ZJB Report

Page 1

A BREATHING LANDSCAPE ZHANGJIABANG URBAN DESIGN AND LANDSCAPE MASTER PLAN


S

hanghai is among the world’s largest and fastest growing cities and it faces many urban environmental challenges including impaired air and water quality, urban heat island, and biodiversity loss. Zhangjiabang Park, located between downtown and Yangtze River’s estuary, is the first of eight green wedges planned by the city to address these challenges. This 4.65 km2 park is ideally situated for comprehensive ecological interventions to recreate native wetlands and forests in an accessible public park surrounded by lively neighborhood redevelopments. Informed by a thorough scientific review, the master plan strives to maximize microclimate benefits to cool and cleanse the city’s air at the local and city-wide scale. The network of canals will be transformed through wetland restoration and de-channelization to maximize water quality benefits and habitat diversity. This ecological park will feature a diversity of habitats and provide much-needed access to nature for the city’s residents.

CONTENTS VISION INTRODUCTION DESIGN & EXPERIENCE APPENDIX


More than 70% of the world population will live in urban areas by 2050. Mega cities like Shanghai will face many urban challanges as they expand, such as the urban heat island, air pollution, and the public health probablems. Urban Heat Island effects have increased 14 folds in the psat 4 decades.

CHALLENGE DEGRADING URBAN MICROCLIMATE


Shanghai has experienced more frequent extreme storm events and flooding in the recent years. The extreme flooding in 2005 affected over one million people and caused over 200 million us dollars damages to the city. The natural hydrological cycle is broken. The canal network in Shanghai has significantly degraded in the last few decades.

CHALLENGE BROKEN URBAN HYDROLOGY

1965

1979

1994

2006

Hydrological Network in Shanghai from 1965 to 2006


Frederick Law Olmsted (1822 - 1903) asserted that the ideal city should be configured around a system of parks, which he called "the lungs of the city." Potentially the largest public open space in Shanghai, Zhangjiabang’s continuous forest and water bodies will bring refreshing air and help cool the city.

VISION 1 COOLING MICROCLIMATE


Urban parks are more than just green and open spaces, design for zhangjiabang strives to integrate ecological principles and BMP (Best Management Practice) to reveal a healthy ecosystem’s metabolism that improves water, air, soil quality and urban biodiversity.

VISION 2 CLEAN WATER, AIR AND SOIL VISION 3 IMPROVE URBAN WILDLIFE HABITAT


Diverse open spaces provide rich recreational opportunities and intimate experience of the nature to the urban citizens. Active and permeable urban interfaces build a strong spatial and functional synergy to the park and public transits.

VISION 4 URBAN RECREATIONAL OPPORTUNITIES


CONCEPT

Re

cr

io

na

l sp

aces

align

ed w ith

sum

m

er

a

节点 URBA 市

ili ng

RE CO

ev

N

pr

e

at

w

in

d

Existing

Conn cted U e

on

ati get

rban

Forest E co

Ve

m ste sy

Scatt ered

Forest And River Corridors Delineate A Series of Recreational Open Spaces

Existing Straight & Channelized Canal

dor With Substant i

s on the Bot

s nd hE

nd

UR BAN CO

RE

iver Corri

城市节

R zed

a etl al W

i ral Natu

Conn ected

Path System Throughout The Park


0

200

400m


CONTEXT


外环

路O

中环

dle

Mid

g Rin

uter

SITE LOCATION Ring

Roa

The site is easily accessible by 3 subway stations to the north and the lightrail from the south.

d

d

Roa

线

号 14

tro

Me

e Lin

14

路 内环

In

ad

g Ro

Rin ner

上海虹桥站 Hongqiao Railway Station

SHA

基地 SITE

ine

上海虹桥国际机场 Hongqiao Airport

线

2号

M

oL etr

2

地 张

Zh

an

gji

an

gL

RT

浦东国际机场 Pudong Airport

PVG


HYDROLOGY Zhangjiabang is one of the major canals connecting downtown and Huangpu River to the Yangtze River. It plays critical roles in the regional hydrology, trasportation, flooding control and recreational uses.

Ri ve r

江 黄浦

市中心 DOWNTOWN

H

ua

pu ng

Ca o

jia

M

aji

aB

Go

u

an

g

张家

陆家嘴 Lujiazui

vjia 浜L

吕家

huan 杨河 C

Yang R

iver

gjia Zhan

g

Ban

Bang


HYDROLOGIC HISTORY From Huangpu River to its end at the Yangtze River, Zhangjiabang stretches 23.5 km. After decades of pollution and recent engineering reinforcement, water quality is at landscape type V, except for NH3-N level. The ecological condition must be improved.

水质良好并有相对完整的野生动植物系统

工业和生活污染日益严重

Clean water with healthy aquatic community

19

60

’s

截流纳污 Separate Sewage System

Worsening industrial and sewage pollution

19

70

’s

19

90

’s

19

98

20

01


2014

1670

1990s


ROOM TO BREATHE: URBAN OPEN SPACES

10% 18% Present

上海的森林覆盖率

Existing Forest Coverage Shanghai

2

82% Absent

5% 18% Present

中国城市平均森林覆盖率

Existing Forest Coverage China Cities Average

82% Absent

张家浜基地

Site Location

世纪公园

Century Park

云层

The cooling effects of the urban open spaces can be clearly measured in a thermal map. 1400%

.70o

2005

.45o

1995

.20o

1985

.05o

1975

上海城区与郊野年平均温度差值 (1975 - 2005)

DIFFERENCE IN AVERAGE ANNUAL TEMPERATURE BETWEEN SHANGHAI & LOCAL COUNTRYSIDE (CELSIUS) Zhao et al. (2006) Frontiers in Ecology & Environment 4(7) 341-346

Cloud

上海地表温度远红外图,2013年8月13日 THERMAL SURFACE IMAGE OF SHANGHAI LANDSAT 8 THERMAL INFRARED SENSOR - 13 AUGUST 2013


URBAN CLIMATE SIMULATION PROCESS An Urban Climate Simulation Process A three-dimensional campus climate simulation process is used to explore the seasonal urban climate of the proposed master plan. The process involves creating a 3D computational model from CAD geometry, simulating and analysing 36 wind directions and hourly 3D solar exposure, coupling the wind simulations and solar exposure simulations with annual meteorology statistics, and finally deriving key climate performance indicators (KPI’s): • A 3D simulation mesh is created from a 3D CAD model consisting of the masterplan buildings, surrounding buildings, and the urban pedestrian realm; • A weather time series is sourced consisting of the hourly data or a typical meteorological year, here representative data from Shanghai was used; • Computational Fluid Dynamic (CFD) wind simulations are performed for 36 wind directions using the simulation mesh; • For the same computational domain, a three-dimensional sun-shade simulation is performed for all relevant hours of the year to determine the hourly solar exposure on the

pedestrian realm; • The 36 wind direction simulation results, the annual hourly solar exposure solution and the annual hourly meteorology data are combined to determine hourly time series describing such indices as thermal comfort and natural ventilation potential; • Histograms of the hourly metrics are used to determine annual frequencies and thus yield key campus climate performance indicators (KPI’s); • The KPI’s that are produced and described here include a seasonal solar shade factor (SHF), a seasonal ventilating wind factor (VWF), a seasonal pedestrian level wind comfort factor and a seasonal thermal comfort factor (TCF). The definition of these KPI’s are provided in Table 1. • Note 1: This simulation process is used as a design tool to identify and map urban area solar exposure, wind exposure, and thermal comfort, so that it can help inform the master plan design. It does not intend to reflect exactly the actual climatic conditions that may be experienced on site.

• Note 2: The present simulations does not include the actual surroundings or landscape as found at the existing site. It is excluded here to facilitate fast analysis and comparision of the local simulated urban climate metrics. • Note 3: Background information on the Universal Thermal Climate Index (UTCI) is provided in Appendix B.


MICROCLIMATE SIMULATION SCENARIOS Winter No Forest

Winter With Forest

Simulated streamlines at pedestrian level for prevailing Northwest winds (winter) without forested areas. Red and yellow colours indicate higher wind exposure compared to reduced and low relative wind exposure in blue.

Simulated streamlines at pedestrian level for prevailing Northwest winds (winter) with forested areas. Red and yellow colours indicate higher wind exposure compared to reduced and low relative wind exposure in blue. Forested areas shield the north side of the south neighbourhood as well as the western perimeters at interior urban blocks.

Summer No Forest

Summer With Forest

Simulated streamlines at pedestrian level for prevailing South-southeast winds (summer) without forested areas. Red and yellow colours indicate higher wind exposure compared to reduced and low relative wind exposure in blue.

Simulated streamlines at pedestrian level for prevailing South-southeast winds (summer) with forested areas. Red and yellow colours indicate higher wind exposure compared to reduced and low relative wind exposure in blue. Forested areas shield the south side of the north neighbourhood as well as the eastern perimeter urban blocks.

Diagram Plan

Diagram Plan Slow Wind Speed Fast Wind Speed


MICROCLIMATE SIMULATION SCENARIOS

Simulated temperature difference is 4 degrees Comparison of Mean Thermal Climate (TCM) for Summer All Day with and without the central forested areas. The forested areas are sheltered from solar radiation which improves the summer time thermal climate. The reduction in wind speed simulated for the north neighbourhood and on the eastern perimeter, marginally increases the perceived temperature.

Legend for summer

Legend for winter

Mean Thermal Climate (TCM) for Summer All Day

Mean Thermal Climate (TCM) for Winter All Day

Pedestrian Level Wind (PLW) for Summer All Day

Pedestrian Level Wind (PLW) for Winter All Day

Mean Ventilating Wind Speed (VWM) for Summer All Day

Mean Ventilating Wind Speed (VWM) for Winter All Day

Comparison of Pedestrian Level Wind (PLW) for Winter All Day with and without the central forested areas. On average, the wind shelter provided by the forested areas improved the wintertime pedestrian level wind condition to suitable for sitting or standing at the north perimeter of the south neighbourhood, as well as around the southeast neighbourhood.

Comparison of Mean Ventilating Wind Speed (VWM) for Winter All Day with and without the central forested areas. For the forested model, lower mean wind speeds are simulated for winter on the north side of the south neighbourhood due to shelter from prevailing northwesterly winds. Reduced winds speeds are also simulated on the perimeter of the southeast neighbourhood.


ADJACENT PARK PROGRAM - Lack of large sports fields and water sports - Lack of educational, arts, and performance program - Lack of green space with rich ecological functions

DOWNTOWN

General Park Sports Park Community Park Cultural Park Forest/Wetland Park Waterfront Park Public Green

SITE


SCALE COMPARISON

4000m

3000m

5000m

2000m

1000m

上海张家浜楔形绿地

加州橘子郡公园

旧金山金门公园

德国柏林滕珀尔霍夫公园

纽约中央公园

ZHANGJIABANG SITE - SHANGHAI

OC GREAT PARK - IRVINE, CALIFORNIA

GOLDEN GATE PARK - SAN FRANCISCO

TEMPELHOFER - BERLIN

CENTRAL PARK - NEW YORK CITY

494 ha.

465 ha.

412 ha.

386 ha.

341 ha.

Zhangjiabang Park is comparable to Orange County Great Park and Golden Gate Park in California in terms of scale and the development density around the park.


DESIGN & EXPERIENCE


0

200

400m


及 市民公园

CIVIC

园 运动公

TS SPOR

PA

G

NE R K ZO

N& ARDE

索景 园及探

动态 ACTIVE

自然 NATURE

FORE & URBAN

龙东湖区

S T ZO N E

NE

观区

动态 ACTIVE

静态 PASSIVE

自然 NATURE

都市 URBAN

都市 URBAN

都市 URBAN

都市 URBAN

静态 PASSIVE

DISC

ZO O V E RY

城市森林

LA

K E ZONE

LANDSCAPE ZONES & ACTIVITIES

动态 ACTIVE

静态 PASSIVE

自然 NATURE

动态 ACTIVE

静态 PASSIVE

自然 NATURE


EXPERIENTIAL ITINERARY

7

& 地 湿 ING 和 RM 场 农 C FA 机 NI 有 GA OR

W

L ET

AN

D

2

场 ZA 广 园 PLA 公 RK 区 心 E PA 核 路 OR 湘 TH C 金 R NO

3

草 动 活 A 园 Z 公 LA 市 TP 城 EN EV

4

园 PE & 蝶 CA 蝴 和 NDS 观 LA 景 叠 ING 折 LD FO

8

场 市 R 夫 OO 农 TD OU

9

R MA

KE

B

T UT

T

湖滨 LAKEFRONT

F ER

G LY

D AR

EN 瞰

1 6

岛 AN 地 ISL 湿 ND 心 湖 TLA E W

鸟 V 地 息 AT O 栖 BIT HA

V ER

D

5

AN 道 步 GHL 徒 HI 林 森 ONT L I 湖 滨 EFR TRA K LA REST FO

D

IEW


HABITAT OVERVIEW



HABITAT TYPES THE NEW ZHANGJIABANG PARK WILL PROVIDE

46

HECTARES

MEADOW/ OPEN HABITAT

medium-low connectivity

48

215

% Proposed Tree Cover In The New Park

HECTARES

FOREST/ WOODLAND HABITAT

Evergreen broadleaf forest

65 ha Upland deciduous forest

16 ha Lowland deciduous forest

128 ha Bamboo forest

6 ha

high connectivity

61 WETLAND & AQUATIC HECTARES

HABITAT

high connectivity

5% Existing Tree Cover At the Zhangjiabang Site

THE EXISTING SITE ONLY OFFERS

22

HECTARES

OF TREE COVER

low connectivity


7

2

E R CO Z A H LA T R P O N RK PA

3 1

4 6 8

9

5


ACTIVE NORTH CORE



ENLARGEMENT PLAN NORTH URBAN CORE 1

金湘路地铁广场 METRO PLAZA

5

雕塑公园 SCULPTURE GARDEN

9

社庄湖 TEMPLE LAKE

13

社区绿廊 COMMUNITY GREENWAY

2

零售商街 COMMERCIAL

6

公园入口广场 GATEWAY PLAZA

10

降噪坡地森林 FORESTED BERM

14

人行天桥 PEDESTRIAN OVERPASS

3

酒店 HOTEL

7

游客信息中心 PARK INFORMATION CENTER

11

园景住宅区 PARKVIEW RESIDENTIAL

15

社区泳池 COMMUNITY POOL

4

艺术馆 ART MUSEUM

8

社庄庙 THE TEMPLE

12

城市景观河道 URBAN LANSCAPE CANAL

1

12

2 13

8

11 3

9

4 15

6 10 7 5

14

0

100

200m


INTEGRATED PUBLIC TRANSIT

METRO LINE 14

ZHANGJIANG LRT


NORTH URBAN CORE

The heart of the district is the Jinxiang Retail Street. This corridor begins at the subway station and join together to form a large plaza and culutral center at the edge of the park. The first 2 levels of the buildings along the corridor will be retail and entertainment programs creating a vibrant social core. This retail complex anchors the district in a series of horziontal pavilions with overhanging photovoltaic canopies that connects right into the entrance of the park. The canopies will provide comfort shading for pedestrians while generating renewable energy for the commerical buildings. The pedistrian scaled cultural and social amenities linked to the larger park system form a vibrant neighborhood of Jinxiang Road Commercial Hub.


NORTH URBAN CORE

金湘路中心广场

Jinxiang Hub Plaza 公园游客中心

Park Visitor Center

北部公园零售区

North Park Retail Village 艺术博物馆 商业街酒店

Market Street Hotel

滨水林荫道

Canal Front Treelined Street

步行街零售和娱乐中心

Marketplace Hub Retail & Entertainment Center

金湘路商业街地标

Jinxiang Gateway Tower

Art Museum


NORTH URBAN CORE COMMERCIAL PROGRAM

The retail plan highlights the active commercial district shown at ground level. This illustrates a kind of retail “figure-ground�, where the figure is colored red and the ground is the landscape paths and paving. The fragmented pavilions in the central area break down in scale in order to integrate with the landscape paving geometries. This specific pavement curvature leads the pedestrian path into the entrance of the park.


JINXIANG ROAD METRO UNDERGROUND STRUCTURE

金湘路商业组团 Jinxiang axis retail wedge

商业街地铁出口 地铁线

Retail street subway exit

Subway line

地下零售 Below ground retail

电梯 Subway escalator

Jinxiang Road station will be served by 5 exits, accessible from all directions near Jinxiang Rd intersection. The Main exit is connected to the commercial hub seamlessly. Underground commercial space is integrated with the passanger corridors and the exits.


NORTH PARKVIEW RESIDENTIAL

城市河道

社区公共空间

Street edge canal

Community public space

现有住宅

Existing residential

学校

School

学校 社区公共空间 公园景观住宅

Park edge residences

School

Community public space

公园景观住宅

Residential park view

公共图书馆

Public Library


7

2

3

N W A L K R T N PA E EV IVIC C

&

1

4 6 8

9

5


RECREATIONAL PROGRAM



ENLARGEMENT PLAN EVENT LAWN AND CIVIC PARK 1

户外剧场 AMPHITHEATER

5

聚会大草坪 EVENT LAWN

9

湿地小岛 WETLAND ISLAND

13

透视花园 PERSPECTIVE GARDEN

2

地形舞台 LANDFORM STAGE

6

树阵 TREE GROVE

10

城市森林 URBAN FOREST

14

竹林书屋 BAMBOO READING ROOMS

3

湿地驳岸 WETLAND EDGE

7

森林山坡 FOREST HILLS

11

社区广场 COMMUNITY PLAZA

15

图书馆 LIBRARY

4

公园零售亭 KIOSKS

8

城市连接道 URBAN LINK PATH

12

木栈道 BOARDWALK

11

4 3

12

5 1 2

13

3

6

14

8

9

7

10 15

0

100

200m


URBAN THERMAL COMFORT

cool-sinking air

warm rising air causes negative pressure

cooler air is drawn into the neighoborhood displacing the rising warmer air

large open spaces allow cooling summer breezes to descend to ground-level The cooling effect of urban green space

Urban Core

Large Parks


DESIGNED THERMAL COMFORT The relocation neighborhood is surrounded by the canals on two sides and the park on the other two sides. It has excellent potential to take advantage of the amenities. The plan suggests naturalize the canal edges to improve water quality and create decks for community uses. Neighborhood green corridors link the residential courtyards to the park.

蒸发与蒸腾

东南风 t Wind Southeas

evapotranspiration

蒸发与蒸腾

evapotranspiration

feed流向城市 ing t he ci ty

蒸发与蒸腾

evapotranspiration

森林

蒸发与蒸腾

蒸发与蒸腾

t Fores

evapotranspiration

evapotranspiration

feed 流向城市 ing t he ci ty

湖区

3~4oC decrease within 2km 两公里内降温3-4摄氏度

森林

心 城市核 ore n a Urb C

森林

场 t 露天剧 ter Fores thea

i Amph20m) (1

草坪 聚会大

Lawn Event0m) 0 (2

t Fores

院 文化庭 rd re Ya

Cultu50m) (2

折 野花坡

叠景观

g FoldinField r e Flow00m) (2

森林

Lake ) (400m

t Fores

风动方

向趋势

W

ORY GECT A R T IND


AMPHITHEATER

Stage

Amphitheater

Meadow Hill

Cafe/Retail

Pedestrian Bridge


TREES AND AIR QUALITY

= 19.3

ZHANGJIABANG PARK WILL HAVE >=

100,000

trees

215

tons CO2

hectares forest & woodlands

captured annually (estimated average)

PM2.5 PM10

Absorbtion

PM2.5 PM10

NO

SO

C(H O)

O

HO

CO CO

Interception

Removed / yr (min.)

O

6.9 6 6.1

PM2.5 PM10 PM2.5 PM10

PM10 PM2.5

CO2

50.3 167.8 4.1 tons tons tons NO O

tons of 03 C(H O )

C(O H

tons of dust

NO NO

Based on: Center for Urban Forest Research, USDA (2007) New York Municipal Forest Research Analysis.

O

OSO

SO

H OH O tons of SOx / NOx

SO

O SO

NO

O

C(H HO)O)

PM2.5 PM10

NO

SO

Produced / yr (min.)

average annual emissions per vehicle type

CO

O O

O

1,080 tons of O2

CO

CO CO

CO


ENLAREGEMENT PLAN SPORTS PARK 10 2 1

3

1

室内运动馆 GYM

2

滑板公园 SKATE PARK

3

1,000米跑道 1,000M TRACK

4

足球 SOCCER FIELDS

5

800米跑道 800M TRACK

6

棒球/垒球 BASE BALL/SOFT BALL

7

网球/篮球 TENNIS/BASKET BALL

8

停车 PARKING

9

森林步道 TRAILS IN THE WOODS

10

市民广场 CIVIC PLAZA

11

儿童游乐场 PLAYGROUNDS

11

4

8

9

7 8

9 5

4 7 6 8 11

7

0

100

200m


& E

7

2 3

4

P A C N S E D D N R A A L G G N FLY I D ER L FOUT T B 1 6

8

9

5


SPRING TIME ACTIVITIES IN THE BUTTERFLY GARDEN



ENLARGEMENT PLAN FOLDING LANDSCAPE & BUTTERFLY GARDEN 1

森林山坡 FOREST HILLS

5

竹林书屋 BAMBOO READING ROOMS

9

趣味折叠景观 FOLDING LANDSCAPE

13

日出坡 SUNRISE SLOPE

2

湿地 WETLAND

6

图书馆 LIBRARY

10

人行天桥 PEDESTRIAN OVERPASS

14

湖岸沙滩 BEACH

3

步道 BOARDWALK

7

野花坡 WILD FLOWER SLOPES

11

社区果蔬园 COMMUNITY GARDEN

15

码头1号 PIER 1

4

透视花园 PERSPECTIVE GARDEN

8

蝴蝶园 BUTTERFLY GARDEN

12

常绿林 EVERGREEN FOREST

16

湖滨步道 PROMENADE

11

2

3 10 4

12 7

8

13

5 1 9 6

14 10 15

16

0

100

200m


EXTENSIVE TRAIL NETWORK


The urban spine trail threads through the major event spaces and provides a strong link between the two neighborhood centers on both sides of the park. Throughout the diverse habitats, 26.5 km of trails provide access including 18.5 km multi-use and 8 km unpaved trails. The series of the recreational fields threaded by the path systems are so diverse that no experiences through our the park are quite the same. From the vibrant summer outdoor concerts, kite festival on the event lawn to the tranquil moments in the folding landscape and butterfly garden, the modes of the landscape vary while the activates on the paths remain energetic.


EXTENSIVE TRAIL NETWORK

Spine Trail 6.6km

Urban Trail 4.7km

Lakefront Trail 4.3km

Island Trail 3.9km

Hill Hiking Trail 2.8km

Sports Trail 3.8km

Urban Forest Loop 2.9km

North Cultural Loop 2.6km


PATH / INFRASTRUCTURE INTEGRATION

Utilize the existing bridges and infrastructure to establish a continous pedestrian network

Accessible Bridge Underpass

3 BRIDGES RETAINED FOR UNDERPASSES

Retrofitted to Pedestrian Bridge

13 BRIDGES RETAINED AS PEDESTRIAN BRIDGES


EXISTING BRIDGES

Landform (To Community Garden)

Middle Ring Expresway

Landform (To Urban Forest)


7

G I H T IL N O RA R F TT E K ES 1 A L OR F

2 3 4 6 8

9

5

A L H

D N


CYPRESS FOREST



ENLARGEMENT PLAN LAKEFRONT HIGHLAND FOREST

1

湖景日光浴山坡 SUNBATHING SLOPE

2

湖岸沙滩 BEACH

3

湖滨步行长廊 LAKE PROMENADE

4

船坞码头 BOAT HOUSE

5

多功能市场 FLEXIBLE MARKET

6

游人码头 PIER

7

游泳池 SWMMING POOL

8

湖区游客信息中心 LAKE INFO CENTER

9

高地森林 HIGHLAND FOREST

10

湿地岛 WETLAND ISLANDS

11

森林岛 FOREST ISLANDS

12

自然体验中心 NATURE CENTER

13

社区菜园 COMMUNITY GARDEN

14

植物治污草甸 PHYTOREMEDIATION

15

社区健身设施 COMMUNITY SPORTS

15 9

14 15

10 13

12

10

1 2

9

11

3

10 9

4 5 11

6 7

8

0

100

200m


NO

SO

O)

FORESTH COMPOSITION O O

O SO

O

NO

O

SO

PM2.5 PM10

C(H O )

O

C(H HO)O)

O

C(O H

Birdwatching Tower

C(H

PM2.5 PM10

NO

O NO

H OH O CO

CO

CO

CO

SO

O

CO

CO PM2.5 PM10

CO CO

Accipiter virgatus

NO

C(H O)

O

SO

O

HO C(H O)

O

CO HO

CO

Upland Deciduous Forest Evergreen Broadleaf Forest

CO CO

Lowland Forest/ Wetland Complex Backwater Stream Vernal Pools Lowland Deciduous Forest

Evergreen Broadleaf Forest Lowland Deciduous Forest Emergent Wetland

Cinnammomum camphorum Metasequoia glyptostroboides

Castanopsis carlesii

Nyssa sinensis

Schima superba

Ulmus parviflora

Quercus glauca

Liquidambar formosana

Sophora japonica

Magnolia x soulangiana

Quercus variabilis

Cornus controversa


CANOPY STRUCTURE

Light

Temperature

Clanga clanga

Glaucidium cuculoides

Accipiter virgatus

Phylloscopus subaffinis

Bombycilla japonica

Anoplophora glabripennis

Cyclophiops major

Horornis diphone

Papilio clytia

Rhinomyias brunneatus

Emergent Canopy Level

Canopy Level

Sub-Canopy Level

Nyctereutes procyonoides Erinaceus amurensis Shrub Level

Herbaceous Level

Plestiodon chinensis

Bufo gargarizans


PLANT MATERIALS

行道树/落叶林

STREET TREES / DECIDUOUS FOREST

选取本地树种因其抗城市 污染物、美观、活力和 净化空气等特征。除伦敦 悬铃木之外,和水杉外其 余均为长江三角州乡土物 种。

Native trees chosen for their tolerance of urban pollutants, their beauty, vigor, and air cleansing ability. Only London Planetree is not native to East China.

銀杏

Ginko biloba

枫香树

Liquidambar formosana

法桐

Platanus x acerifolia

玉兰

Magnolia denudata

灯台树

Cornus controversa

木兰

Magnolia x soulangiana

榔榆

榉树

盐肤木

国槐

Ulmus parvifolia

Rhus chinensis

Zelkova serrata

Sophora japonica

Saphora japonica

鹅掌楸

Liriodendron chinense

七叶树

Aesculus chinensis

水杉

Metasequoia glyptostroboides

栓皮栎

Quercus variabilis

金钱松

Pseudolarix amabilis

蓝果树

Nyssa sinensis

檫木

Sassafras tzumu


PLANT MATERIALS

常绿林 常绿森林原生于离靠近上 海的丘陵地区。常绿林冠 能够常年四季净化空气, 减少污染物。

EVERGREEN FOREST

Evergreen forest community native to the hilly regions nearest Shanghai will cleanse the air and reduce pollutants through all four seasons. 樟树

红楠

榔榆

多穗石柯

柱冠粗榧

小叶青冈

福建青冈

硬壳柯

米槠

苦櫧

Cinnammomum camphorum

天竺桂

木荷

茅栗

灰柯

青冈树

蕈树

Cinnamomum pedunculatum

Lithocarpus henryi

Schima superba

Quercus glauca

Castanea seguinii

Altngia chinensis

Machilus thunbergii

Cephalotaxus harringtonia

Lithocarpus hancei

Castanopsis cuspidata

Cyclobalanopsis myrsinifolia

Castanopsis carlesii

Lithocarpus polystachus

Cyclobalanopsis chungii

Castanopsis sclerophylla


NOISE AND VISUAL IMPACTS

Major Infrastructure as Noise and Visual Barriers 路路 路路

The middle ring road bisects the site, creating physical and visual barriers. The middle and outer ring road are the major noise sources.

+74dB 65-74dB 60-65dB


NOISE MITIGATION

STRATEGIES FOR REDUCING NOISE POLLUTION

现状中环路和基地的噪音研究

With several bisecting streets, an eleveated highway, and other major roadways surrounding the site; noise reduction strategies have been studied and will be integrated into the overall landscape concept.

Noise Study of Existing Section of Ring Road and Site

1、假定交通量条件:6000辆/小时 2、在这6000辆车里面: 小汽车: 85% 5100 中性汽车: 5% 300 重型汽车: 15% 600

Unobstructed

74dB 65dB

3、车速:80公里/小时 4. 使用硬质基地的图表(阿尔法值为0) 用于生源物和接受物高度大于10英尺(3.048米), 或者连接高度高于地面10英尺(3.048米)的情况下

100m

Forest Buffer

现状噪声量:73.6dB 噪音减少量: 3-6m高遮音板可减少:5-12dB 土坡阻挡视线可减少:5dB

74dB 64dB 60m

1. Assumptions: 6000 Vehicle/Hour 2. Among All The 6000 Vehicles: Automobiles: 85% 5100 Medium Trucks: 5% 300 HeavyTrucks: 10% 600

Landscape Berm

74dB

3. Speed: 80 km/Hour

64dB 4. Use of hard site nomograph (ALPHA=0) in all situations in which the source or the receiver is located 10 feet above the ground or whenever the sight averages more than 10 feet above the ground. Existing Noise: 73.6dB

30m

Noise Barrier

74dB

Noise Reduction: 5-12dB(3-6m noise barriers ) 5dB(when the earth berm break the line-of-signt)

63dB

60dB 60m

66dB 30m

15m


EARTHWORKS + NOISE MITIGATION

2 Forest Buffer

60m -10dB

2

1

3

30m -10dB

variable

Forest Meadows Earth Berms

-5-12dB 1 Noise Barrier + Landscape Berm

3 Landscape Berm


7

2 3 4 8

9

6

W

E

D N A TL 1

5

I

A L S

D N


LAKEFRONT AND WETLAND



ENLARGEMENT PLAN LAKE ZONE

1

1

自然体验中心 NATURE CENTER

2

鱼类孵化场 FISH HATCHERY

3

湿地 WETLAND

4

观鸟塔 BIRD WATCHING TOWER

5

湿地木栈道 WETLAND BOARDWALK

6

森林眺望台 FOREST OUTLOOK

7

林间步道 FOREST TRAIL

8

回水段 BACKWATER

9

水生鸟类保护区 WILDLIFE SANCTUARY

10

信息中心 TRAIL HEAD INFO CENTER

11

游人码头 PIER

12

城市湿地 URBAN WETLAND

13

船坞 BOAT HOUSE

14

湖岸沙滩 BEACH

15

城市常绿林 EVERGREEN URBAN FOREST

2

15

14

6

3 11

6

5 4

7

8

13 6

12 11 9 10

6

0

100

200m


WETLAND STRUCTURE WETLAND NATURAL PEST CONTROL:

1 bat can eat up to

1000

mosquitos per hour!

N78%

Griffin, D.G. et al (1960). The echolocation of flying insects by bats. Animal Behavior 8: 141-154

P49%

Bats

ESTMATED % NUTRIENT REMOVAL: UP TO 49% PHOSPHOROUS; UP TO 78% NITROGEN

Dragonflies

Cygnus colombianus

Grus grus

RaptorPlatform

Lotus Backwater

Catfish Spawning

XX Upland

Evergreen Broadleaf Forest Emergent Wetland Lowland Deciduous Forest

Scrub Shurb Wetland Emergent Wetland

Lowland Deciduous Forest

Submerged Wetland Artificial Reef Structure Near-shore | littoral zone

Open water | limnetic zone Phragmites

Scirpus

Cattail


WETLAND FOODWEB

Tertiary Predators INCREASING BIODIVERSITY + ECOSYSTEM RESILIENCE

Secondary Predators

Primary Predators

Herbivores

Primary Production

WETLAND AREA + COMPLEXITY


WINTERING / MIGRATORY WETLAND BIRDS (IUCN LISTED)

LEAST CONCERN 无危

NEAR THREATENED 近危

VULNERABLE 易危

ENDANGERED 濒危

CRITICALLY ENDANGERED 极危

EXTINCT 灭绝

MIGRANTS

OCCASIONAL MIGRANTS

Greater Spotted Eagle (Clanga clanga) Habitat: Hunts over marshes, swamps, wetlands Status: Vulnerable

Lesser White-Fronted Goose (Anser erythropus) Habitat: Lakes, mixed wetlands - Omnivorous Status: Vulnerable

Hooded Crane (Grus monacha) Habitat: Emergent wetland / wet meadow / fields Status: Vulnerable

Dalmatian Pelican (Pelicanus crispus) Habitat: Lakes - Eats fish Status: Vulnerable

Black-faced Spoonbill (Platalea minor) Black-tailed Godwit (Limosa limosa) Habitat: Emergent wetlands / shallows Habitat: Varied wetlands & shores Status: Endangered Status: Near-Threatened

乌雕 生境:于沼泽、湿地狩猎 状态:易危

小白额雁 生境:湖泊、各种湿地 - 杂食 状态:易危

白头鹤 生境:湿地/湿草甸/田野 状态:易危

达尔马提亚鹈鹕 生境:湖泊 - 吃鱼 状态:易危

黑面琵鹭 生境:新生湿地/浅滩 状态:濒危

黑尾塍鹬 生境:多样湿地和海岸 状态:近危

Eastern Imperial Eagle (Aquila heliaca) Habitat: Wetlands with tall perches Status: Vulnerable

Swan Goose (Anser cygnoides) Habitat: Varied freshwater / wet meadow Status: Vulnerable

Falcated Duck (Anas falcata) Habitat: Emergent & Floating Veg. - Dabbler Status: Near-Threatened

Red-Crowned Crane (Grus japonensis) Habitat: Varied wetlands, meadows, ponds Status: Endangered

Chinese Egret (Egretta eulophotes) Habitat: Emergent wetlands Status: Vulnerable

Nordman’s Greenshank (Tringa guttifer) Habitat: Wet meadows, fields, paddies Status: Endangered

白肩雕 栖息地:湿地与高栖木 状态:易危

天鹅 栖息地:淡水/湿草甸 状态:易危

罗纹鸭 生境:新生与浮游植物 状态:近危

丹顶鹤 生境:湿地、草地、池塘 状态:濒危

中国白鹭 生境:新生湿地 状态:易危

小青脚鹬 生境:湿草地、田野、稻田 状态:濒危

Eurasian curlew (Numenius arquata) Habitat: Beaches, shores, wetlands, meadows Status: Near-Threatened

Baer’s Pochard (Aythya baeri) Habitat: Freshwater lakes - Dabbler Status: Critically Endangered

Scaly-sided Merganser (Mergus squamatus) Habitat: Open water - eats fish Status: Endangered

Oriental White Stork (Ciconia boyciana) Habitat: Shallows, wetlands - eats fish Status: Endangered

Black-Headed Ibis (T. melanocephalus) Grey-tailed Tatter (Tringa brevipes) Habitat: Varied wetlands Habitat: Rocky shores, rock platforms Status: Near-Threatened Status: Near-Threatened

白腰杓鹬 生境:海滩、海岸、湿地、草地 状态:近危

青头潜鸭 生境:淡水湖泊 状态:极危

中华秋沙鸭 生境:开放水域 - 吃鱼 状态:濒危

东方白鹳 生境:浅滩、湿地 - 吃鱼 状态:濒危

黑头白鹮 生境:多样湿地 状态:近危

Ochre-rumped Bunting (Emberiza yessoensis) Habitat: Reed beds & varied wetlands Status: Near-Threatened

Collared Crow (Corvus torquatus) Habitat: Parklands, openings with trees Status: Near-Threatened (Resident)

Japanese Waxwing (Bombycilla japonica) Habitat: Parks and woods and gardens Status: Near-Threatened

Yellow-breasted Bunting (Embiriza aureola) Habitat: Fields, wetlands, reedbeds Status: Endangered

赭石腰鹀 生境:芦苇塘和多样湿地 状态:近危

白颈鸦 生境:园地,开阔树林 状态:近危

日本太平鸟 生境:公园、树林、花园 状态:近危

黄胸鹀 生境:田野、湿地、芦苇 状态:濒危

短柄鹬 生境:岩石海岸,岩石台地 状态:近危


OTHER WILDLIFE

Common Amphibians, Reptiles, and Potential Mammals

Black-spotted Pond Frog(Pelophylax nigromaculatus) Habitat: Varied freshwater habitats, meadows, wet forests Status: Near Threatened

Eastern Golden Frog (Pelophylax plancyi) Habitat: Favors lotus ponds Status: Least Concern

Common Pond Frog (Fejervarya limnocharis) Habitat: All freshwater habitats and wet forests. Status: Least Concern

Tiger Frog (Hoplobatrachus rugulosus) Habitat: All freshwater habitats. Eats other amphibians. Status: Least Concern

Asiatic Toad (Bufo gargarizans) Habitat: Forests with adjacent wetlands Status: Least Concern

黑色斑点池蛙 生境:淡水栖息地、草地、湿地森林 状态:近危

东方金蛙 生境:喜好荷花池 状态:无危

泽蛙 生境:所有淡水栖息地和湿地森林 状态:无危

虎纹蛙 生境:所有淡水栖息地。吃其它的两栖动物 状态:无危

中华蟾蜍 生境:与湿地相邻的森林 状态:无危

Racoon Dog (Nyctereutes procyonoides) Habitat: Status: Least Concern

Siberian Weasel (Mustela sibirica) Habitat: Status: Least Concern

Chinese Rabbit (Lepus sinensis) Habitat: Status: Least Concern

Manchurian hedgehog (Erinaceus amurensis) Habitat: Status: Least Concern

Chinese pond turtle (Chinemys reevessi) Habitat: Wetlands and ponds. Uplands for nesting Status: Endangered

Chinese skink (Eumeces chinensis) Habitat: Fields, meadows, and woods. Status: Least Concern

Green Snake (Cyclophiops major) Habitat: Fields, meadows, and woods. Status: Least Concern

中国石龙子 生境:田野、草地、树林。 状态:无危

青蛇 生境:田野、草地、树林 状态:无危

貉 生境: 状态:无危

黄鼬 生境: 状态:无危

中国兔 生境: 状态:无危

The freshwater wetlands, rivers, and lakes of the Yangtze Delta region comprises critical nonbreeding winter habitat for a number of declining and listed migratory birds. Some of these are declining due to issues in their breeding range; however, most of them are being impacted by habitat destruction / degradation in their non-breeding winter ranges as well. In the case of wetlands, this often is due to impoundment, development, or other human activities. At Zhangjiabang we have to opportunity to create meaningful habitat for these birds within the urban fabric of Shanghai. We can create artificial structural habitats for these birds as well as others. For example, installing perch poles adjacent to open wetlands will support the two listed eagles. Installing islands in the lake provides safe roosting for the geese. Among these listed birds, only the Collared Crow is a resident breeder.

满洲刺猬 生境: 状态:无危

中国塘龟 生境:湿地和池塘。高地筑巢 状态:濒危

上海两栖动物多样性减少50% (从14种减少到7种) Shanghai 50% reduction in amphibian diversity (14 to 7 sp.) Li, Anlan (2014). Frogs though diminishing, varieties still found in region’s waterways. Shanghai Daily 06/11/14.

Japanese Gecko (Gekko japonicus) Habitat: Varied, including urban. Status: Least Concern 日本蛤蚧 生境:多样,包括城市 状态:无危


NATURE CENTER

Zhangjiabang Hatchery shall produce: • Fish for aquatic systems restoration (nongame fish including minnows) • Chinese Pond Turtle (Endangered) for population restoration • Amphibians (esp. Tiger frog (Hoplabatrachus rugulosus, Gunther’s frog (Hylarana guentheri, and spot-legged treefrog, Polypedates megacephalus) for population restorations • Sport fish for recreational fishing (esp. mandarin fish, yellowcheek, and chinese catfish)

Wetland Island

Fish Hatchery Overlook

Nature Center

Forest Hill

Meadow Hill

Boardwalk

ZHANGJIABANG LAKE AND WETLAND SECTION


THREATENED FISH POPULATION

Ocean / Estuary Spawning

Lake/Wetland Spawning

Takifugu (Takifugu obscurus)

Yellowcheek (Elapichthys bambusa)

Snakehead (Channa argus)

Marbled Eel (Anguilla marmorata)

Barbel Chub (Squaliobarbus curriculus)

Chinese catfish (Silurus asotus)

Mandarin Fish (Siniperca chuatsi)

Bronze Gudgeon (Coreius heterodon)

Redfin Cutter (Chanodichthyes erythropterus)

Chinese bleak (Aphyocypris chinensis)

Swamp Eel (Monopterus albus)

Goldfish (Carassius auratus)

High-fin Banded Shark (Myxocyperinus asiaticus)

Common Carp (Cyprinus carpio)

Japanese Grenadier Anchovy (Coilia nasus)

Black Carp (Mylopharyngodon piceus)

暗纹东方鲀

鲈鳗

50%

River Spawning

鳡鱼

赤眼鳟

鳜鱼

43%

VULNERABLE TO UNREASONABLE HARVESTING

黄鳝

胭脂鱼

Citation:

铜鱼

中华细鲫

金鱼

VULNERABLE TO HABITAT LOSS / DEGREDATION 刀鲚

30%

花鲶

UP TO 50% OF YANTZE RIVER FISH SPECIES IMPACTED BY LIMITED DISPERSAL OR RESTRICTED RANGE 红鳍鲌

86%

乌鳢

青鱼

Grass Carp (Ctenopharyngodon idellus)

VULNERABLE TO WATER POLLUTION

Shaowen Ye, Zhongjie Li, Jiashou Liu, Tanglin Zhang and Songguang Xie (2011). Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China. Ecosystems Biodiversity, PhD. Oscar Grillo (Ed.) ISBN: 978-953-307-417-7, InTech.

草鱼


CONSTRUCTED HABITAT

FISH STRUCTURES

RAPTOR STRUCTURES

BAT STRUCTURES

WATERFOWL STRUCTURES

SWIFT COLONIES ART STRUCTURES

BASKING LOGS


EXISTING WATERBODIES

THE NEW PARK PROPOSES

78

LINEAR KILOMETERS

OF RESTORED RIPARIAN EDGES

CURRENTLY, ZHANGJIABANG HAS

49

LINEAR KILOMETERS

OF EXISTING HARD-EDGED CANALS


WATER QUALITY & WETLAND

Constructed wetlands increase riparian edge and filtation potential Adjacent canals lack riparian buffers

Riparian buffers & wetland filters overland and groundwater flow

Artificially drained wetland in the Lower Yangtze River Delta for agriculture • Simplified hydrology • Habitat diversity loss • Minimized ecological edge condition • Fast water drainage

Existing channelized water edge

Proposed filtering wetland edge

Design principles for Wetland • Restore and maximize water/land edge condition • Re-establish wetland habitat diversity to including highland woodland to submerge aquatic habitat • Maximize the time that water flows through soil and vegetation to have the highest exchange rate. • Create a hierarchy of water bodies for various habitat and recreational purposes.


WETLAND ECOSYSTEM SERVICE

HOW CAN INTEGRATED NATURAL SYSTEMS IMPROVE WATER QUALITY Building upon knowledge of proven “best management practices,� restored natural systems become one of the primary features of the park lansdcape both in design and funtion. Outside of the future park area, existing canals are being expanded and retrofitted with hard, stabilized edges. Recognizing that these hard edges eliminate both instream and buffer filtration, canal edges within the park examine the potential for establishing continuous riparin wetland buffers throughout, restored floodplain wetlands at locations where the canal enters and exits the park, and constructed wetlands at stormwater outfalls.

2-4%

Effective size should be 2-4% of the contrubuting watershed area

Constructed Stormwater Wetland (Ouftall)

30m

Reccomended minimum buffer width for filtration and biodiversity

Naturalized Canal Edge/Riparian Buffer

Restored Floodplain Wetland (Canal)

These expanded naturalized wetland edges will provide significantly increased potential for the removal of nutrient and sediment pollution, improving the water quality of Zhangjiabang.

Constructed wetlands

Enhanced riparian buffer wetland

effective treatment up to :

100% Removal of suspended solids

100% N reduction from surface & groundwater

90% Removal of nurients

Food source supporting

80% Removal of heavy metals

90% of aquatic species


7

R A F C I N D A N G A OR ETL W 2

I M

G N

&

3 1

4 6 8

9

5


COMMUNITY HARVEST



ENLARGEMENT PLAN URBAN FARMING & WETLAND 1

温室 GREEN HOUSE

5

森林廊道 FOREST CORRIDOR

9

花园草坪 GARDEN LAWN

13

社区健身 COMMUNITY SPORTS

2

花园中心 GARDEN CENTER

6

草甸迷宫 MEADOW LABYRINTH

10

城市农场 URBAN AGRICULTURE

14

儿童游戏场地 PLAYGROUND

3

花园中心湿地植物岛 WETLAND PLANTS ISLAND

7

植物治污草甸 PHYTOREMEDIATION FIELD

11

工作坊 TOOLSHED/WORKSHOP

15

湿地 WETLAND

4

草甸步道 TRAILS

8

湿地森林 WETLAND FOREST

12

果园 ORCHARDS

5

4

11

12

10

15 2

5

6 3 1

8 9

7

13

14

0

100

200m


SOIL ECOLOGY

PLANTING, PHASING, AND PROCESS Considering long-term phasing strategies for the Zhangjiabang site, several areas may require a process-based approach to transition from postindustrial to park. Strategic plantings can help to remove any residual low-grade contaminants and build soil organic matter and nutrients over time, improving the environmental quality and soil ecology of grey/brownfield areas destined to be future parkland. Many common plants used for agriculture and afforestation have been shown to provide detoxifying and nitrogen fixing capabilities. Planting and harvesting these beneficial species as part of the park phasing constuction process will guide the site back toward a more healthy and optimal ecological condition using natural processes.

Removal of metals

Phytoextraction

Phytostabilization

Removal of organic compounds and some chlorinated solvents Rhizodegradation

Phytovolatilization

Soil building

Nitrogen fixing

NH

As

Zn Cd

Se

TCE

NH

N

Cu Ni

Hg

N


SOIL ECOLOGY

Process based site regeneration

Site preparation Soil building cover crop Site preparation

1

Afforestation

Removal of debris and remaining structures

Soil building

Carve out park program

2

Planting of cover crops and nitrogen fixing plants

Design principles for previously developed/post-industrial areas Afforestation

3 Once soil organic matter and nutrient levels are increased, plant with early, mid, and late-successional tree species

Program

4 Carve park program areas out of established meadows and forested areas

• It is likely that the park would be developed in phases due to the scale and complexity of the site • Previously developed areas likely would have deminished capacity for the establishment of plant material • The master plan proposal suggests that the afformentioned areas follow a processed-based approach to minimize cost and to work with natural processes as park of the park’s phasing plan


POTENTIAL CONTAMINATION & PHYTOREMEDIATION

Potential Source of Contamination 路路 Most of the existing factories are potential source of contamination, based on the produc-

tion being manufactured 路路 Any contaminated buildings and site shall be remediated before being reused in the park

Phytoremediation & Soil Building Areas Existing Structures


PLANTING & PHASING STRATEGY FOR PHYTOREMEDIATION

PHASE 1 SPORTS

GARDEN & DISCOVERY

CIVIC & RECREATION

LAKE ZONE

PHASE 2

PHASE 3


7

2 3 1

4 6

8

R O T O E D K T R U A O M

9

5


EARLY MORNING AT THE FARMER’S MARKET



ENLARGEMENT PLAN FARMER’S MARKET 1

码头 PIER

5

湖景餐厅/茶室 LAKE VIEW RESTAURANT/ TEAHOUSE

9

城市湿地 URBAN WETLAND

13

社区公园 COMMUNITY POCKET PARK

2

湖景公寓 LAKE VIEW CONDO

6

商业 RETAIL

10

游泳池 SWIMMING POOL

14

水岸平台 DECK

3

驳船岸 BOAT DOCK

7

露天市场 FLEXIBLE OUTDOOR MARKET

11

运河岸混合商业/办公 CANAL FRONT MIXED USE RETAIL

15

街区绿轴 NEIGHBORHOOD GREEN AXIS

4

船坞 BOAT HOUSE

8

酒店 HOTEL

12

购物中心/ 办公 SHOPPING MALL/ OFFICE

16

阶梯运河景观办公楼 CANAL TERRACE OFFICE

1

2 15

1 5 3

6

4

7

13

1 14

9

8 5

11

10 1

16

12 0

100

200m


LAKESIDE URBAN PARK


LAKESIDE URBAN CORE

办公大楼

复合用地住宅

Office Tower

Residential Mixed Use

湖景酒店 Lakeview Hotel

商业庭院

滨河商业

Retail Courtyards

Canal Retail

滨河商业 Canal Retail

河景阶梯办公楼 Canal Office Terraces

湖景公寓 Lakeview Reisdential

多功能集市 Linear Market

景观地形滨水餐饮 餐厅

Landform Waterfront

Restaurants 船坞俱乐部 Civic Boathouse


RESIDENTIAL BLOCK TYPOLOGY

线性低密度住宅 Linear Low Residential 开放空间

Landscape Open Space

街区微气候 Block Microclimate

Eve r 街区 green 西北 Tree 两侧 s on 种植 Nort 常绿 h and 乔木 Wes ,以 t to B 挡冬 lock 天冷 Win 风 ter W ind

un rS e t n Wi 光 for 态采 t s 动 Ea nd 促进 a , uth So 乔木 n s o 落叶 ree 植 T 种 s ou 侧 idu 南两 c De 区东 街

街区构成 Axon Composite

5m

17 105

m 0

25

50m


OFFICE TERRACE BLOCK TYPOLOGY

河景阶梯办公组团

Canal Office Terraces

开放空间

Landscape Open Space

建筑界面

Building Interface

街区构成 Axon Composite

185

m

150

m

0

25

50m


HYBRID RETAIL BLOCK TYPOLOGY

混合商业

Hybrid Retail 庭院式商业

Courtyard Retail

线性多功能集市 Linear Market

城市滨河商业 Canal Retail

街区构成 15 5

m

Axon Composite

178 m

0

25

50m


LANDFORM WATERFRONT BLOCK TYPOLOGY

景观地形滨水 Landform Waterfront 景观和步道交汇口

Landscape/boardwalk intersect

建筑界面

街区构成

13

3

m

Building Interface

Axon Composite

77m 0

25

50m


STORMWATER MANAGEMENT

地下停车入

5m 1.5m ay Drivew

8m

2.5m

Setback

lk Sidewa

建筑退

人行道

Bike

自行车

7m ay Drivew

车行道

Ramp

坡道 m

ROW 30

生态过滤池

5m

Bioswale

4m

1.5m

车行道

Bioswale

7m

2.5m Bike

自行车

4m lk Sidewa

人行道

Setback

建筑退


STORMWATER MANAGEMENT


7

2

R E M

3 4 8

M O E C T ON N O LZ 1 R F RA E K U A L ULT C 6 5

9

A I C

& L


DUSK ON THE LAKE



PARK RELINKS THE CITY

道 休

湿

湿

湿

道 湿

场 野

营 湖

球 放

筝 热

赛 跑


PARK RELINKS THE CITY

We worked closely with ecologists and climate scientists to investigate the

complex environmental challenges to Shanghai as well as the ecoregion beyond. The research findings together with Shanghai’s long term goals for the green wedge concept reinforced our design phylosophy. We strive to create a new model and catalyst for the rest of the eight green wedges proposed by Shanghai.


ECOLOGY CREATES VALUE FOR SHANGHAI

GLOBAL WETLAND ECOSYSTEM SERVICES

FOREST ECOSYSTEM SERVICES

(Russi et al, 2013)

GLOBAL WETLANDS

200

系统 EM

%

A RE A 地球 面

ST SY

.5 1 积的

服务

40 % G OBAL ECO L

A OB GL 1.5 % OF

LL AN D

SE

R VI CES

0% 4 提 供 全球

评估树木量:100000 (芝加哥取样)

ESTIMATED TREES: 100,000 (Chicago Example)

种植与维护成本(30年) 净价值总计: 每棵树:

Cost of installation and maintenance (over 30 yrs): 22.1 million USD Total net present value: 62.1 million USD Per Tree: 402 USD

评估树木量:100000 (纽约市取样)

ESTIMATED TREES: 100,000 - Annual Benefits in $ (New York City Example)

能量 空气质量 雨洪 二氧化碳 美化/其它

Energy 47.63 / tree Air Quality 9.02 / tree Stormwater 61 / tree CO2 1.29 / tree Aesthetic / Other 89.88 / tree TOTAL: 209 USD / tree / yr

= 20.9 million USD / yr

ACCORDING TO NEW YORK CITY GOVERNMENT’S DATA ESTIMATE IN 2014, THE ESTIMATE VISIBLE VALUE FROM THE ECOLOGICAL SERVICE OF ZHANGJIABANG’S

million USD

ESTIMATED VALUATION: 44,000 USD / HA / YR (Russi et al, 2013) = ZB (46 ha) = ~2 million USD/yr

215 HECTARE

2090

million USD

Jim & Chen (2009) Ecosystem services and valuation of urban forests in China. Cities 26. 187-194.

Data Sources:

McPherson EG, Nowak D, Heisler G, Grimmond S, Souche C, Grant R and Rowntree R. 1997. Quantifying urban forest structure, function, and value: the Chicago Urban Forest Climate Project.

Russi D., Brink P., Farmer A., Badura T., Coates D., Forster J., Kumar R. and Davidson N. (2013) The economics of ecosystems and biodiversity for water and wetlands. Institute for European Environmental Policy (IEEP) and Ramsar Secretariat (London & Brussels). 78 pp.

Sakadevan K. and Bavor H.J. (1999) Nutrient removal mechanisms in constructed wetlands and sustainable water management. Water Science and Technology 40. 121-128.

New York City Parks and Recreation Dept. (2014) Calculating tree benefits for New York City [Online] at: https://www.nycgovparks.org/sub_your_park/trees_greenstreets/images/treecount_report.pdf

FOREST AREA.


ZHANGJIABANG URBAN DESIGN AND LANDSCAPE MASTER PLAN


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