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HJ 442.5-2020 English PDF

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HJ 442.5-2020: (Technical specifications for environmental monitoring in coastal waters - Part 5: Monitoring of biological quality in coastal waters)
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HJ 442.5-2020English219 Add to Cart 3 days [Need to translate] (Technical specifications for environmental monitoring in coastal waters - Part 5: Monitoring of biological quality in coastal waters) Valid HJ 442.5-2020

PDF similar to HJ 442.5-2020


Standard similar to HJ 442.5-2020

GB 8702   HJ 630   HJ 607   HJ 442.1   HJ 442.2   HJ 442.10   

Basic data

Standard ID HJ 442.5-2020 (HJ442.5-2020)
Description (Translated English) (Technical specifications for environmental monitoring in coastal waters - Part 5: Monitoring of biological quality in coastal waters)
Sector / Industry Environmental Protection Industry Standard
Classification of Chinese Standard Z06
Classification of International Standard 13.020
Word Count Estimation 10,199
Date of Issue 2020-12-16
Date of Implementation 2021-03-01
Older Standard (superseded by this standard) HJ 442-2008
Regulation (derived from) Ministry of Ecology and Environment Announcement No. 66 [2020]
Issuing agency(ies) Ministry of Ecology and Environment

HJ 442.5-2020: (Technical specifications for environmental monitoring in coastal waters - Part 5: Monitoring of biological quality in coastal waters)


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(Technical specifications for environmental monitoring in coastal waters Part 5 Monitoring of biological quality in coastal waters) National Environmental Protection Standards of the People's Republic of China Replace HJ 442-2008 Technical specifications for environmental monitoring in coastal waters Part V Monitoring of Biological Quality in Coastal Waters Technical specification for offshore environmental monitoring Part 5 biological quality monitoring 2020-12-16 release 2021-03-01 implementation Issued by the Ministry of Ecology and Environment i table of contents Foreword...Ⅱ 1 Scope of application...1 2 Normative references...1 3 General requirements for biological quality monitoring in coastal waters...1 4 Collection, storage and transportation of biological quality samples...2 5 Preparation of biological samples...3 6 Analysis of Biological Quality Samples...4 7 Quality Control of Biological Quality Monitoring...4 Appendix A (informative appendix) Biological quality monitoring project analysis method...6

Foreword

To implement the Environmental Protection Law of the People’s Republic of China, the Marine Environmental Protection Law of the People’s Republic of China, and the People’s Republic of China Regulations of the People’s Republic of China on the Prevention and Control of Land-Source Pollutants Pollution and Damage to the Marine Environment “Regulations on the Management of Environmental Pollution Damage to the Marine Environment” and the “Administrative Measures for Environmental Functional Zones in Coastal Sea Areas” to regulate the ecological environment Environmental quality monitoring, protect the ecological environment, and ensure the scientific, accurate, systematic, and feasible Comparability and representativeness, formulate this standard. This standard was first published in.2008.The original standard drafting unit was China Environmental Monitoring Station and Zhoushan Ocean Ecological environment monitoring station. This is the first revision. The revised standard consists of the following ten parts. Part One General Provisions Part Two. Data Processing and Information Management Part III Water Quality Monitoring of Inshore Waters Part Four. Monitoring of Sediment in Coastal Seas Part V Monitoring of Biological Quality in Coastal Waters Part VI Biological Monitoring in Inshore Waters Part VII Monitoring of rivers entering the sea Part 8.Monitoring of Direct Discharge of Sea Pollution Sources and Impact on the Water Environment of Inshore Waters Part IX Emergency and Special Monitoring in Coastal Waters Part 10 Evaluation and Report This standard, as the fifth part of the revised standard, focuses on sample collection, The methods and procedures of preservation, transportation, laboratory analysis, and quality control are mainly revised in the following aspects. --Add relevant requirements for routine monitoring in accordance with GB 18421; --Detailed sample preparation process; --Improved the selection requirements of analysis methods; - Supplement related requirements for quality control. Appendix A of this standard is an informative appendix. From the date of implementation of this standard, the "Environmental Monitoring Specifications for Coastal Sea Areas" (HJ 442-2008) shall be abolished. This standard was formulated by the Department of Ecological Environment Monitoring and the Department of Regulations and Standards of the Ministry of Ecology and Environment. Drafting organizations of this standard. China Environmental Monitoring Station, Zhoushan Marine Ecological Environmental Monitoring Station of Zhejiang Province, Tianjin Ecological Environmental Monitoring Center, Dalian Ecological Environmental Monitoring Center of Liaoning Province. This standard was approved by the Ministry of Ecology and Environment on December 16, 2020. This standard will be implemented on March 1, 2021. This standard is interpreted by the Ministry of Ecology and Environment.

1 Technical specifications for environmental monitoring in coastal waters

Part V Monitoring of Biological Quality in Coastal Waters

1 Scope of application

This standard specifies the collection, storage and transportation of biological quality samples in coastal waters, sample preparation, sample analysis, quality Control and other aspects. This standard applies to biological quality monitoring in coastal waters.

2 Normative references

The content of this standard refers to the terms in the following documents. For undated references, the valid version is applicable to This standard. GB 17378.3 Marine Monitoring Specification Part 3.Sample Collection, Storage and Transportation GB 18421 Marine Life Quality Standard HJ 168 Technical Guidelines for the Preparation and Revision of Environmental Monitoring and Analysis Methods HJ 442.1 The general rules of the first part of the technical specifications for environmental monitoring in coastal waters HJ 442.2 Technical Specification for Environmental Monitoring in Coastal Seas Part 2 Data Processing and Information Management HJ 442.4 Technical Specification for Environmental Monitoring in Coastal Seas Part 4 Monitoring of Sediment in Coastal Seas HJ 442.10 Technical Specifications for Environmental Monitoring in Coastal Seas Part Ten Evaluation and Report HJ 730 Technical Specification for Layout of Environmental Monitoring Points in Coastal Waters

3 General requirements for biological quality monitoring in coastal waters

The implementation plan for routine monitoring of biological quality in coastal waters shall be formulated in accordance with the relevant requirements of HJ 442.1; The relevant requirements of HJ 730 shall be implemented; data processing and data reporting shall be implemented according to the requirements of HJ 442.2; evaluation and reporting shall be implemented according to HJ 442.10 Require execution. The biological quality monitoring frequency for routine monitoring of important estuaries, bays and key regions determined by the state is once a year. According to the monitoring conditions and evaluation requirements, the area can be sampled once a year or once every two years. The sampling time is arranged in July to August or Class maturity. The biological maturity period is determined according to the specific conditions of each region, and the sampling time in different years should be consistent. collection For crustaceans, fish and algae samples, the frequency and time of sampling shall be determined according to the monitoring purpose. The sampling is generally during the fishing period; Fish and shrimp monitoring are generally in the mature period; sampling times in different years should be kept the same. The mandatory test items for routine monitoring are the shellfish pollution evaluation items specified in GB 18421; the selected test items are the monitoring area Quality of other shellfish pollution factors and other organisms (crustaceans, fish and algae) except those specified in GB 18421 Wait. The biological quality monitoring items, time and frequency of other monitoring tasks shall be determined according to the monitoring purpose. 24 Collection, storage and transportation of biological quality samples 4.1 Collection of samples 4.1.1 Basic principles a) The principle of regional representativeness. The sample collection for routine monitoring should be able to reflect the Accumulation status; should choose to represent different types of habitats (intertidal zone, subtidal zone and nearshore sea area); Avoid sources of pollution. For sample collection for other thematic monitoring, select those that meet the monitoring purpose and are suitable for thematic evaluation. area. b) The principle of species representativeness. For the types of samples collected for routine monitoring, shellfish samples should be selected in accordance with GB 18421; When the requirements of GB 17378.3 cannot be met, local dominant species should be selected; such as crustaceans, fish and general When monitoring the biological quality of algae, local dominant species or economic species should be collected. 4.1.2 Selection of sample types The species should be economic organisms with abundant yields, preferably edible; for settlers in this area, the life cycle requirement is one Over years; have an appropriate size to provide enough tissue samples for analysis; have a strong ability to accumulate pollutants; The main species is shellfish, and fish, crustaceans and algae can be selected according to the characteristics of the sea area (tidal flat); according to my country’s marine life According to the characteristics of distribution, the shellfish recommended to be sampled are mussels, oysters, cockles, clams, razor clams, etc.; fish are yellow croaker, plum boy, Pomfret, mullet, flounder, etc.; crustaceans are portunus, sturgeon, shrimp, etc.; algae are kelp, seaweed, sargassum, etc. With The type of body may be determined according to the actual local conditions. 4.2 Collection of samples 4.2.1 Sampling method Sampling methods include benthic trawl fishing, nearshore fixed-point aquaculture sampling, fishing boat fishing, fixed-net fishing in coastal waters and For fishing or direct purchase from the market, the samples obtained should be newly collected and uncontaminated samples. 4.2.2 Sampling tools When sampling, attention should be paid to the impact of sampling tools on the items to be tested, and general iron tools cannot be used to determine metal items. And galvanized and chrome-plated tools. 4.2.3 Sampling area The sampling of environmental quality monitoring points in coastal waters can be directly collected at the points and nearby areas; The sampling of environmental quality monitoring points in coastal waters can also be collected in the intertidal zone or breeding farms in adjacent areas. To the monitoring point When samples cannot be collected nearby, the actual situation should be noted. Shellfish in the intertidal zone should be collected at designated locations; the shellfish, fish, shrimp, and algae samples in the subtidal zone and inshore waters should be collected locally Collected in farms, fishing boats, and fishing ports. 4.2.4 Number of samples Shellfish collection of individuals with roughly similar body length is about 1.5 kg; algae sampling is about 100 g; crustaceans, fish and other organisms 3 The sampling volume is about 1.5 kg to ensure a sufficient number (usually 100 g of muscle tissue is required) of intact samples for analysis and determination. The collected samples were rinsed with sea water on site. For samples used for bacteriological index detection, the whole sampling process is strictly performed Perform aseptic operation. When using on-site parallel samples to analyze the distribution range of biological contamination concentration, on-site parallel samples should be collected, and the number of samples should be Meet the needs of analysis requirements. 4.3 Storage and transportation of samples 4.3.1 Sample storage The biological samples collected should be frozen and stored in a double-layer polyethylene bag (-10℃～-20℃), and the samples should not be deteriorated. Determination. The samples used for bacteriological index detection should be stored in an ice bottle (0℃～4℃) for no more than 24 hours. 4.3.2 Sample transportation After the sample is collected, if it is transported for a long distance, the sample should be placed in the refrigerator to always keep it in a low temperature state and prevent contamination.

5 Preparation of biological samples

5.1 Preparation of mussel samples Use a plastic knife or plastic brush to remove all attachments on the outside of the shell. Rinse each mussel with distilled water or clean sea water Shell, let it drain naturally, and pull out the silk. Use another plastic knife to insert the foot wire extension port, cut the closure muscle, and open the mussel. Wash the soft tissues in the shell with distilled water or clean surface seawater, remove the soft tissues with a plastic knife and tweezers, and let the water run out. Homogenize the sample in a homogenizer, put the homogenized sample back into the original plastic container, weigh it again, record the total weight, and calculate the homogenized weight. Label the sample and save it for testing or freezing. 5.2 Preparation of crustacean samples Separate the abdomen from the head, chest and tail with a plastic knife, carefully remove the internal organs from the abdomen, and remove all the legs. Abdomen Turn off the upper part, cut along the edge of the abdomen outer carapace with a plastic knife, remove the inner outer carapace with plastic tweezers and discard it. Use another plastic The knife loosens the abdominal muscles and removes the muscles with tweezers. Use tweezers to move the muscle into a plastic container, weigh and record the fresh weight. Close the container tightly, affix the sample label, to be tested or frozen. 5.3 Preparation of small and medium fish samples Wash the fish sample with distilled water or clean surface seawater, place it on the workbench, use a plastic knife to remove the pectoral fins and cut open the back Fish skin from head to tail near the fin. Cut a cut across the body of the fish near the gills and tail; on both sides of the abdomen, gills and tail Cut each. Cut with four knives only on one side of the fish body, and do not cut too deep, so as not to cut the internal organs and stain the meat. Use tweezers to move fish The skin is separated from the meat slices, and be careful not to stain the meat slices on the outer skin. Separate the muscle from the spine with another plastic knife and remove it with tweezers muscle. Put the tissue in a plastic container, weigh and record the weight. If the muscle mass on one side cannot meet the analysis dosage, take Replenish the muscles on the other side. Homogenize the fish tissue with a homogenizer, transfer the homogenate into a plastic container of known weight, cover tightly, and weigh Make a note of the weight of the homogenate and other data. Label the sample and save it for testing or freezing. 45.4 Preparation of large fish samples If necessary, place the frozen samples in a refrigerator at 0°C to 4°C overnight to thaw some of them for easy sectioning. Use distilled water Or clean sea water to wash fish samples and place them on a clean workbench. Remove the remaining skin and bone, cut off the surface with a plastic knife, and then Repeat the operation with another plastic knife, leaving a uniform and uncontaminated muscle tissue. Put the muscle tissue into the plastic container In the container, close tightly, weigh, record all the data in the record sheet, affix the sample label, to be tested or cryopreserved.

6 Analysis of biological samples

6.1 Method selection The monitoring analysis method is selected in accordance with the relevant requirements of HJ 442.1.Common on-site testing and laboratory analysis methods see attached Record A. 6.2 Method verification In accordance with the relevant requirements of HJ 442.1, when the initial use method and conditions change, it is necessary to carry out method verification Or it can be used for sample determination after confirming and meeting relevant requirements.

7 Quality control of biological quality monitoring

7.1 Basic requirements The basic requirements of organization, personnel, equipment, etc. shall be implemented in accordance with relevant regulations of HJ 442.1. 7.2 Quality control of sample collection Sample collection should avoid contamination of samples with sampling tools. When a single sample is not sufficient for analysis, multiple samples should be collected. Organisms are used for sample preparation; transportation and storage need to avoid contamination of the sample by the storage container and storage conditions, and avoid The sample has undergone qualitative change. 7.3 Laboratory quality control The laboratory's analytical personnel self-control and internal laboratory control shall be carried out according to the following requirements. a) Carry out method verification and validation as required; b) The quality control of biological quality sample analysis generally adopts methods such as laboratory parallel sample analysis and standard sample analysis. If the method requires the recovery rate of standard addition, it can be controlled by adding standard recovery sample. In the analysis, attention should be paid to individual biological Preparation of samples and multiple biological samples, consistency of sample preparation, etc.; c) The self-control of the analyst generally adopts the clear code sample control, and the other control in the laboratory can use the password and the clear code; d) The other control laboratory adopts a random sampling of inspection samples according to the ratio of HJ 442.4 Table 2 from the analysis samples, and separate samples are compiled separately No., the same test as the original sample, carry out other laboratory control; e) The allowable value of relative deviation of parallel double samples of biological quality samples (including random samples). Analytical methods are required to be implemented, if there is no requirement, refer to HJ 442.4 Table 3; each batch of laboratories will be combined in parallel If the grid rate is above 90%, the analysis result is valid; 30% of the samples are randomly selected when the pass rate is 70% to 90% 5 Re-examination, when the total pass rate of the re-examination result and the original result is more than 90%, the result is valid; the pass rate is 50%～70% When the time, 50% of the samples should be rechecked, and the cumulative pass rate is more than 90%, the result is valid; the pass rate is less than 50% It should be re-analyzed until the result is qualified; when submitting data, generally submit each parallel double sample The mean value of the measured value or the parallel double sample, the average value of the parallel double sample is calculated according to the relevant regulations of HJ 442.2; f) Each batch of samples controlled by the laboratory should insert 2 to 3 marine biological quality standard materials/standard samples or quality control samples. Analysis is used to check whether there are systematic errors. When the number of samples is small, it should not be less than 1; The requirements of the standard method used, and the judgment of the standard range of standard materials/standard samples or quality control samples; g) The analyst refers to HJ 168 and the adopted analysis method to determine the effective digits of the data and confirm the effective digits of the data The last digit of the detection limit is consistent with the last digit of the detection limit, and the number of significant digits is consistent with the requirements; h) The data audit controlled by other laboratories shall be implemented in accordance with the relevant regulations of HJ 442.2.

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