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The document represents the second national report of the Republic of Azerbaijan on the implementation of the United Nations Framework Convention on Climate Change. It presents national situational analysis, information on emissions and removals of greenhouse gases (GHGs), overview the activities Azerbaijan undertakes to implement the Convention, assessment of vulnerability to climate change, and calls for adaptation measures.

The document is published within the framework of the joint project of the Government of Azerbaijan and United Nations Development Programme "Enabling Activities for the Preparation of Azerbaiijan's Second National Communication to the UNFCCC" with the financial support of the Global Environmantal Facility (GEF).

The Tauw Consortium (TC) formed by Tauw bv - the Netherlands, Milieukontakt International (MKI) - the Netherlands, International HCH and Pesticides Association (IHPA) - Denmark and COWI A/S - Denmark, was selected by the World Bank in October 2009 to execute a Caspian regional POPs workshop in Azerbaijan. TC forms a strong OP, POP and hazardous chemicals team that has cooperated in different combinations in many projects in Central Asia and the Caucasus. Local partner was Mr. Islam Muslim Mustafayev the director of the Azerbaijan branch of the Caucasus Environmental NGO Network.

The workshop aiming at the improvement of obsolete pesticides management was held at the World Bank Office in Baku, from 7 till 11 December 2009 with participants from the five Caspian littoral states and donor organizations (World Bank, FAO). The workshop comprised sessions on: - An update on implementation of international requirements related to obsolete/ POPs pesticides - Development and strengthening of legal and institutional framework - Public awareness raising - Technical problems and priorities The workshop was held as an interactive workshop in which participants presented the current state of the abovementioned aspects of pesticide management for their country. Difficulties and gaps were discussed and ideas were developed in order to bridge the gaps identified. A legal gap analysis showed that in all countries there are gaps in legislation concerning the pesticides cycle. POPs often are not included and legislation needs to be aligned with international requirements. There is a lack of coordination between institutions and stakeholders in most countries. In many countries environmental and human health problems related to obsolete pesticide stocks are aggravated by a lack of awareness. Russia and Azerbaijan presented their experiences with inventory and technical difficulties. The presentations showed that there are problems with planning and coordination, a lack of environmentally sound storage capacity, a lack of knowledge concerning the scale of the problem (reliable and complete national inventory) and a lack of knowledge concerning handling of liquid pesticides. Action plans were presented, which for some countries like Russia, were plans of different options (signing the convention, detailed inventory, pilot on implementation PSMS). Also for Turkmenistan, ratification of the Stockholm Convention is a big challenge. For other countries like Azerbaijan, there is a follow up project about to start. Therefore the action plan for Azerbaijan comprises a number of defined steps already (capacity building, full national inventory). Iran presented an action plan for repackaging of obsolete pesticides in the Golestan province.

Sampling was conducted from the vessel Svetlomor 2 by personnel from AmC, the Ministry of Ecology and Natural Resources (MENR) and SOCAR. Sediment samples for physical and chemical analysis consisted of 2 replicates, while 3 replicates were taken for biological analyses. Analyses were carried out at AmC Caspian Environmental Laboratory.

Sediments around Central Azeri were very poorly sorted, the majority being a mixture of sand and gravel. At many stations, the two replicates were substantially different, indicating patchiness of physical characteristics on a small spatial scale (metres).

LAO was detected at 7 stations in 2010. There was little evidence of change at the majority of stations, and the overall area within which LAO was observed remains very similar to that observed in previous surveys. In general the hydrocarbon concentrations were low or very low and UCM and NPD content were indicative of weathered material being present throughout the survey area.

For the majority of trace metals the data show no clear trends or gradients which could be associated with platform activities. Three elements – barium, cadmium, and lead – exhibited very similar concentration patterns. These were the only elements which indicated a ‘footprint’ which was spatially related to the platform location. A similar association was evident in the 2008 data.

The macrobenthic community was numerically dominated by amphipods which were also the most taxonomically rich group. There was a general tendency towards lower species richness and abundance at stations to the north of, and immediately to the south of, the platform, as was also noted in 2008.

The 2010 data for sediment composition, chemistry and macrobenthic biology suggest that there is an area immediately around the platform in which some degree of sediment alteration is present, and where there is a slightly lower macrobenthic community biomass and diversity relative to more distant stations. However, there are no stations which could be considered biologically impoverished compared to previous surveys.

Technical Summary

Sampling was conducted from the vessel Svetlomor 2 by personnel from AmC, the Ministry of Ecology and Natural Resources (MENR) and SOCAR. Sediment samples for physical and chemical analysis consisted of 2 replicates, while 3 replicates were taken for biological analyses. Analyses were carried out at AmC Caspian Environmental Laboratory.

In general the survey stations around the SDX-5 well site were found to have well sorted very fine silt sediments with low variation in metal and hydrocarbon concentrations.

Relationships were found to be present between metals Cr, Cu, Fe, Mn, Pb and Zn. With the exception of phenols all hydrocarbon parameters were interrelated, with the proportions of UCM and NPD indicating that all hydrocarbons present were weathered.

The macrobenthic community had a low abundance and species richness and was characteristic of the area and depth. Overall no relationship was found to exist between any of the measured variables and the community structure, with the low species richness and abundance likely being due to the depth of the survey area exceeding 500m.

Comparison to previous baseline data indicated change at one station adjacent to the well location. Samples from this station indicated the presence of WBM contaminated drill cuttings, with coarser grained sediments, very high concentrations of Ba and the absence of the metal relationships evident at all other stations.

Hydrocarbon analysis of samples from this position revealed an LAO signature indicating the presence of SBM in addition to the WBM. These samples also had a high proportion of NPD which suggests the likely presence of cuttings contaminated with LAO and also reservoir fluids.

LAO was detected in one other sample and two stations had slightly elevated concentrations of Ba.

Technical Summary

Sampling was conducted from the vessel Svetlomor 2 by personnel from AmC, the Ministry of Ecology and Natural Resources (MENR) and SOCAR. Sediment samples for physical and chemical analysis consisted of 2 replicates, while 3 replicates were taken for biological analyses. Analyses were carried out at AmC Caspian Environmental Laboratory.

The sediments around East Azeri were very poorly sorted with generally good agreement between replicate samples.Variation between metal concentrations was low.

Metal and hydrocarbon concentrations were, with the exception of Ba and Cd, within the range of baseline conditions for the ACG contract area, and in many instances were lower in 2010 than in 2008.

The condition of the macrobenthic community throughout the survey area was, in 2010, better than in 2008, and was closer to the original baseline conditions. There was no evidence that any physical or chemical parameter was associated with impaired community structure or function, although it was clear that the dominant taxonomic groups were more diverse and abundant in coarser sediments.

Specifically, the results of the 2010 survey show no evidence of sustained impact as a result of continuing platform drilling and production operations; there has (with the possible exception of Cd) been no evidence of direct contamination, and the diversity, abundance and biomass of the macrobenthic community has improved since 2008.

This project aimed at inventory training for 10-15 people, mainly from the four Ministries with a designated role in the management of obsolete pesticide stocks (MoA, MoE, MoEm, MoH). The training comprised training on the inventory process, health and safety during inventory, management of inventory data with PSMS, different approaches for stores and burial sites and on the job inventory training (practical part). The practical training was performed on sites of five former pesticide stores including one site where pesticides were buried and soil and groundwater sampling was trained. This World Bank project will be followed on by a TCP project approved by FAO regarding capacity building in pesticide management in Azerbaijan. The TCP project aims at (amongst others) a full national inventory, risk quantification and action plans for high risk sites. For repackaging, there is no project approved yet. In the evaluation of the training, the trainees were confident to be able to train others in order to perform a full national inventory. Further assistance might be needed on selected topics. The trainees did not see a problem concerning knowledge transfer. It is recommended to select trainees more carefully in the future. Ideally, the participants of the inventory training are the people doing the inventory and to keep all steps of the pesticide stockpile management cycle in mind during the individual steps in order to have funding for the following steps like repackaging, safeguarding and final disposal or destruction.

Sampling was conducted from the vessel Svetlomor 2 by personnel from AmC, the Ministry of Ecology and Natural Resources (MENR) and SOCAR. Sediment samples for physical and chemical analysis consisted of 2 replicates, while 3 replicates were taken for biological analyses. Analyses were carried out at AmC Caspian Environmental Laboratory.

The sediment characteristics and metal concentrations around Chirag were found to be highly variable within and between stations, with generally little change being observed from 2008. Despite the detection footprint remaining unchanged from previous years, LAO concentrations continue to reduce. THC and PAH concentrations were generally low, with the highest concentrations being recorded at stations directly to the northeast of the platform.

Ba concentrations were highest within the LAO contamination footprint, suggesting the higher concentrations to be the result of historical drilling discharges. As observed on previous years the concentration of Cd was also highest within this area. The LAO and Ba footprint, indicating the extent of contamination from platform drilling discharges was found to extend 1250m NE, 500m N, 750m E, 1000m W and 250m S of the Chirag platform position.

The 2010 macrobenthic community was numerically dominated by polychaetes and amphipods.

Abundance and species richness were highest at stations on the periphery of the survey area and decreased towards the platform. The lowest abundance an taxonomic richness were found at stations within the LAO and Ba footprint, with the sparsest communities being present at stations directly to the northeast of the platform. Despite a continual reduction in hydrocarbon concentrations from 2006, a general reduction in abundance and taxonomic richness has been observed at the Chirag survey area from 2000 to 2008. This negative trend has reversed in 2010, with a survey wide increase in annelid abundance and amphipod abundance and taxonomic richness being observed. No distinct change in the physicochemical characteristics has been observed between 2008 and 2010 that can be attributed to the abrupt reversal of these trends.

No additional physicochemical impacts from operational activities have been observed between 2008 and 2010 and in general contamination levels continue to reduce

Delegations from five Caspian littoral states - the Republic of Azerbaijan, the Islamic Republic of Iran, the Republic of Kazakhstan, the Russian Federation and Turkmenistan attended the first meeting of the Commission.

On August 11, 2017, a number of events were held by the Ministry of Ecology and Natural Resources of the Republic of Azerbaijan (MENR) connected with the 12 August – “Caspian Day” for the purpose of raising public awareness with regard to the problems and conservation of the Caspian Sea. A meeting was held at MENR by way of the discussion of environmental issues of the Caspian Sea, implemented works and mechanism of involvement of the public in the protection of the Caspian Sea with the participation of certain governmental bodies, Non-Governmental Organizations (NGOs), as well as the youth. Furthermore, a cleansing action was conducted at the coastal zone of Novkhani beach in order to increase the public role, and strengthen the collaboration with public on the betterment of the environmental state of the Caspian Sea and its littoral zone. It should be noted that 2 hectare area was cleaned during the cleansing action, and the collected wastes were recycled. The main objective of the celebration of “Caspian Day” is the strengths mobilization on the protection of the Caspian Sea environment from pollution, conservation, restoration, sustainable and effective use of biological resources of the sea, and public enlightenment in this sphere.

It should be noted, that there did not exist National parks in the Republic of Azerbaijan before establishment of the Ministry of Ecology and Natural Resources. 

In 2003 was established Zangazur National Park on the base of Ordubad National Park named after Academician Hasan Aliyev, Shirvan, Aggol, in 2004 Hirkan, Altiaghaj National Park, in 2005 Absheron National Park, in 2006 Shahdag National Park, in 2008 Goygol National Park. 

In 2008, the area of Hirkan National park was enlarged to 40358 hectares. 

On 25 November 2009 was created an area of 42797,4 hectares on the base of Ordubad National Park named after Academician Hasan Aliyev and Shahbuz State Nature Reserve in Nakhchivan Autonomous Republic. 

Zangazur National Park was named after Academician Hasan Aliyev. 

Shahdag National Park was established in accordance with the decree of the President of the Republic of Azerbaijan dated July 8, 2010. The area of Shahdag National Park was enlarged to 130508,1 hectares. Yalama Forestry Protection and Restoration Division was established in accordance with the decree of the President of the Republic of Azerbaijan dated November 5, 2012 and enlarged to 11772,45 hectares and established Samur- Yalama National Park. 
Currently, the area of the territory of National Parks is 3,7 %.
At the present there are carried out relevant works regard to establishment of new national parks, state natural reserves and is intended to enlarge the territory of Gizilagaj state natural reserve.

In December 23, 2013, a conference was hold about State Program of the total fulfillments on Baku city and its districts’ social-economic progress in 2011-2013 under the chairmanship of Ilham Aliev, the President of Azerbaijan Republic.
Lake BoyukShor was polluted as a result of littering, discharging untreated sewage water, leaking slops from oil industries. The coast line was polluted considerably with solid trashes and oil. On the basis of samples’ analysis was found out that the sediment layer of lake was extremely polluted with oil products. It is also to be found out that ecosystem and quality of water were seriously polluted according to the observations. It is expected to complete more analysis about quality of lake till December 2013. To be improved quality of Lake is the main work. It is necessary to be improved the environment and ecological situation for to renovate place of stadium and to make an enjoyable place for guests. The main goal is to make an acceptable condition of the east part of lake before beginning the European Games. The dam will be built which separate it into the eastern and western parts between the northern and southern shores for to allow partial restoration of the eastern part of the lake. The lake must be turned into the clear lake which has not any visible pollution, suitable to local ecosystem and esthetic vision. It is necessary to make relation between land and water, as well as, nature, life and functional use. In addition, the shoreline of the lake should look attractive and fit the design of the stadium.