{{{P_i}}}{{{O_i}}}<1.2,$$
(13)
$${\text{FA}}1.25=0.8<\frac{{{P_i}}}{{{O_i}}}<1.25.$$
(14)

The index of agreement shows the degree of medium agreement between the actual and the predicted values, as well as the error between them. It is a relative and standardized statistical performance indicator with values between 0 (poor agreement) and 1 (excellent agreement) [74],

$${\text{IA}}=1 - \frac{{\sum\nolimits_{{i=1}}^{n} {{{({O_i} - {P_i})}^2}} }}{{\sum\nolimits_{{i=1}}^{n} {{{\left( {\left| {{P_i} - {O_m}} \right|+\left| {{O_i} - {O_m}} \right|} \right)}^2}} }}.$$
(15)

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Adamović, V.M., Antanasijević, D.Z., Ristić, M.Đ. et al. An optimized artificial neural network model for the prediction of rate of hazardous chemical and healthcare waste generation at the national level. J Mater Cycles Waste Manag 20, 1736–1750 (2018). https://doi.org/10.1007/s10163-018-0741-6

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