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Factores que aumentan la incidencia de inundaciones por Precipitaciones Pluviales en núcleos urbanos de la Ciudad Capital, Pana= má. Caso de estudio en la Ave. Domingo Diaz.

Factors that increase the incidence of flooding due to rainf= all in urban areas of the Capital City, Panama. Case study in Ave. Domingo Diaz Ave.

 

Isaac Ernesto Trejos Saucedo1, Gilda Achurra2.

 

1Escuela de Ingeniería Civil. Facultad de Ingeniería y Tecnología. Universidad Santa María la Antigua (Panamá).<= /o:p>

https://orcid.org/0000-0002-8486-576X<= /span>

=  

2Escuela de Ingeniería Civil. Facultad de Ingeniería y Tecnología. Universidad Santa María la Antigua (Panamá).<= /o:p>

https://orcid.org/0000-0003-0148-1056<= /span>

 

*Autor por correspondencia= : Isaac Ernesto Trejos Saucedo, isaac.trejos02@gmail.com

 

 

Recibido: 05 de abril de 2021

 Aceptado: 15 de julio de 2021<= o:p>

 

= Resumen

 

 Este trabajo ana= liza la situación de 7 kilómetros de la avenida Domingo Diaz a través de 7 núcle= os de inundacion, evaluados en los años 2016 y 2019 posterior a la construcció= n de obras civiles muy importantes como: la ampliación a cuatro carriles de la avenida Domingo Diaz y la construcción de la Línea 2 del Metro de Panamá, empleando revisiones fotográficas para detectar cambios en el comportamient= o de estos núcleos de inundacion, después de la construcción de cada obra en sus respectivos años de culminación. Se evalúa, a partir del comportamiento en = cada núcleo de inundacion, factores que inciden en sus réplicas de inundacion a través de los años, como el crecimiento urbano en la parte alta de las cuen= cas urbanas que discurren sobre la avenida Domingo Diaz, en sus 7 kilómetros analizados, el aumento de áreas impermeables, aumento del nivel del mar con respecto a la ciudad de Panamá y el creciente impacto por cambio climático = al que está expuesta toda ciudad. La amplia revisión bibliográfica, actual y pionera en su momento, de los factores que se estudian en el documento, muestran falencia existente en el área de análisis, así como dan a conocer = múltiples informaciones y reiteran lecciones aprendidas en otras latitudes, impactadas por estos mismos factores en ciudades costeras como la ciudad de Panamá.

El análisis mues= tra que todos los núcleos inundables evaluados en 2016, con réplicas de inundac= ion posterior a la ampliación a cuatro carriles de la avenida Domingo Diaz, mantienen su recurrencia de inundacion en 2019, posterior a la construcción= de la Línea 2 del Metro de Panama, a pesar de contar obras que "renovarían del sistema pluvial" siguen utilizando exclusivamente soluciones rígid= as grises insuficientes para resolver el problema de inundacion. Estas solucio= nes rígidas, ascienden con gastos de 273 millones de dólares, por la ampliación= a cuatro carriles de la avenida en 2016 y de 1,875 millones, por la construcc= ión de la Línea 2 del Metro de Panamá. Además, hasta la fecha el Ministerio de Obras Públicas (MOP) no incluye en sus Términos de Referencia, para aprobac= ión de planos para drenaje pluvial, ninguna consideración debida  a variaciones en el patrón de lluvias e= n los análisis hidrológicos  (Centroameri= cana, 2016), ni una integración entre el drenaje de agua de lluvia, la inundación= de agua de mar y la protección de la costa, ni de planificación urbana, ni pru= ebas de que el plan que sostiene de continuar con construcciones de obras estructurales rígidas más grandes, sea la mejor solución para mitigar los problemas de inundación en el núcleo de análisis.

 

Palabras clave: Domingo Diaz; Drenaje Pluvial; Crecimiento Urbano; A= umento del Nivel del Mar; Cambio Climático.

Abstract

 

          This work analyzes the situatio= n of 7 kilometers of Domingo Diaz Avenue through 7 flood centers, evaluated in 2016 and 2019 after the construction of essential civil works such as the extens= ion to four lanes of Domingo Diaz Avenue and the construction of Line 2 of the Panama Metro, using photographic reviews to detect changes in the behavior = of these flood centers, after the construction of each work in their respective years of completion. Factors affecting its flood replicas over the years include urban growth at the top of the urban basins running on Domingo Diaz Avenue. Its 7 kilometers analyzed, the increase in impervious areas, rising= sea levels relative to Panama City, and the growing climate change impact to wh= ich every city is exposed are assessed from behavior in each flood core. The extensive bibliographic review, current and pioneering at the time, of the factors, studied in the document, show lack existing in the area of analysi= s, as well as publicize multiple information and reiterate lessons learned in other latitudes, impacted by these same factors in coastal cities such as Panama City. Analysis shows that all flood-flood cores evaluated in 2016, w= ith post-extension flood replicas of four lanes of Domingo Diaz Avenue, maintain their flood recurrence in 2019, following the construction of Panama Metro = Line 2, despite counting works that would "renew the storm system" continue to exclusively use insufficient grey rigid solutions to solve the flood problem. These rigid solutions amount to expenses of $273 million, for the extension to four lanes of the avenue in 2016 and 1,875 million, for Li= ne 2 of the Panama Metro. In addition, to date, the Ministry of Public Works (MO= P) does not include in its Terms of Reference, for approval of plans for storm drainage, any consideration due to variations in the pattern of rainfall in hydrological analyses (Central American, 2016). Nor an integration between rainwater drainage, seawater flooding, and coastal protection, neither urban planning nor evidence that the plan contends to continue with more signific= ant rigid structural constructions is the best solution to mitigate flooding problems in the analysis core.

      

 Keywords: Domingo Díaz avenue; storm drain; urban growth; Ri= sing sea levels; climate change.


 

 

= Introducción

 

El alma de las carreteras es el = buen drenaje superficial (SIECA, Manual Centroamericano de Normas para el Diseño Geométrico de Carreteras, 2011), hoy por hoy, el agua sigue siendo el primer factor que disminuye la calidad de funcionamiento en una vía. Por esto, la capacidad de alejar las aguas lo más rápido posible de las carreteras en zo= nas urbanas sigue siendo un reto de la ingeniería moderna.

Ninguna característica en una ca= rretera tiene mayor influencia sobre la seguridad y confort de la conducción que el ancho y la condición de la superficie (Officials, 2011). =

El objetivo del diseño del drena= je pluvial de la carretera es proporcionar un paso seguro de vehículos durante= el evento de tormenta de diseño. A medida que aumenta la propagación desde la acera, aumentan los riesgos de accidentes de tráfico y retrasos, así como las molestias y posibles peligros para el tráfico de peatones (Administration, 2009).

Según el Banco Interamericano de Desarrollo se estima que en el 2040 el 70% de la población mundial vivirá en zonas urbanas (ONU, 2019). Y nuestra ciudad no escapa de este crecimiento, = en las últimas tres decenas de años, la ciudad ha experimentado un alto crecimiento demográfico, duplicando su población de 830 mil habitantes en 1= 990, a 1.4 millones en 2017 (Rockefeller, 2017). Este crecimiento, determinado en gran parte por la migración campo-ciudad aunado a los problemas socio-polít= icos de muchos vecinos en América Latina y el Caribe ha resultado por triplicar = la huella urbana, al pasar de 12 mil hectáreas en 1990 a más de 33 mil y creci= endo en la actualidad. Hoy la huella urbana de la ciudad, supera los 80 kilómetr= os de Este a Oeste (BID, 2015).

Los gestores de la carretera de = todo el mundo se enfrentan a fenómenos climáticos, aumento de áreas urbanas y catástrofes naturales cada vez más frecuentes y graves. En los últimos 20 a= ños, las pérdidas económicas notificadas debido a fenómenos meteorológicos extre= mos han aumentado un 151 % en comparación con el período 1978-1998, alcanzando = los 2.250 millones de dólares estadounidenses (UNISDR, 2017).

Según el Plan Naci= onal de Seguridad Hídrica 2015-2050, en los últimos 5 años, el Estado Panameño ha invertido cerca de US$ 331.03 millones en reconstrucciones de asentamientos= por eventos climatológicos extremos, todos relacionados con el agua (Panamá C. N., 2015).

En la última décad= a, a nivel nacional, se ha registrado un incremento del número de personas afect= adas anualmente por desastres naturales, pasando de 4,623 en el 2001 a 19,950 en= el 2011, siendo los años con el mayor número de afectados el 2008 y 2010, con = más de 65 mil personas afectadas durante cada uno de esos años (Desastres, 2019).

El Sistema Nacional de Protección Civil (SINAPROC) no cuenta con información pública sobre el costo anual que generan las inundaciones en el núcleo urba= no de análisis, ni en el resto de la ciudad de Panamá, en movilización de rescatista, equipo, contención de daños, reorganización de familias damnificadas y la reconstrucción de propiedad privada y pública. Los datos = almacenados en la base de datos de DESINVENTAR dan una idea sobre esta información. Seg= ún la base de datos las inundaciones de 2008 alcanzaron costos por 15,000,000 millones de dólares, en 2010 (con la Purísima) cerca de 149,000,000 millone= s, en 2013 500,000 mil dólares y en 2018 cerca de 128,000 mil dólares <= span lang=3DEN-US style=3D'font-size:10.0pt;line-height:115%;font-family:"Times = New Roman",serif; color:black'>(Desastres, 2019). Estos datos son solo los registrados= en la plataforma, por lo que podrían ser valores superiores a estos números. E= s de esperarse que la inundación terrestre, es el evento de riesgo más costoso q= ue resguarda el Sistema Nacional de Protección Civil.

 =

Propuesta  

 

El objetivo de este estudio es comprender los factores que inciden en las inundaciones en 7 kilómetros del núcleo urbano ubicado en la avenida Domingo Diaz, desde las proximidades del cruce de la Domingo Diaz con el rio Matías Hernandez hasta pasado el cruce = del rio Juan Diaz con la misma avenida. Se evaluarán, específicamente, 7 nodos = de inundación comparando su comportamiento en los años 2016 y 2019 posterior a= la rehabilitación del sistema de drenaje pluvial existente posterior a la construcción de obras civiles importantes.

La decisión sobre el núcleo de estudio fue con base en una observación continua del estado de la avenida Domingo Diaz en el periodo 2016 y 2019 y su comportamiento en época lluvios= a.

La observación permitió encontra= r un comportamiento repetitivo, al de 2016, sobre la Domingo Diaz en el periodo = en 2019, las zonas inundables, dentro del núcleo de análisis, eran las mismas en amb= os periodos de tiempo. De todas las zonas inundables tres presentaban el mayor grado de vulnerabilidad, todas en áreas cercanas a los cruces de cauces a lo largo de la vía. Dentro de los 7 kilómetros del área de análisis se encuent= ran los ríos Matías Hernández, Palomo y Juan Diaz que fueron observados como el área más vulnerable de la avenida Domingo Diaz. 

 =

Pregunta 1. ¿Cuáles son los fact= ores de incidencia, de las inundaciones en el área de estudio?=

Pregunta 2. ¿Los planes actuales= de las instituciones públicas funcionarán para resolver el problema o siguen el mismo camino de años anteriores?

Pregunta 3. ¿Cuál es la posibili= dad del área de análisis para aumentar su resiliencia y minimizar las inundacio= nes?

 =

Una mirada al pasado en busca de respuestas

 

Una definición poética sobre las carreteras la escribió el ingeniero panameño Elías Allain en 1977: “El desarrollo vial de un país siempre ha representado un factor muy importante, para planificador, urbanista, gobernador, etcétera. Puesto que una vía tiene implicaciones profundas en la vida de una región. Su radio de acción es eno= rme y sus efectos repercuten en la economía, cultura, e incluso en la estructura física social de los hombres”.

 

El primer paso de la nueva repúb= lica en pro del desarrollo del país data del 23 de febrero de 1904, cuando media= nte el decreto No. 3, se creó la Secretaría de Obras Públicas, que cumplía el objetivo de satisfacer la necesidad de contar con una institución responsab= le de la construcción y el mantenimiento de las diferentes obras del Estado en= el primer período republicano de nuestro país. Pero no fue hasta 1920 cuando se crea la Junta Central de Camino (1920 a 1936) (Chong, 1998), creada con el objetivo de proveer al país de vías terrestres de comunicación que facilita= rán primordialmente las relaciones económicas y la fácil injerencia del Estado sobre el resto del país.

 

 SEQ Ilustración = \* ARABIC 1. Una avenida d= el Barrio de la Exposición en 1930. (500, 2017)

De ahí para las próximas décadas se inicia la constru= cción de estructuras que recojan el agua que escurre de la superficie del camino debido al bombeo, así como también la que escurre desde sus taludes a los extremos de la vía, estas estructuras llamadas “cunetas”, iban de acuerdo c= on la cantidad de agua que debía escurrir ajustado también a la amplitud de rodadura o ancho del camino.

A finales de la década de los años 60, ya se había prescindido de las cunetas rectangulares por su baja capacidad de movilizar basura y elementos naturales que caían en ella, empozando y manteniendo cantidades de agua suficientes para producir mosquitos, malos olores y bajos rendimientos de escurrimiento. 

 

<= i>Ilustración <= /a>2. Tipos de Cunetas utilizadas para la de carga de aguas pluviales. (Tello, 1977)

Análisis de factores que inciden en la recurrencia de inundaciones por precipitaciones pluviales en = el área de estudio

=  

1.   &n= bsp;   Crecimiento urbano en la parte alta de = las cuencas y aguas abajo de las mismas

 =

Según el profesor Ángel Rubio “el despe= rtar por la preocupación del ordenamiento territorial de la ciudad comienza en 1= 940 con el Informe y Plan Regulador presentado por Kart Brunner y sigue después= con la creación del Banco de Urbanización y Rehabilitación en 1944” (Gordo= n, 2019). Ya en 1977 se planteaba un gran número de conexiones, tanto longitudinales como transversales, esto para garantizar la conectividad entre las troncales de = la ciudad y dirigir con esto hacia donde ubicar el crecimiento urbano.

El Metro de Panamá se ha convertido en ese “regulador urbano” de la ciudad con la construcción de las Líneas 1 y 2 del Metro de P= anamá transformando a partir de estas nuevas líneas avenidas existentes en arteri= as suburbanas como parte del plan de integral del metro, un plan que no cuenta= con todas las medidas de mitigación a posibles problemas causados en su proceso “urbano”.

(Uribe A., 2020) cuenta que “La arteria metropolitana= por la que transcurrirá el metro tiene actualmente un carácter suburbano que se modificará con la aparición de las estaciones de metro. Entorno a éstas se deberán planificar áreas de centralidad, que dotarán al eje de una sucesión= de subcentros de actividad entorno a las estaciones. Igualmente, los espacios entre las estaciones serán referencias de centralidad para las zonas aledañ= as, por lo que la Avenida Domingo Díaz deberá en realidad transformarse de arte= ria suburbana, prolongación de una carretera interestatal, en un corredor de centralidad urbana vertebrador de la ciudad. Para cumplir con este objetivo= es necesario identificar las actuaciones que permitirán aprovechar las oportunidades que abre la nueva infraestructura, y multiplicar sus impactos positivos.

Las actuaciones en su conjunto se alinean con una vis= ión estratégica general que dirige la transformación de esta parte de la ciudad= y que en este caso se condensa en un gran objetivo transformador: la reconver= sión de la Avda. Domingo Díaz en un eje urbano vertebrador de la ciudad, basado = en la presencia del transporte masivo.”

 

Aguas arriba de los ríos Matías Hernánd= ez, Palomo y Juan Diaz el crecimiento urbano sigue aumentando con los años. Gra= cias a las imágenes satelitales se logra ver los cambios en el uso de suelo aguas arriba.

Desde 2002 la huella urbana aguas arrib= a de las cuencas, han experimentado un crecimiento continuo, contando en 2002 con 1,883 hectáreas hasta hoy en 2020 contar con 1,341 hectáreas con una pérdida del 28,78% de la cobertura vegetal. En las imágenes también se muestra las ubicaciones de desarrollos urbanos aislados dentro de la zona verde, marcad= os en color morado (ver ilustración 3), que en 2002 no representaban poco meno= s de 4 hectáreas para contar hoy con 68 hectáreas cubiertas dentro de la zona ve= getal existente. Si restamos esa área de 68 hectáreas a la zona total existe pasaríamos de 1,341 hectáreas a solo 1,273 hectáreas de área verde aguas ar= riba de los ríos. 

Hoy, no existen un límite urbano ni zon= as de expansión planificadas, pues no existe una estrategia metropolitana de crecimiento, experimentándose un crecimiento de la huella urbana aleatorio y desorganizado. Esto a pesar de los esfuerzos por parte del Municipio de Pan= amá y la sociedad civil de crear y aprobar el POT (Plan de Ordenamiento Territo= rial) a la fecha no se logrado un acuerdo para aprobarlo.  

Ilustración = 3. Crecimiento urbano aguas arriba de las cuencas analizad= as dentro del área de análisis. Elaboración propia

 

Además, aumentan las viviendas ubicadas en suelos con pendientes superiores al 30% (MUPA B. , 2017). Hoy el 8,38% = de la huella urbana actual está afectada por algún tipo de inundación. El aumento de las zonas impermeables en las áreas que discurren a lo largo de = la avenida Domingo Diaz ha mantenido un incremento considerable. Para 2003 el = área permeable de las áreas que discurren en la Domingo Diaz llegaba a ser 147 H= a y en 17 años se redujeron en un 35.6%, quedando a ser poco más de 57 Ha.=

Los desarrollos causan pérdida de masa verde (mayormente tala y quema de árbole= s), rápidos deslaves y erosión de las superficies no protegidas que causan sedimentación en el lecho de los ríos y los canales de drenaje, y la pérdid= a de posibles áreas de inundación y retención a lo largo del sistema fluvial. Es= te incremento en áreas pavimentadas resulta en un excedente de aguas de pluvia= les que abruma el sistema, el cual no ha sido adaptado para el incremento del deslave  (Bajos, 2015).

En un artículo publicado en la revista de Geología de los Estados Unidos en su circular 554 en 1968 ya se venían anunciando investigaciones referentes al impacto de la urbanización avanzada y los problemas que causaría al entorno sino eran tratados sus efectos, citando el artículo, describen:  “Hay cuatro efectos interrelacionados p= ero separables de los cambios en el uso de la tierra en la hidrología de un áre= a: cambios en las características del flujo máximo, cambios en la escorrentía total, cambios en la calidad del agua y cambios en las amenidades hidrológi= cas. Las amenidades hidrológicas son lo que podría llamarse la apariencia o la impresión que el río, su cauce y sus valles, dejan al observador (Leopold, 1968)”.

En otro famoso articulo nombrado: “How Urbanization Affects the Water Cycle= ” traducido sería algo como “Cómo afecta la urbanización al ciclo del agua” se reza que “Las superficies impermeables asociadas con la urbanización altera= n la cantidad natural de agua que toma cada ruta. Las consecuencias de este camb= io son una disminución en el volumen de agua que se filtra en el suelo, y un aumento resultante en el volumen y disminución en la calidad del agua superficial” (Partnership, 2007). Y sobre las zonas con un alto grado de urbanización comentan que “En áreas altamente urbanizadas, más de la mitad = de toda la lluvia se convierte en escorrentía superficial, y la infiltración profunda es solo una fracción de lo que era naturalmente” (Partnership, 2007). La disminución de flujo que se infiltra y el aumento de agua superficial pasa de 10% a 55%.  A medida que se acort= a el tiempo necesario para que se escurra una determinada cantidad de agua, aume= nta la tasa máxima de escorrentía (pico de inundación) (Leopold, = 1968).

El crecimiento urbano reduce la infiltración, el flujo base y los tiempos de demora y, al mismo tiempo, aumentan drásticamente los volúmenes de flujo de aguas pluviales, la descarga máxima, y la escorrentía superficial (Du, y otros, 2012).

La relación lluvia- escorrentía, de la cual, el aumento de la pendiente, de las áreas provoca una disminución del tiempo de concentración (el cual se define como el tiempo mínimo necesario para que todos los puntos de una cuenca est= én aportando agua de escorrentía de forma simultánea al punto de salida) y pic= os de descarga más altos (SIECA, Manual de Consideraciones Técnicas Hidrológicas e Hidráulicas para la Infraestructura Vial en Centroamérica, 2016). Siguiendo en = ese sentido, este estudio busca conocer el incremento de escorrentía superficia= l, agua superficial que llega a la vía, por el aumento del área permeable en las zo= nas que discurren sobre la avenida Domingo Diaz como parte del crecimiento urba= no. Para esto se utilizo el método SCS, que para análisis de lluvia-escorrentía puede aplicarse para determinar el incremento en la cantidad de escorrentía= que se origina por la urbanización (Chow, Maindment, & Mays, 1994).

SCS (Soil Conservation System= ) por sus siglas en inglés, calcula el flujo máximo en función del área de la cue= nca de drenaje, el almacenamiento potencial de la cuenca y el tiempo de concentración. El procedimiento estudia la relación lluvia-escorrentía, sep= ara la precipitación total en escorrentía directa, retención y extracción inici= al para producir la siguiente ecuación para la escorrentía de lluvia (FHWA, 2009).

dónde:

= =3D profundida= d de escorrentía directa, mm (pulg);

= =3D Profundida= d de precipitación de 24 horas, mm (pulg); Esta información está disponible en la mayoría de los manuales de drenaje de las agencias de carreteras al multipl= icar la intensidad de lluvia de 24 horas por 24 horas.

= =3D Retención,= mm (pulg).

=  

Los estudios empíricos encontraron que la  está relacionada con el tipo de suelo, la cobertura terrestre y la condición de humedad antecedente de la cuenca. Est= os están representados por el número de la curva de escorrentía, CN, que se utiliza para estimar SR con la siguiente ecuación (Suelos, 1972).

 

 

dónde:

=3D Número de curva, enumerado en la Tabla 3-6 para diferentes usos de la tierr= a y tipos de suelo hidrológico. Esta tabla asume condiciones de humedad antecedentes promedio;

=3D Factor de conversión de unidades igual a 25,4 (1,0 en unidades inglesas).

 

Dentro del Plan Panamá Resiliente promovido por el BID (Banco Interamericano de Desarrollo) a través del Municipio de Panamá se entregó en uno de sus anexos, los estudios hidrológi= cos realizados dentro del Estudio integral de actuaciones de mitigación de inundaciones en la cuenca del rio Juan Díaz. En este estudio, al cálculo de caudales se le aplico valores de Número de Curva o SCS para la condición de humedad antecedente tipo II y se han considerado que los suelos de toda la cuenca, misma que nuestra área de análisis, son de tipo C (suelos de lenta infiltración), de acuerdo con su naturaleza edafológica y con las pendiente= s de la zona media y alta del cauce (CANTABRIA & BID, Estudio de Factibilidad de actuaciones de Mitigacion de inundaciones en la cuenca baja de Juan Diaz, 2016).

 

Los datos de lluvia para realizar la estimación lluvia- escorrentía sobre el nú= cleo de análisis se utilizaron las Curvas IDF presentadas en la investigación de 2015 de Lau y Pérez (Lau & Perez, 2015), donde se demuestra que las curvas IDF plasmadas para la cuenca del rio Juan Diaz, cuenca del pacifico 144 específicamente, en el Manual de Requisitos p= ara la revisión de Planos de Drenaje Pluvial del MOP, no entrega valores representativos para la condición actual de la cuenca. En efecto, una de las causas de inundación en Panamá es la estimación inapropiada (Lau & Perez, 2015) de valores de intensidad de lluvia. En la misma investigación de (Lau & Perez, 2015)  en página 168, la gráfica 5.6: Curvas I= DF de las cuencas ubicadas en el Pacífico y la curva del MOP para 10 años de peri= odo de retorno, hasta 3 horas de duración, muestra la diferencia de valores par= a un periodo de retorno de 10 años entre las gráficas existentes en el manual del MOP y los nuevos valores conseguidos por (Lau & Perez, 2015). Para nuestro = análisis, los valores de lluvia con un periodo de retorno de 10 años se tomarán de la= s gráficas de (Lau & Perez, 2015).  

Pa= ra los Grupos Hidrológicos del Suelo, los valores fueron sacados del Estudio de Factibilidad de Actuaciones de Mitigación de Inundaciones en la cuenca Baja= de Juan Diaz, Anexo VII: Estudios Hidrológicos elaborado por IH Cantabria y BI= D, estos valores son 86 para Áreas Pobladas (2017) y 71 Bosques Secundarios (2017) y= 79 para Áreas Pobladas (2003) y 71 Bosques Secundarios (2003). El valor de los Bosques Secundarios mantiene con su valor de 71 por no ser modificada su ár= ea en el tiempo.

Ilustración = 4. Micro cue= ncas de análisis con zonas con la condición de humedad antecedente tipo II (tipo= C: suelos de lenta infiltración). Elaboración Propia y (CANTABRIA & BID, Estudio de Factibilidad de actuaciones de Mitigacion de inundaciones en la cuenca baja de Juan Diaz, 2016).

El impacto sobre la escorrentía superf= icial por el aumento de las zonas impermeables desde 2003, ha aumentado en 6.8= 1%. Eso significa que en el núcleo de análisis para lluvias con un periodo de retorno de 10 años existe un excedente de 11.09 mm/h en lluvias de diseño con tiempo de concentración de 10 minutos.

Esto con base en datos meteorológicos y aproximaciones matemáticas sin lograr evaluar datos directos del sitio de estudio, como concluye (Lau & Perez, 2015) “A = pesar de pertenecer a la misma vertiente, las intensidades de eventos extremos generados en las cuencas presentan grandes variaciones entre ellas como par= a considerarse utilizar una ecuación general por vertiente, ya sea Atlántico o Pacífico. En consecuencia, sería más apropiado aplicar la ecuación de la cuenca correspo= ndiente, sobre todo si la ecuación del MOP subestima la intensidad del sitio de estu= dio”.

 

Para ampliar el impacto so= bre el ciclo hidrológico producido por la urbanización, analizaremos un concepto introducido desde 1958 por Gordon Manley de la Universidad de London quien llamo “islas de calor” a la diferencia de temperatura entre un área urbana = y su entorno rural. Una definición más detallada la da (Oke, Johnson, Steyn, & Watson, 1991) y (Mirzaei, 2015)<= !--[if supportFields]> que definen las islas de calor como el calor de origen antropogénico, la alteración o bloqueo de los patrones de vientos, la alta absorción de radiación solar debido a la implementación de materiales artificiales superficiales que sustituyen la cobertura natural, y en ocasio= nes con un mayor bloqueo de las emisiones al cielo de onda corta y larga debido= al efecto obstructivo de los edificios.

La expansión urbana y sus islas de cal= or urbanas asociadas también tienen impactos mensurables en los procesos meteorológicos y climáticos, también puede afectar el ciclo global del agua= a través del desarrollo de nubes y precipitaciones en las ciudades y sus alrededores (Shepherd & Burian, 2003). 

Al= gunas ciudades del mundo con estudios de islas de calor muestran de manera ilustrativa el aumento de calor y vientos a favor que generan las zonas más pobladas en una ciudad.

"Las ciudades tienden a ser de uno a 10 grados Fahrenheit [.56 a 5.6 Celsius] más cálidas que los suburbios circundantes y= las áreas rurales y el calor adicional puede desestabilizar y cambiar la forma = en que el aire circula alrededor de las ciudades", en promedio, las tasas máximas de lluvia en las regiones a favor del viento a menudo excedían los valores máximos en las regiones en contra del viento en un 48% - 116%  (Daily, 2002). Principalmente durante los meses más cálidos, el calor agregado crea circulaciones de viento y aire ascendente que pueden producir nubes o mejor= ar las existentes. En las condiciones adecuadas, estas nubes pueden convertirs= e en productoras de lluvia o tormentas. Se sospecha que el aire convergente debi= do a las superficies de las ciudades de diferentes alturas, como los edificios, también promueve la elevación del aire necesario para producir nubes y lluv= ia (Shepherd & Burian, 2003).

 

2.   &n= bsp;   Aumento en el nivel del mar =

 =

El riesgo de eventos naturales como inundaciones podría ser incrementado por el cambio climático. La alteración de ciertos patrones meteorológicos, como, p= or ejemplo: el potencial aumento del ritmo de subida del nivel del mar en zonas costeras- 60 de las 77 ciudades más densamente pobladas de América latina e= stán situadas cerca de la costa-, el cambio de patrones loca­les de precipitació= n y el potencial incremento de la frecuencia de tormentas, el cambio de la frecuencia y duración de sequias, así como la actividad de ciclones tropica= les intensos, podría ser asociada a un clima más caluroso (Brakel, y otros, 2017)= . Estas alteraciones podrían ser motor= es de mayores inundaciones con sus correspondientes impactos (Mundial, 2016)<= !--[if supportFields]>.

Lo= s retos relacionados con el sistema hídrico de la Ciudad de Panamá incluyen riesgos= de inundaciones (precipitación, desbordamiento de ríos y elevación del nivel d= el mar) (CANTABRIA & MUPA, Informe de la Misión del Equipo Holandés de Reducción de Riesgo en la cuenca del río Juan Díaz (Resumen-Ejecutivo), 2016). Según el Plan Estratégico de Gobierno (PEG15-19), se estima que el costo anual actual por eventos climáticos recurrentes en el país oscila entre B/.125 y 150 millones/año (0,36% a 0,42% del PIB) (Agropecuario, 2018). La data científica ha documentado un incremento en el nivel medio del Mar Caribe, en la entrada Norte del Canal = de Panamá. Según las estadísticas, el nivel medio del mar caribe pasó de 0,024 pies (0.73 cm) en 1925 a 0,90 pies (27 cm) en 2010 (Jimenez, 2018).

En= la escala global el aumento del volumen de agua en los océanos debido al calentamiento climático fue más de 15 cm en últimos cien años. Se predice que el cambio climático causara un aumento= del nivel del mar de cerca 30 cm para el año 2050, que medido para la ciudad de Panama alcanza los 27 cm en 2010, debido al deshielo de los glaciales y por= la expansión térmica de la capa superficial del océano (Kwiecinski & Cr= uz, 2008)= . El incremento del nivel del mar en el pacífico p= anameño no escapa de esta realidad, en 2008 una investigación del departamento de Biología Marina y Limnología de la Universidad de Panamá estimo el incremen= to del nivel del mar en la costa del pacífico panameño desde 1909 a 2100. Un estudio de 2016 (Panamá G. d., 2016), concluye que en el último siglo el nivel del mar en el pacífico panameño aumento aproximadamente en 20 cm y se estima que antes de final de siglo incremente cerca de 55 cm.  Históricamente, el aporte de Panamá a las emisiones globales de GEI ha representado el 0,02%; y las emisiones per cáp= ita de GEI indican que el país no contribuye significativamente al cambio climático. No obstante, Panamá es sumamente vulnerable a sus efectos y ya enfrenta los impactos de este (Panamá G. d., 2016).

3.   &n= bsp;   Cambio Climático, modificación en los patrones de lluvia sobre el área de análisis=

 =

La precipitación es un eslabón clave e= n el ciclo global del agua y una comprensión adecuada de su carácter temporal y espacial tendrá amplias implicaciones en el diagnóstico y la predicción del clima, el análisis y la modelización del ciclo global del agua y la energía (GWEC), la previsión meteorológica, la gestión de los recursos de agua dulc= e y los procesos de la interfaz tierra-atmósfera-océano (Shepherd & Burian, 2003). Las consecuencias del cambio climático en los sistemas hídricos urbanos incluyen, por una parte, temperaturas más altas, menos precipitaciones y se= quías más graves; una mayor frecuencia de las lluvias torrenciales y de los episo= dios de inundaciones. Precisamente estos extremos hacen que la planificación del espacio urbano y la creación de infraestructura resulten tan complicadas (ONU, = Informe Mundial de las Naciones Unidas sobre el desarrollo de los recursos hidricos 2020: agua y cambio climatico. , 2020).=

Las precipitaciones en la ciudad y la escorrentilla superficial proveniente de lugares más altos en las cuencas, = por lo que drenar adecuadamente en los cuerpos de agua circundantes se vuelve complicado para un sistema rígido de control de aguas superficiales, como lo existente. En el mapa de inundaciones que se muestra en la ilustración 5, d= onde se agregan estimaciones por impacto del cambio climático se puede observar = el impacto de las precipitaciones para un periodo de retorno de 100 años y los distintos tipos de calado inundable.

 

Ilustración = 5. Zonas inundables en el área de estudio para un periodo de retorno de 100 años. (MUPA, Wetlands, & Bajos, Diálogos del Agua: Construyendo solucio= nes sostenibles juntos., 2016)= y Elaboración Propia.<= /span>

Este tipo de fenómenos aquejan las ciudades en medidas avanzas cada año, de ahí la necesidad de adaptar los diseños de control de aguas pluviales a estas variaciones o a su prevencion/mitigacion. En el Manual de Consideraciones Tecnicas Hidrologica= s e Hidraulicas para la Infraestructura Vial en Centroamérica publicado por el SICEA en 2016, el Ministerio de Obras de Panama aporto a este documento la siguiente informacion sobre consideraciones debidas a variaciones en el pat= rón de lluvias en los análisis hidrológicos:

·&nb= sp;        Ha= sta la fecha de realización de este documento, MOP no incluye en sus Términos de Referencia alguna consideración debida a variaciones en el patrón de lluvia= s en los análisis hidrológicos (Centroamericana, 2016)<= /i>.

El clima panameño está dictado por su posición, orientación de su estrechez, la influencia de la zona de converge= ncia intertropical c (ver ilustración 6) y las interacciones océano-atmósfera. El anticiclón semipermanente del Atlántico Norte afecta sensiblemente las condiciones climáticas de nuestro país, ya que desde este sistema se generan los vientos alisios del nordeste que en las capas bajas de la atmósfera lle= gan a nuestro país, determinando sensiblemente el clima de la República. Existe= una zona de confluencia de los vientos alisios de ambos hemisferios (norte y su= r) que afecta el clima de los lugares que caen bajo su influencia y que para nuestro país tiene particular importancia: la Zona de Convergencia Intertropical (ZCIT), la cual se mueve siguiendo el movimiento aparente del= sol a través del año. Esta migración norte-sur de la ZCIT produce las dos estaciones (seca y lluviosa) características de la mayor parte de nuestro territorio. (ETESA, 2020)= <= span style=3D'font-size:10.0pt;font-family:"Times New Roman",serif;color:black; mso-ansi-language:ES-PA'>.

(Fábrega, Nakaegawa, Pinzón, & Nakayama., 2013) analizaron cua= tro regiones, y que cubren, estas cuencas, aproximadamente el 43% de Panamá. Las cuencas de las regiones de Bocas del Toro y del Canal de Panamá del Canal de Panamá que desembocan en el Océano Atlántico, mientras que las cuencas correspondientes de las regiones de Veraguas y Darién descargan en el Océano Pacífico.

En 2013 se publicó el experimento de <= w:Sdt Citation=3D"t" ID=3D"899711208">(Fábrega, Nakaegawa, Pinzón, & Nakayama., 2= 013) quienes a trav= és de MCGA (Atmospheric Global Circulation Models), una explicac= ión más completa sobre los  MCGA (Atmospheric Global Circulation Models) <= /span>de malla de 20 km vea Mizuta et al. (2006), con malla de 20 km utilizaron un análisis en el tiempo para el pres= ente y el futuro: para el presente (1979-2002), emplearon valores mensuales de temperatura de la superficie del mar (TSM) y la concentración de hielo mari= no; para el futuro (2075-2099).

La ilustración 6 muestran las proyecciones hidro climáticas futuras para la precipitación, la evaporación= y la escorrentía total en el MCGA de malla de 20 km. La precipitación futura parece aumentar para todas las regiones en al menos un 5%, con la excepción= de algunas zonas de la región de Bocas del Toro. Cabe señalar que incrementos superiores al 15% se proyectaron para las zonas más pobladas de Panamá. (Fábrega, Nakaegawa, Pinzón, & Nakayama., 2= 013).

Ilustración 6. (izquierda; a-c) Cambios de la varia= ble hidrológica media anual climatológica en el clima futuro en relación con el actual. (Fábrega, Nakaegawa, Pinzón, & Nakayama., 201= 3).

= 4.&n= bsp;       Estado del sistema de drenaje actual =

Según el Informe “Reducción de Riesgo = en la cuenca del Río Juan Díaz” presentado por IH CANTABRIA al Municipio de Pa= namá la principal causa por el momento, en las áreas que discurren aguas debajo = de la cueca del rio Juan Diaz, es probablemente la insuficiente capacidad de l= os ríos, flujos, alcantarillados y cloacas debido al alto incremento de las corrientes que ocurren en las áreas en constante proceso de urbanización (BID & CANTABRIA, Estudio Intengral de actuaciones de mitigacion de Inundaciones en la cuenca del rio Juan Diaz, 2016).

 

 

Nodo 7

Nodo 6

Nodo 5

Nodo 4

Nodo 3

Nodo 2

Nodo 1

 

Ilustración 7= . Nodos de inundación observados en ár= eas de análisis. Elaboración propia.

 

La ilustración 7 muestra los nodos de = inundacion encontrados de 2016 en el área de análisis y evaluados hasta 2019. La ubica= ción de los nodos es la siguiente:

 

Nodo 1. Se ubica diagonal a la Cárcel de Mujeres antes del cruce del rio Matías Hernández.

Nodo 2. Se ubica diagonal a Ricardo Pérez sobre la Domin= go Diaz justo antes del acceso a P.H. Mystics Hills.

Nodo 3 y 4. Nodo 3 se ubica justo encima del cruce del rio Palomo y el Nodo 4 se ubica debajo del puente vehicular de la avenida Manuel Zarate.

Nodo 5 y 6. Nodo 5 se ubica justo después del cruce del aflue= nte del rio Espave y antes del Patio de Buses de Mi Bus en los Pueblos y el Nod= o 6 se ubica diagonal a Farmacias Arrocha de los Pueblos y justo en frente a la parte frontal de Metromall.

Nodo 7. Se ubica pasado el cruce del rio Juan Diaz con la avenida Domingo Diaz y ju= sto en frente a la Universidad Americana.

 

La observación= de los nodos permitió conocer las zonas afectadas por inundaciones y conocer si existía una relación de recurrencia entre estos años. Todo el análisis de l= as revisiones, para cada nodo, en los años 2016 y 2019, a través de registros fotográficos están resumidas en la tabla 1.

In= iciando en el año 2016 luego de la culminación de las obras de Ampliación a cuatro carriles de la avenida Domingo Diaz realizadas por el Consorcio ICA-MECO po= r un monto de 273 millones de dólares  CITATION Cin14 \l 2058 (Almanza, 2014) hasta el año 2019 posterior a la culminación del nuevo sistema de drenaje pluvial de la avenida Domingo Diaz= por la construcción de la Línea 2 del Metro de Panamá bajo un costo de 1,875 billones de dólares (Telemetro, 2019).

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

&n= bsp;

Tabla <= /span>1. Tabla Resumen: obra civil y recurren= cia de inundación en los años 2016 y 2019.

 

 

Co= mo se muestra en las tablas 1 y 2, cada nodo cuenta con problemas de inundación recurrentes desde 2016, cada nodo sostuvo sus réplicas de inundación en 2019 luego de adecuaciones a la mediana y modificaciones a gran parte de los acc= esos sobre la avenida con la construcción de la Línea 2 del Metro de Panamá.


<= o:p> 

<= o:p> 

<= o:p> 

<= o:p> 

<= o:p> 

<= o:p> 

<= o:p> 

<= o:p> 

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<= b>=  

Tabla 2. Tabla Resumen: recur= rencia de inundación en los años 2016 y 2019.

 

Estado 2016

Estado 2019

Nodo 1

Nodo 2

Nodo 3

Nodo 4

Nodo 5

Nodo 6

Nodo 7

Es= ta investigación ha mostrado lo ineficiente que han sido las soluciones grises (obras civiles exclusivamente de construcción, rígidas y con límites de diseño: cunetas longitudinales, tragantes, parrillas, tubos de descarga y cordones cunetas) para mantener un mínimo de funcionalidad ante los cambios y modificaciones = climáticas. Por ejemplo, los tragantes construidos en 2016 contaban con una abertura de acceso para la lámina de agua de 10 cm y en 2019 cuentan con una abertura de acceso de 35 cm, un aumento del 350% en la abertura para controlar el aumen= to de escorrentía y su velocidad de acceso, función que no se cumple aun en 20= 19. Los tragantes con aberturas de 35 cm siguen sin tener la capacidad de absor= ber la lluvia en época lluviosa ni con la llegada de lluvias extraordinarias propias de modificaciones climáticas inducidas o naturales, debido a que un sistema rígido sin capacidad de adaptación.

En cada uno de los años estudiados, el sistema de drenaje pluvial se encontraba aprobado por el Ministerio de Obras Públicas y con dichas obras entregadas = por el contratista a totalidad.

Co= mo se demostró a través de las ilustraciones, las nuevas estructuras de drenaj= e de 2019 solo impactaron la mediana de la Domingo Diaz, los borde= s de la vía, en los núcleos de inundacion, aún mantienen el mismo sistema de dre= naje pluvial desde 2016.

 Ilustración 8. Altura de estructura de drenaje construido en = 2016 sobre la Domingo Diaz.

 

A pesar de la construcción de obras de ingeniería, grandes y costosas, las soluciones para el sistema de drenaje pluvial sigue siendo la misma de hace varias décadas, obras grises rígidas cada vez mas grandes focalizadas sin la evaluación integral del sistemas ausentando y manteniendo en el olvido fact= ores de incidencia como el aumento del nivel del mar, el cambio climático, el crecimiento urbano que propicia modificaciones en el espectro climático y e= l aumento de aguas superficiales que llegan desde áreas permeables al borde la avenida Domingo Diaz.

 

Todo lo descrito en el párrafo anterior, se puede visualizar, en un rápido recor= rido mental (imaginando la actualidad del resto de la ciudad), a lo largo de tod= a la ciudad de Panama. 

 =

=  

=  

= Conclusiones

=  

= ·&nb= sp;        En= los últimos 12 años, de 2008 a 2020, la ciudad de Panamá sufrió daños económicos por poco más de 164 millones de dólares y un aumento de asentamientos vulnerables. Según (Panamá C. N., 2015) en los últimos 5 años, el Estado Panameño ha invertido cerca de US$ 331.03 millones en reconstrucciones de asentamientos por eventos climatológicos extremos y a pesar de esto y que sobran fundamentos descritos en esta investigación, el Manual de Requisitos para la Revisión de Planos donde se dictan las normas para la construcción = de drenajes pluviales, no ha sido modificado/adaptado/actualizado desde hace y= a 18 años.

 =

= ·&nb= sp;        Desde 2002 la huella urbana aguas arrib= a de las cuencas ha experimentado un crecimiento continuo, contando en 2002 con 1,883 hectáreas hasta hoy en 2020 contar con 1,237 hectáreas con una pérdida del 35,6% de la cobertura vegetal.  

 

= ·&nb= sp;        El impacto sobre la escorrentía superficial por el aumento de las zonas impermeables desde 2003 ha aumentado en 6.81% eso significa que, en el núcl= eo de análisis, para lluvias con un periodo de retorno de 10 años existe un excedente de 11.09 mm/h en lluvias de diseño con tiempo de concentración de= 10 minutos.

 

·      =    Los tragantes con aberturas de 35 cm, incrementados en 350% desde 2016, siguen = sin tener la capacidad de absorber la lluvia, en los núcleos de inundacion, en época lluviosa ni con la llegada de lluvias extraordinarias propias de modificaciones climáticas inducidas o naturales, debido a que es un sistema rígido sin capacidad de adaptación.

 

·&nb= sp;        El estudio confirmó, en la comparación de los años 2017 y 2019, que los sistem= as de drenaje pluvial existentes se encontraban en general en buenas condicion= es estructurales y su desempeño fue el esperado de acuerdo con su diseño. Y qu= e en ambos años de evaluación sufrió colapsos por la precipitación de la estación lluviosa dentro del áreas de análisis.  

=  

=  

=  

= Referencias

 

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