HJ 212-2017_English: PDF (HJ212-2017)
| Standard ID | Contents [version] | USD | STEP2 | [PDF] delivered in | Standard Title (Description) | Status | PDF |
| HJ 212-2017 | English | 495 |
Add to Cart
|
0--9 seconds. Auto-delivery
|
Data transmission standard for online monitoring systems of pollutant
| Valid |
HJ 212-2017
|
| HJ/T 212-2005 | English | 280 |
Add to Cart
|
0--9 seconds. Auto-delivery
|
Standard for data communication of pollution emission auto monitoring system
| Obsolete |
HJ/T 212-2005
|
Preview PDF: HJ 212-2017
| Standard ID | HJ 212-2017 (HJ212-2017) | | Description (Translated English) | Data transmission standard for online monitoring systems of pollutant | | Sector / Industry | Environmental Protection Industry Standard | | Classification of Chinese Standard | Z10 | | Classification of International Standard | 13.020.40 | | Word Count Estimation | 62,672 | | Date of Issue | 2017-04-24 | | Date of Implementation | 2017-05-01 | | Older Standard (superseded by this standard) | HJ 212-2005 | | Quoted Standard | GB 3096-2008; GB/T 16706-1996; GB/T 19582-2008; HJ/T 75-2007; HJ/T 76-2007; HJ 524-2009; HJ 525-2009 | | Drafting Organization | Xi'an Jiaotong University Changtian Software Co., Ltd. | | Administrative Organization | Ministry of Environmental Protection | | Regulation (derived from) | Ministry of Environmental Protection Notice No. 15 of 2017 | | Summary | This standard applies to the data transmission between the pollutant on-line monitoring (monitoring) system, the pollutant discharge process (condition) automatic monitoring system and the monitoring center, and specifies the transmission process and parameter commands, interactive commands, data commands and control commands. The format of the code, given the code definition, this standard allows extensions, but the extension of the content must not conflict with the control commands used or retained in this standard. This standard also stipulates the format of data transmission between on-line monitoring (monitoring) instruments and data acquisition and transmission devices, and gives code definitions. |
HJ 212-2017
HJ
ENVIRONMENTAL PROTECTION STANDARD
OF THE PEOPLE’S REPUBLIC OF CHINA
Replacing HJ/T 212-2005
Data transmission standard for online
monitoring systems of pollutant
ISSUED ON. APRIL 24, 2017
IMPLEMENTED ON. MAY 01, 2017
Issued by. Ministry of Environmental Protection
Table of Contents
Foreword ... 3
1 Scope ... 6
2 Normative references ... 6
3 Terms and definitions ... 6
4 System structure ... 9
5 Layer of protocol ... 11
6 Communication protocol ... 12
7 Communication method of online monitoring instrumentation and data
acquisition transmitter ... 30
Appendix A (Normative) Cyclic redundancy check (CRC) algorithm ... 33
Appendix B (Normative) Coding table of commonly used monitoring factors and
equipment information (expandable) ... 35
Appendix C (Informative) Example of communication command as well as
example of split package and response mechanism ... 49
Appendix D (Informative) Calculation method for main pollutants in monitoring
points of sewage and flue gas pollution sources ... 93
Data transmission standard for online
monitoring systems of pollutant
1 Scope
This standard applies to the data transmission between the online monitoring
system of pollutants, the automatic monitoring system of the pollutant discharge
process (working conditions), and the monitoring center. It specifies the
transmission process as well as the format of parameter commands, interactive
commands, data commands, control commands; gives the definition of code.
This standard allows for expansion, but the expansion of content shall not
conflict with the control commands used or retained in this standard.
This standard also specifies the data transmission format between the online
monitoring instrumentation and the data acquisition transmitter, meanwhile
gives the definition of code.
2 Normative references
This standard refers to the following documents or their terms. For undated
references, the valid version applies to this standard.
GB 3096-2008 Environmental quality standard for noise
GB/T 16706-1996 Codes for environmental pollution source categories
GB/T 19582-2008 Modbus industrial automation network specification
HJ/T 75-2007 Specifications for continuous emissions monitoring of flue gas
emitted from stationary sources (on trial)
HJ/T 76-2007 Specification and test procedures for continuous emission
monitoring systems of flue gas emitted from stationary sources (on trial)
HJ 524-2009 Codes for air pollutants
HJ 525-2009 Codes for water pollutants
3 Terms and definitions
The following terms and definitions apply to this standard.
Process monitoring
According to the process design, the monitoring of key parameters (including
such processing parameters as flow rate, temperature, oxygen content,
pressure, etc., and such electrical parameters as current, voltage, frequency,
rotation speed, etc.) of the operation of production facilities and pollution
treatment facilities (hereinafter referred to as treatment facilities) that affect
discharge of pollutants; combined with the enterprise’s production process
and end monitoring data, comprehensively monitor the operation of the
production facilities and treatment facilities of the enterprise, pollutant
treatment effects and emissions, determine the rationality, authenticity,
acceptability of the monitoring data of the pollutant discharge, which is
named as the emission process (working conditions) monitoring in this
standard.
3.7
Clearance
The process of using clean water, water sample, chemical reagent, etc., to
clean and wash the sample injection pipeline and the main measurement
parts to ensure the accuracy of the measurement data, before the online
monitoring equipment tests the sample, which is called clearance.
3.8
Blowback
In the measurement process of online monitoring instrument, in order to
prevent the measurement results from being affected by the blocking or un-
smoothness of the measurement circuit, use high-pressure gas to
automatically and regularly purge the measurement circuit, so as to ensure
the smooth flow of the measurement circuit, which is called blowback.
3.9
Sampling for overproof
The process of triggering the automatic sampling equipment to collect
pollutant samples when the pollutants exceed the standard, which is called
sampling for overproof.
3.10
Zero calibration
The process of using the zero calibration solution as the specimen to perform
test, where the indicated value of the online monitoring instrument is
One of more of above communication media consists the transmission network
as referred to in this standard.
The application layer of this standard depends on the basic transmission layer.
The basic transmission layer uses the TCP/IP protocol (the TCP/IP protocol has
four layers, namely the network interface layer, the network layer, the
transmission layer, the application layer), the TCP/IP protocol is constructed in
the selected transmission network, which realizes the interface with the
transmission network through the network interface layer in the TCP/IP protocol.
The application layer in this standard substitutes the application layer (only use
three layers of it) in the TCP/IP protocol. The protocol of the entire application
layer is irrelevant to the specific transmission network. This standard is
irrelevant to the communication media.
6 Communication protocol
6.1 Answer mode
A complete command consists of the requester's initiation and the responder's
response. The specific steps are as follows.
1) The requester sends a request command to the responder;
2) After receiving the request, the responder sends a request response (the
handshake is completed) to the requester;
3) After receiving the request response, the requester waits for the responder
to respond to the execution result; if the requester does not receive the
request response, it is processed as overtime of request response;
4) The responder performs the request operation;
5) The responder sends the execution result to the requester;
6) The requester receives the execution result and the command is
completed; if the requester does not receive the execution result, it is
processed as overtime of execution.
6.2 Overtime retransmission mechanism
6.2.1 Overtime for request response
• If the response is not received within the specified time after a request
command is issued, it is considered as overtime;
• In case of retransmission after overtime, if the response is not received after
the retransmission exceeds the specified number, it is considered that the
Note. This field may not be available if the packet is not
split, it is related to the flag bit
Command
parameters CP Character 0 ≤ n ≤ 950
CP = &&data area&&, data area is as defined in clause
6.3.3
6.3.3 Data area
6.3.3.1 Structure definition
The field is concatenated with its value by “=”; in the data area, the different
classification values of the same item are separated by “,”, the different items
are separated by “;”.
6.3.3.2 Field definition
6.3.3.2.1 Field name
Field names are case sensitive, the first character of a word is uppercase, the
other parts are lowercase.
6.3.3.2.2 Data type
C4. It indicates a character string of up to 4 digits, it is based on the actual
number of digits if it is less than 4 digits;
N5. It indicates a character string of up to 5 digits, it is based on the actual
number of digits if it is less than 5 digits;
N14.2. A numeric representation expressed as a variable-length string, which
represents a 14-bit integer and a 2-digit fraction, with a decimal point, signed,
the maximum length is 18;
YYYY. Date year, for example, 2016 indicates the year 2016;
MM. Date month, for example, 09 indicates September;
DD. Date date, for example, 23 indicates 23rd;
hh. Time hour;
mm. Time minute;
ss. Time second;
zzz. Time milliseconds.
6.3.3.2.3 Field comparison
The field comparison is as shown in Table 4. The "width" in Table 4 only contains
Table 4 (continued)
Name of
field Descriptions
Character
set Width Value and description
NewPW New password
0 ~ 9 / a
~ z / A ~
C6
OverTime Overtime 0 ~ 9 N2 The unit is second, the value is 0 < n ≤ 99
ReCount Number of retransmissions 0 ~ 9 N2 The value is 0 < n ≤ 99
VaseNo Sampling bottle No. 0 ~ 9 N2 The value is 0 < n ≤ 99
CstartTime Sampling startup time of equipment 0 ~ 9 N6 hhmmss
Ctime Sampling cycle 0 ~ 9 N2 The unit is hour, the value is 0 < n ≤ 24
Stime Sampling time 0 ~ 9 N4 The unit is minute, the value is 0 < n ≤ 120
xxxxxx-Info Field information - --
“xxxxxx” is the field information code.
Refer to Table B.10 of Appendix B for
details
InfoId Field information code 0 ~ 9 / a ~ z C6
The value is as shown in Table B.10 of
Appendix B
xxxxxx-SN Online monitoring instrumentation coding
0 ~ 9/A ~
F C24
It consists of an EPC-96 code converted
string, consisting the 24 characters of 0 ~
9, A ~ F
Note. The (converted) real-time value of pollutants, the (converted) maximum value, the (converted)
minimum value, the (converted) average value, etc., determine the width of the uploaded characters
according to the actual pollutant monitoring range and accuracy, meanwhile the metering unit of the
(converted) real-time value of pollutants, the (converted) maximum value, the (converted) minimum
value, the (converted) average value shall be consistent.
6.4 Coding rules
There are three types of monitoring factors involved in this standard. The first
category is the pollutant factor, the second category is the condition monitoring
factor, the third category is the field information. The pollutant factor code is
defined by relevant national and industry standards GB 3096-2008, HJ 524-
2009, HJ 525-2009. The definition of the condition monitoring factor and the
field information coding are as shown in the following clauses.
6.4.1 Coding rules for working condition monitoring factor
The coding of condition monitoring factor consists of a six-digit fixed-length
alphanumeric hybrid format. The alphanumeric code is abbreviated, the
numeric code is represented by an Arabic numeral, using an incremental
numeric code.
6.6.1 System code (expandable)
It corresponds to the system code in Figure 4 “Data structure in communication
protocol”.
6.6.1.1 Division of categories
System code is divided into four categories, each category represents a system
type.
10 ~ 29 indicates the category of environmental quality;
30 ~ 49 indicates the category of environmental pollution source;
50 ~ 69 indicates the category of working conditions;
91 ~ 99 indicates the category of system interaction;
A0 ~ Z9 are used for expansion of unknown system code.
6.6.1.2 System coding method
The system code (as shown in Table 5) is represented by two characters with
values 0 ~ 9 and A ~ Z.
Table 5 -- System coding table (refer to GB/T 16706-1996)
System name System code Descriptions
Monitoring of surface water quality 21
Monitoring of air quality 22
Monitoring of acoustic environmental quality 23
Monitoring of groundwater quality 24
Monitoring of soil quality 25
Monitoring of seawater quality 26
Monitoring of volatile organic compound 27
Atmospheric pollution sources 31
Surface water environmental pollution sources 32
Groundwater environmental pollution sources 33
Marine environmental pollution sources 34
Soil environmental pollution sources 35
Acoustic environmental pollution sources 36
Vibration environmental pollution sources 37
Radioactive environmental pollution sources 38
Site dust fly pollution sources 39
Electromagnetic environmental pollution sources 41
Monitoring of flue gas emission process 51
Monitoring of sewage discharge process 52
3) Setting of real-time data reporting interval;
4) Setting of minute data reporting interval;
5) Setting whether the real-time data is reported or not;
6) Setting whether the operation status of the pollution treatment equipment
is reported or not.
7 Communication method of online monitoring
instrumentation and data acquisition transmitter
The online monitoring instrumentation and the data acquisition transmitter use
the RS-485 serial communication standard to realize data communication.
7.1 Electrical interface standards between online monitoring
instrumentation and the data acquisition transmitter
It is recommended that the online monitoring instrumentation and the data
acquisition transmitter adopt the two-wire system RS-485 interface. For the
electrical standard of the RS-485 interface, refer to the RS-485 industrial bus
standard.
The RS-485 interface of the on-line monitoring instrumentation and the data
acquisition transmitter shall clearly indicate the words “RS485+” and “RS485-’,
etc., to indicate the wiring method.
7.2 Serial communication standards between online monitoring
instrumentation and the data acquisition transmitter
7.2.1 Serial communication bus structure
The communication bus structure between the online monitoring
instrumentation and the data acquisition transmitter is single-master and multi-
slave, as shown in Figure 11.
Figure 11 -- RS485 bus system structure
7.2.2 Transmission protocol of serial communication
Data collector (master)
RS485 bus
Field monitoring instrument
(slave)
Field monitoring instrument
(slave)
Appendix A
(Normative)
Cyclic redundancy check (CRC) algorithm
The CRC check (cyclic redundancy check) is a method for checking the data
transmission error. This standard uses ANSI CRC16, which is shortly referred
to as CRC16.
The CRC16 code is calculated by the transmission equipment and added to the
data packet. The receiving equipment recalculates the CRC16 code of the
received data packet, compares it with the received CRC16 code. If the two
values are different, there is an error.
The steps for generating the CRC16 check byte are as follows.
1) The CRC16 check register is assigned 0xFFFF;
2) Assign the first byte of the checked string to the temporary register;
3) The temporary register is XORed with the upper byte of the CRC16 check
register, assigns to the CRC16 check register;
4) Take the last bit of the CRC16 check register, assign it to the detection
register;
5) Move the CRC16 check register one bit to the right;
6) If the detection register’s value is 1, the CRC16 check register is XORed
with the polynomial 0xA001, assigns to the CRC16 check register.
7) Repeat steps 4 ~ 6, until 8 bits are moved;
8) Assign the next byte of the checked string to the temporary register;
9) Repeat steps 3 ~ 8, until all bytes of the checked string are verified;
10) Return the value of the CRC16 check register.
The check code is stored in the order of the first high byte and then low byte.
Example of CRC check algorithm.
/****************************************************************************************
Function. CRC16_Checkout
Appendix B
(Normative)
Coding table of commonly used monitoring factors and equipment
information (expandable)
Note. The data types in the Table below refer to the definition of “6.3.3.2.2 Data
type”.
Table B.1 -- Coding table of water monitoring factor (citing HJ 525-2009)
Code Chinese name Original code
Default
measurement unit
(concentration)
Default
measurement
unit (discharge)
Default data
type
(concentration)
w00000 Sewage B01 L/s m3 N5.2
w01001 pH value 001 Dimensionless N5.2
w01002 Chroma 002 Chroma N3.2
w01006 Total dissolved solids -- mg/L kg N4
w01009 Dissolved oxygen -- mg/L N3.1
w01010 Water temperature -- °C N3.1
w01012 Suspended solids 003 mg/L kg N4
w01014 Conductivity -- Micro-siemens/cm N3.1
w01017 5-day biochemical oxygen demand 010 mg/L kg N5.1
w01018 Chemical oxygen demand 011 mg/L kg N5.1
w01019 Permanganate index -- mg/L kg N3.1
w01020 Total organic carbon 015 mg/L kg N3.1
w02003 Fecal coliform 550 piece/L N9
w02006 Total bacteria -- piece/L N9
w03001 Total alpha radioactivity 570 Becquerel/L N3.1
w03002 Total beta radioactivity 571 Becquerel/L N3.1
w19001 Surfactant -- mg/L kg N3.2
w19002 Anionic surfactant 520 mg/L kg N3.2
w20012 Barium 039 mg/L kg N3.3
w20023 Boron 037 mg/L kg N3.3
w20038 Cobalt 040 mg/L kg N3.4
w20061 Molybdenum 038 mg/L kg N3.4
w20089 Thallium 041 ng/L mg N4
w20092 Tin 036 mg/L kg N3.1
w20111 Total mercury 020 μg/L g N3.2
w20113 Alkyl mercury 021 ng/L mg N4
w20115 Total cadmium 022 μg/L g N3.1
Appendix C
(Informative)
Example of communication command as well as example of split
package and response mechanism
Descriptions of example. In the example of Appendix C,
QN=20160801085857223 means that a command request is triggered at
8.58.57.223 milliseconds on August 1, 2016, ST=32 means that the system type
is the environmental pollution source of surface water,
MN=010000A8900016F000169DC0 indicates the unique identifier of the
equipment, PW=123456 indicates the equipment access password.
I. Example of communication command
Table C.1 -- Set overtime and number of retransmissions
Category Item Example / description
Command
used
Host
computer
Send “set
overtime and
number of
retransmissions”
Field
computer
Return the
request response
Field
computer
Return the
execution result
Field used
Overtime Overtime
Recount Number of retransmissions
OnRtn Request response result
ExeRtn Request execution result
Execution
process
1. The host computer sends a request command of “set overtime and number of retransmissions”, waits
for the response from the field computer;
2. The field computer receives a request command of “set overtime and number of retransmissions”,
responds “request response”;
3. The host computer receives the “request response”, determines whether to wait for the execution results
of field computer according to the value of the request response flag QnRtn;
4. The field computer executes the request command of “set overtime and number of retransmissions”,
returns the “execution result”;
5. The host computer receives the “execution result”, judges whether the request is completed according
to the value of the execution result flag ExeRtn, the request execution is completed.
Table C.50 -- Extract hour data of pollutant (with response, with split
packet)
Category Item Example / description
Command
used
Host
computer
Send the request of
“Extract hour data
of pollutant”
Field
computer
Return request
response
Field
computer
Upload hour data
of pollutant
Host
computer
Return data
response
Field
computer
Upload hour data
of pollutant
Host
computer
Return data
response
Host
computer
Return execution
result
Field used
BeginTime Start time of history request, accurate to hour
EndTime End time of history request, accurate to hour
QnRtn Request return result
ExeRtn Request execution result
Execution
process
1. The host computer sends a request command “Extract hour data of pollutant”, waits for the field computer
to respond;
2. The field computer receives the request command of “Extract hour data of pollutant”, responds the
“Request response”;
3. The host computer receives the “Request response”, determines whether to wait for the field computer
to report the history data according to the value of the request response flag QnRtn;
4. The field computer executes the request command of “Extract hour data of pollutant”;
5. The field computer reports one message of hour data of pollutant within the time period of request;
6. The host computer receives the command of “Upload hour data of pollutant” and executes it, returns the
“Data response”;
7. The field computer receives the “Data response”;
8. The field judges whether the hour data of pollutant within the time period of request is all reported; if it
is not all reported, jump to step 5; otherwise return the “Execution result”;
9. The host computer receives the “Execution result”, judges whether the request is completed according
to the value of the execution result flag ExeRtn, the execution of request is completed
Appendix D
(Informative)
Calculation method for main pollutants in monitoring points of sewage
and flue gas pollution sources
D.1 Calculation method of main pollutants in monitoring points of sewage
pollution sources
D.1.1 Sewage discharge
D.1.1.1 Sewage discharge within time slice (seconds)
Where.
DΔi - The sewage discharge within the ith T time slice, m3;
Q - Instantaneous flow rate of sewage, L/s;
T - Length of time slice, collecting a set of real-time data at least 5 s, s.
Note. The sewage discharge within the time slice (second) can also be obtained
by the method of accumulating the flow difference of the corresponding time
period.
D.1.1.2 Minute (for example, 10 minutes), hour, daily sewage discharge
Where.
Dm - The sewage discharge at the mth minute, m3;
n - The number of sewage discharge data within the time slice of effective
DΔi - Sewage discharge in the ith T time period, m3.
D.1.2.2 Minute (for example, 10 minutes), hour, day water pollutant discharge
Where.
GΔi - Pollutant discharge in the ith T time period, kg;
Gm - Water pollutant discharge at the mth minute, kg;
n - The number of pollutant discharge data in the time slice as effectively
measured within the mth minute, (n is an integer, n ≥ 120);
Gh - Water pollutant discharge at the hth hour, kg;
m - The number of minute pollutant discharge data as effectively measured
in the hth hour, (m is an integer, 1 ≤ m ≤ 6);
Gd - Daily water pollutant discharge, kg;
h - The number of hour pollutant discharge as measured effectively within
one day, (h is an integer, 1 ≤ h ≤ 24).
D.1.2.3 Minute (for example, 10 minutes), hour, daily average of water pollutant
concentration (weighted average method)
Where.
It is cited from HJ/T 75-2007, HJ/T 76-2007.
D2.1 Calculation formula for conversion of pollutant concentration
(1) The conversion between the concentration of pollutant at working
conditions (measured status) and the concentration at standard conditions
(standard status) are calculated according to formula (18).
Where.
Csn - Mass concentration of pollutant under the standard status, mg/m3;
Cs - Mass concentration of pollutant under the working conditions, mg/m3;
Bα - The ambient atmospheric pressure value of the CEMS installation site,
Pa;
Ps - Static pressure value of flue gas as measured by CEMS, Pa;
Ts - Temperature of flue gas as measured by CEMS, °C.
Note. The dry/wet-base state for the concentration at working conditions and
the concentration at standard conditions in the formula (18) shall be the same.
(2) The conversion of pollutant’s dry-base concentration and wet-base
concentration is calculated according to formula (19).
Where.
Cdry - Dry-base concentration of pollutant, mg/m3 (μmol/mol, ppm);
Cwet - Wet-base concentration of pollutant, mg/m3 (μmol/mol, ppm);
XSW - Absolute humidity of flue gas (also known as moisture), %.
Note. The working conditions of dry-base concentration and wet-base
concentration in formula (19) shall be the same; the calculation method of
dry/wet-base concentration conversion of oxygen content is the same as in
formula (19).
(3) The conversion of the volume concentration of gaseous pollutants and the
dry
wet
Where.
- The average value of the dry-base standard status mass concentration
of the pollutant as measured by the at jth minute, mg/m3;
CQi - Instantaneous mass concentration of pollutant at dry-base standard
status as acquired and measured by the CEMS at the maximum interval of
5s, mg/m3;
n - The number of instantaneous data as effectively measured by CEMS
during that minute, (n is an integer, n ≥ 12).
Note. For the other monitoring factors such as oxygen content of flue gas, flow
rate of flue gas, temperature of flue gas, static pressure of flue gas, humidity of
flue gas, the calculation method is same as the formula (23).
(2) The hour data of mass concentration of pollutant is calculated according
to formula (24).
Where.
- The average mass concentration of pollutant discharge at dry-base
standard status as measured by CEMS at the hth hour, mg/m3;
k - The number of minute average as effectively measured by CEMS during
that hour (45 ≤ k).
Note. For the other monitoring factors such as oxygen content of flue gas, flow
rate of flue gas, temperature of flue gas, static pressure of flue gas, humidity of
flue gas, the calculation method is same as the formula (24).
(3) Daily average value data of mass concentration of pollutant is calculated
according to formula (25).
CVO2 dry - Dry-base volume concentration of oxygen content in flue gas
emission, %.
(3) For the type of pollution source whose oxygen content of industry emission
standard is specified in the pollutant discharge standard, the converted
emission concentration of the pollutant is calculated according to the
formula (28).
Where.
CO2s - The oxygen content of industry standard as specified in the emission
standards, %.
(4) For the types of pollution sources whose standard excess air coefficient
or standard oxygen content are not specified in the pollutant discharge
standard, the converted concentration of the pollutant discharge is
calculated according to the dry-base mass concentration at standard
status.
D2.4 Calculation formula for pollutant discharge flow rate
(1) The average flow rate of flue gas emissions along the cross-section of the
chimney or flue is calculated according to formula (29).
Where.
Kv - The velocity field coefficient as set by CEMS;
- The flow rate of the flue gas as acquired and measured by the CEMS
at the maximum interval of 5 s, m/s;
- The instantaneous flow rate of the flue gas along the cross-section of
chimney or flue, m/s.
(2) The hour flow rate of flue gas emission under working condition is
calculated according to formula (30).
dry
dryconverted
......
|