1.2 Технологийг үнэлэх, баримтжуулах ажилд хамаарах мэдээлэл өгсөн хүмүүс, байгууллагуудын холбоо барих мэдээлэл

Технологи баримтжуулах/үнэлэх ажилд дэмжлэг үзүүлсэн төслийн нэр (шаардлагатай бол)

Book project: Making sense of research for sustainable land management (GLUES)

Технологи баримтжуулах/үнэлэх ажилд дэмжлэг үзүүлсэн төслийн нэр (шаардлагатай бол)

Interplay among multiple uses of water reservoirs via innovative coupling of substance cycles in aquatic and terrestrial ecosystems (INNOVATE / GLUES)

Технологи баримтжуулах/үнэлэх ажилд дэмжлэг үзүүлсэн байгууллага(ууд)-ын нэр (шаардлагатай бол)

Leibniz-Institut für Gewässerökologie und Binnenfischerei (IGB) - Герман

Технологи баримтжуулах/үнэлэх ажилд дэмжлэг үзүүлсэн байгууллага(ууд)-ын нэр (шаардлагатай бол)

Potsdam-Institut für Klimaforschung (PIK) - Герман

Технологи баримтжуулах/үнэлэх ажилд дэмжлэг үзүүлсэн байгууллага(ууд)-ын нэр (шаардлагатай бол)

Universität Hohenheim - Герман

Технологи баримтжуулах/үнэлэх ажилд дэмжлэг үзүүлсэн байгууллага(ууд)-ын нэр (шаардлагатай бол)

Technische Universität Berlin (Technische Universität Berlin) - Герман

Технологи баримтжуулах/үнэлэх ажилд дэмжлэг үзүүлсэн байгууллага(ууд)-ын нэр (шаардлагатай бол)

Hochschule für Technik und Wirtschaft Dresden (HTW Dresden) - Герман

1.3 ВОКАТ-аар баримтжуулсан өгөгдлийг ашиглахтай холбоотой нөхцөл

Эмхэтгэгч болон гол мэдээлэгч хүн(хүмүүс) WOCAT аргачлалаар баримтжуулсан мэдээллийг ашиглахтай холбоотой нөхцлийг хүлээн зөвшөөрсөн:

Тийм

2.1 Технологийн товч тодорхойлолт

Технологийн тодорхойлолт:

Water purification using macrophytes to treat effluent from fish farming.

2.2 Технологийн дэлгэрэнгүй тодорхойлолт

Тодорхойлолт:

The “Green Liver System” uses aquatic plants, established in artificial wetlands, to remove, transfer, stabilize or eliminate pollutants in wastewater from fish farms. The use of large quantities of feed in aquaculture, along with the application of antibiotics, hormones and probiotics, has negative impacts on aquatic ecosystems due to the introduction of nitrogen, phosphorous and drug residues into the system. The Green Liver System is a form of phytoremediation (phyto = plant and remediate = correct) that uses a range of plants to decompose, extract, or hold contaminants present in soils and waters. This technology has been considered as an innovative alternative and a low cost option compared to others used in contaminated sites - like membrane bioreactors, upflow anaerobic sludge blanket (UASB), and others.

The plants selected for use in Green Liver System artificial wetlands depend on the pollutant to be removed. Research shows physiological differences between species, which need to be taken into account when planning wastewater treatments. Ideal plants for phytoremediation need: a) a fast growth rate; b) high biomass production; c) long rooting systems; d) easy maintenance/pruning; e) to be able to persists, and f) to have the ability to store trace metals within specific parts which can be later removed.

The Green Liver System uses aquatic macrophytes, which extract contaminants from the water, store them, or even metabolize them - transforming them into less toxic or harmless products. In the case of Eichhornia crassipes, most of the solids in suspension are removed by sedimentation or by adsorption in the root system. The dense coverage of these plants reduces the mixing effect of the wind, as well as minimizing thermal mixture. Shading by the plants restricts algal growth and the root system prevents horizontal movement of particulate material. In this way, particles are removed from the wastewater and microorganisms associated with the plants’ rhizosphere slowly decompose. Many organisms can be used in biodegradation: these include bacteria and fungi as well as plants, and the efficiency of one or the other depend, in many cases, on the molecule structure and of the presence of enzymes that are effective in degrading the pollutant.

The fish farm used as an example here is located on the margins of the Itaparica reservoir in Brazil. There are dozens of excavated tanks used to produce tilapia (Oreochromis niloticus) and “tambaqui” (Colossoma macropomum) fingerlings and juvenile fish. As well as these tanks, there are many net enclosures installed in the reservoir where the fishes are reared to maturity. Part of the wastewater from the excavated tanks is released into a stabilization lagoon, and the remainder goes to the Green Liver System. The effluent is enriched with spare feed, and excreta from the fish, which includes drug residues. If not treated, this may cause eutrophication because of its mineral richness. The Green Liver System consists of an excavated tank of 100m x 20m x 2m in size. The tank is subdivided into six parts: two planted to Eichhornia crassipes and four to Egeria densa. A mesh barrier stops fish from being flushed into the tank. Regular monitoring of the physical, chemical and biological parameters is required to control environmental fluctuations.

2.3 Технологийн гэрэл зураг

2.5 Энэ үнэлгээнд хамрагдсан технологийг хэрэгжүүлсэн улс орон/ бүс нутаг/ байршил

2.6 Хэрэгжсэн хугацаа

Байгуулсан тодорхой оныг мэдэхгүй бол баримжаа хугацааг тодорхойл:

• <10 жилийн өмнө (саяхны)

2.7 Технологийн танилцуулга

Технологийг хэрхэн нэвтрүүлснийг тодорхойл:

• Туршилт/судалгааны үр дүн

Тайлбар (төслийн төрөл г.м.):

Construction took place in 2013, building on earlier experiences of the principal scientist, for instance in South Korea.

3.1 Технологийн үндсэн зорилго (ууд)

• экосистемийг хамгаалах

3.2 Технологи нэвтрүүлсэн газрын одоогийн газар ашиглалтын хэлбэр(үүд)

Тайлбар:

Major land use problems (compiler’s opinion): The Itaparica reservoir was completed in 1988 to generate hydropower. About 40,000 people were compulsorily relocated. The construction of the reservoir had interrupted fish movement, leading to a shortage of fish, making aquaculture a viable and profitable alternative, and current law allows this. However excess feed and excreta of fish, partly containing drug residues, add nutrients and pollute water. ECONOMIC ASPECTS: The agricultural economy of this semi-arid region is characterized by pastoral activities, as well as the cultivation of crop species resistant to drought, such as cotton, corn (maize), beans, and cassava in humid areas. Irrigation from the reservoir was potentially possible but investments in aquaculture proved more profitable. In general, the commercial companies involved do not treat effluent, leading to pollution. Even though monitoring is mandatory, almost nobody does it, nor do they make substantial efforts to purify the effluent.

Major land use problems (land users’ perception): There are several conflicts over water and related land use in the region. Some people say the water quality in the reservoir is good (and use it directly for drinking), others report ill-health especially during times of low water levels. Commercial aquaculture primarily produces tilapia. Invariably, some tilapia escape from their net cages and take over from other local species. The hydroelectric company manages the reservoir according to national needs in electricity – thus sudden water level fluctuations are frequent. Commercial aquaculture and associated land use dominate the shoreline, preventing access for artisanal fishermen to their traditional fishing grounds.

Future (final) land use (after implementation of SLM Technology): Other: Ow: Waterways, drainage lines, ponds, dams
Constraints of transition land, fallow or sporadicall used by roaming livestock (mainly goats) (area in between the land-based aquaculture and the lake)

3.3 Газар ашиглалтын тухай нэмэлт мэдээлэл

Технологи хэрэгжүүлсэн газрын усан хангамж:

• Байгалийн/усалгаатай арга хосолсон

Жилд ургамал ургах улирлын тоо:

• 1

Тодорхойлно уу:

Longest growing period from month to month: all year due to tropical climate

3.4 Технологи ГТМ-ийн аль бүлэгт хамаарах вэ

• гадаргын усны менежмент (булаг, гол, нуур, тэнгис гэх мэт)
• Ус намгархаг газрын хамгаалал / менежмент

• Water purification

3.5 Технологийн хамрах талбай

Тайлбар:

Total area covered by the SLM Technology is 2 m2.
The reservoir is 100m long and 20 m wide, with a depth of 1.7 m, but the area may be larger depending on the volume of effluent to be treated. The whole area comprises the fish ponds.

3.6 Технологийг бүрдүүлэх ГТМ арга хэмжээ

Тайлбар:

Specification of other vegetative measures: macrophytes, different species
Type of vegetative measures: in blocks

3.7 Технологид харгалзах газрын доройтлын төрөл

Тайлбар:

Main causes of degradation: deforestation / removal of natural vegetation (incl. forest fires) (slash-and-burn practices), over-exploitation of vegetation for domestic use (firewood and charcoal making), overgrazing (free roaming run-wild donkeys, and small ruminants), urbanisation and infrastructure development (construction works near to body bodies (not respecting conservation areas)), discharges (point contamination of water) (indiscriminate disposal of effluents; excrements, drugs and surplus feed from fishes in net-cages), over abstraction / excessive withdrawal of water (for irrigation, industry, etc.) (abstraction of water from the reservoir without prior registration, not holding water use permits), change in temperature (supposed to be climate change induced), change of seasonal rainfall (high variability in semi-arid regions rather normal; though rainfall appears to fall in shorter periods), droughts (recurrent droughts are "normal", they appear to last for longer periods), poverty / wealth (limited livelihood sources in the rather remote municipality), inputs and infrastructure: (roads, markets, distribution of water points, other, …) (spoilage and low quality), education, access to knowledge and support services (often little value attached to natural resources), war and conflicts (conflicts among two families; conflicts among indigenous and commercial users), governance / institutional (restricted enforcement of existing rules; clientelism)

Secondary causes of degradation: soil management, crop management (annual, perennial, tree/shrub), industrial activities and mining, release of airborne pollutants (urban/industry…), disturbance of water cycle (infiltration / runoff), Heavy / extreme rainfall (intensity/amounts), wind storms / dust storms, floods, other natural causes (avalanches, volcanic eruptions, mud flows, highly susceptible natural resources, extreme topography, etc.) specify, population pressure, land tenure, labour availability

3.8 Газрын доройтлоос урьдчилан сэргийлэх, сааруулах ба нөхөн сэргээх

Газрын доройтолтой холбоотойгоор Технологи ямар зорилго тавьсан болохыг тодорхойл:

• Газрын доройтлыг бууруулах

4.1 Технологийн техник зураг

4.2 Техникийн үзүүлэлт/ техникийн зургийн тайлбар

The constructed wetland termed a “Green Liver System” is 100m x 25m x 2.0m in size. It is divided into six parts (one third of the tank planted with Eichhornia crassipes the remainder with Egeria densa). The average outflow during the period was 1,800 m³/h. Point P1 is the catchment from the reservoir. Point P2 is the inlet that receives the discharge of effluent from 10 ponds with juvenile tilapia (Oreochromis niloticus). Point P3 is the stage after the treatment with Eichhornia crassipes. Point P4 is the stage of the treatment with Egeria densa. Point P5 is the outlet into a containment basin.

Location: Itacuruba. Pernambuco
Date: 2013

Technical knowledge required for field staff / advisors: high (It is a sophisticated system which requires close observation and monitoring. Site-specific adaptation might be necessary (for instance fencing to avoid goats entering the area).)
Technical knowledge required for land users: high (It is a sophisticated system which requires close observation and monitoring. It will be easier with some experience.)
Main technical functions: improvement of water quality, buffering / filtering water

In blocks
Vegetative material: O : other
Number of plants per (ha): 250000
Other species: Egeria densa; Eichhornia crassipes

Dam/ pan/ pond
Depth of ditches/pits/dams (m): 1.7
Width of ditches/pits/dams (m): 20
Length of ditches/pits/dams (m): 100

Wall/ barrier
Depth of ditches/pits/dams (m): 1.7
Width of ditches/pits/dams (m): ca 0.3
Length of ditches/pits/dams (m): ca 15

Construction material (other): tubes, valves
Specification of dams/ pans/ ponds: Capacity 3400m3
Dimensions of spillways: ca 100m

4.3 Материал болон зардалд хамаарах ерөнхий мэдээлэл

Үнэ өртөгийг тооцоход ашигласан мөнгөн нэгж:

• Америк доллар

Ам.доллар ба үндэсний мөнгөн нэгж хоорондын хөрвөх үнийг тодорхойл (шаардлагатай бол): 1 USD =:

3.17

4.4 Бий болгох үйл ажиллагаа

	Үйл ажиллагаа	Арга хэмжээний төрөл	Хугацаа
1.	Digging the pit, stabilizing the walls	Ургамлын
2.	Fencing	Ургамлын
3.	Building separation walls	Ургамлын
4.	Planting macrophytes in place	Ургамлын

4.5 Бий болгоход шаардагдсан зардал, хөрөнгийн өртөг

	Зардлын нэр, төрөл	Хэмжих нэгж	Тоо хэмжээ	Нэгжийн үнэ	Зардал бүрийн нийт өртөг	Нийт дүнгээс газар ашиглагчийн төлсөн %
Хөдөлмөр эрхлэлт	Construction		1.0	3000.0	3000.0
Хөдөлмөр эрхлэлт	Macrophyte installation		1.0	1900.0	1900.0
Тоног төхөөрөмж	Truck for removal of soil		1.0	125.0	125.0
таримал материал	Macrophytes					100.0
таримал материал	Wooden fence posts					100.0
Барилгын материал	Walls/baffles (cement)		1.0	475.0	475.0
Барилгын материал	Barbed wire		1.0	315.0	315.0
Барилгын материал	Earthwork		1.0	250.0	250.0
Барилгын материал	Tubular elements		1.0	30.0	30.0
Бусад	Labour: Cutting fence posts		1.0	160.0	160.0
Бусад	Labour: SUpervision		1.0	1000.0	1000.0
Технологи бий болгох нийт үнэ өртөг					7255.0

4.6 Арчилгаа/ урсгал үйл ажиллагаа

	Үйл ажиллагаа	Арга хэмжээний төрөл	Хугацаа/ давтамж
1.	Exchange macrophytes	Ургамлын

4.7 Арчилгаа/урсгал ажилд шаардагдсан зардал, хөрөнгийн өртөг (нэг жилд)

	Зардлын нэр, төрөл	Хэмжих нэгж	Тоо хэмжээ	Нэгжийн үнэ	Зардал бүрийн нийт өртөг	Нийт дүнгээс газар ашиглагчийн төлсөн %
Хөдөлмөр эрхлэлт	Labour		1.0	3000.0	3000.0
Тоног төхөөрөмж	Nylon fabric		1.0	15.0	15.0
таримал материал	Macrophytes		1.0			100.0
Технологийн арчилгаа/урсгал үйл ажиллагаанд шаардагдах нийт үнэ өртөг					3015.0

Тайлбар:

Because of the tropical climate of Brazilian northeast there is a need to remove Eichhornia crassipes periodically because it grows very quickly as there is plenty nutrients and warm temperatures during all year. The cost of removal of the macrophytes is permanent and must be made monthly as the plant reaches adulthood it loses its capability in removing nutrients and gives it back to the water.

5.1 Уур амьсгал

5.2 Гадаргын хэлбэр

5.3 Хөрс

Боломжтой бол хөрсний бүрэн тодорхойлолт, боломжит мэдээллийг өгнө үү, жишээ нь хөрсний төрөл, хөрсний урвалын орчин/хүчиллэг байдал, катион солилцох чадавхи, азотын хэмжээ, давсжилт г.м.

Soil fertility is low
Soil drainage/infiltration is poor
Soil water storage capacity is very low

5.4 Усны хүртээмж ба чанар

5.5 Биологийн олон янз байдал

5.6 Технологи нэвтрүүлсэн газар ашиглагчдын тухай мэдээлэл

Газар ашиглагчдын бусад шинж чанарыг тодорхойл:

Land users applying the Technology are mainly common / average land users
Population density: < 10 persons/km2
Annual population growth: 1% - 2%

5.7 Технологи нэвтрүүлсэн газар ашиглагчийн өмчилж буй, эзэмшиж буй, түрээсэлж буй эсвэл ашиглаж буй (ашиглах эрх) газрын талбай

5.8 Газар эзэмшил, газар ашиглах эрх, ус ашиглах эрх

Газар өмчлөл:

• хувь хүн, өмчийн гэрчилгээгүй
• хувь хүн, өмчийн гэрчилгээтэй

Газар ашиглах эрх:

• хувь хүн

• needs official registration and permission; heavy water use has a price

• needs official registration and permission; heavy water use has a price

5.9 Дэд бүтэц, үйлчилгээний хүртээмж

6.1 Технологийн талбайд үзүүлсэн нөлөө

Нийгэм-эдийн засгийн үр нөлөө

Усны хүртээмж ба чанар

Орлого, зарлага

Нийгэм-эдийн засгийн бусад үр нөлөө

Нийгэм-соёлын үр нөлөө

Экологийн үр нөлөө

Усны эргэлт/ илүүдэл

Хөрс

Экологийн бусад үр нөлөө

6.4 Өртөг ба ашгийн шинжилгээ

Бий болгох зардалтай харьцуулахад ямар ашиг өгсөн бэ (газар ашиглагчийн бодлоор)?

Арчилгаа/урсгал зардалтай харьцуулахад ямар ашиг өгсөн бэ (газар ашиглагчийн бодлоор)?

6.5 Технологи нэвтрүүлэлт

Тайлбар:

There is a little trend towards spontaneous adoption of the Technology. A broad adoption is not yet expectable at this stage of experimental analysis and testing. Few people did already express their interest.

6.7 Технологийн давуу тал/боломжууд

Газар ашиглагчдын тодорхойлсон давуу тал/боломжууд
If the environmental authority increases controls of how effluent from aquaculture ponds is handled (checking pollution and nutrient loads in the effluent which is usually returned to the reservoir without any treatment), the technology would help compliance with existing rules.
The technology can be constructed using locally available material.

Эмхэтгэгч, бусад мэдээлэл өгсөн хүмүүсийн өнцгөөс тодорхойлсон давуу тал/боломжууд
Water purification is realized by using natural processes.
Among the advantages of adopting the Green Liver technology are the low costs, the speed of construction and it's relatively easy operation.

6.8 Технологийн дутагдалтай/сул тал/аюул болон тэдгээрийг хэрхэн даван туулах арга зам

Газар ашиглагч нарын тодорхойлсон сул тал/ дутагдал/ эрсдэл	Тэдгээрийг хэрхэн даван туулах вэ?
Additional manual labour increases costs (and hinders adoption)	The more people use such techniques, for instance due to improved environmental monitoring and fines imposed, the more such extra expenditure will be accepted as regular running costs.
The management of the system is not simple. Many different and unexpected disturbances can occur. Experience and close, constant watch out is needed.	Exchange of experience among users would facilitate its management. An updated list of threats could be helpful.

Эмхэтгэгч, бусад мэдээлэл өгсөн хүмүүсийн өнцгөөс тодорхойлсон сул тал/ дутагдал/ эрсдэл	Тэдгээрийг хэрхэн даван туулах вэ?
From time to time the macrophytes have to be removed, tubes may need cleaning and the system needs to be set up again. Sometimes, the removal of almost all water may be indicated. Major maintenance can cause peak labour needs. Manual labour required to monitor the system on a regular basis, and perform maintenance according to needs. Depending on the number and size of Green Liver Systems in action, caring for them can be a full-time job.	The maintenance costs have to be well budgeted in the overall planning of costs and benefits of the related productive units.
The disposal of the removed macrophytes is still a problem to be solved. If the macrophytes have accumulated high levels of toxins, the biomass cannot be used for compost making or livestock feeding.	The removed macrophytes should be analysed for their pollutant content. A biodigester could be the solution to the disposal of contaminated biomass, generating energy for the productive unit and possibly for the local population too.

7.1 Мэдээлэл цуглуулсан арга/эх үүсвэр

7.2 Ном, хэвлэлийн ишлэл

Гарчиг, зохиогч, он, ISBN:

Pflugmacher, S., Kühn, S., Lee, S.-H., Choi, J.-W., Baik, S., Kwon, K.-S., Contardo-Jara, V., 2015. Green Liver Systems® for water purification: Using the phytoremediation potential of aquatic macrophytes for the removal of different cyanobacterial toxins from water.

Хаанаас авч болох вэ? Зардал?

AJPS 06 (09), 1607–1618. doi:10.4236/ajps.2015.69161.

Гарчиг, зохиогч, он, ISBN:

Nimptsch, J., Wiegand, C., Pflugmacher, S., 2008. Cyanobacterial toxin elimination via bioaccumulation of MC-LR in aquatic macrophytes: An application of the “Green Liver Concept”

Хаанаас авч болох вэ? Зардал?

Environ. Sci. Technol. 42 (22), 8552–8557. doi:10.1021/es8010404.